Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149083 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Chlorpyrifos. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151912 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Date for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161797 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161622 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Chlorpyrifos. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161595 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149136 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Chlorpyrifos. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149144 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Chlorpyrifos. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161552 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 4 samples were collected, 4 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2010-07-20 to 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152033 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Chlorpyrifos . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151873 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Date for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161436 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2012-02-28 to 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161692 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chlorpyrifos. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161417 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 4 samples were collected, 4 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2010-07-20 to 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151976 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Chlorpyrifos . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161324 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
17 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 17 samples exceeded the water quality threshold for Chlorpyrifos. Although a total of 23 samples were collected, 6 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2011-04-26 to 2017-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161380 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Chlorpyrifos. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161478 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chlorpyrifos. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161493 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Chlorpyrifos. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151949 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Chlorpyrifos . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161773 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Chlorpyrifos. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152018 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Date for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151977 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 4 samples exceeded the evaluation guideline for Chlorpyrifos . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-06-22 to 2013-06-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151909 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Chlorpyrifos . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161400 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151768 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Date for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152056 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 3 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 4 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-04-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161648 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161617 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
17 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 17 samples exceeded the water quality threshold for Chlorpyrifos. Although a total of 23 samples were collected, 6 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2011-04-26 to 2017-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149137 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Chlorpyrifos. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152078 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 4 samples exceeded the evaluation guideline for Chlorpyrifos . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-06-22 to 2013-06-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151850 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 3 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 4 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-04-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161402 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000, with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2012-02-28 to 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57252 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 9 samples exceed the criterion for CHLORPYRIFOS. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
16233 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
Final Data File used for assessment: SWAMP Sediment Chemistry Data from Region 3 Harbors, 2004
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57254 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceed the criterion for CHLORPYRIFOS. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for chlorpyrifos is 2 µg/L. |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57251 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 9 samples exceed the criterion for CHLORPYRIFOS. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15187 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 8/24/2006-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15095 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Department of Pesticide Regulation_Lower Salinas (DPR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for chlorpyrifos. |
Data Reference: |
e-mail providing Standard operating procedures and Quality Assurance information |
|
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309DAV_DPR - Salinas River at Davis Road, 309SBR_DPR - Salinas River at Del Monte Rd] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
18676 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
25 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Department of Health Services (R3_DHS1) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 25 samples exceed the criterion for Chlorpyrifos Oxygen Analogue. |
Data Reference: |
Final Data File used for assessment: DHS Sediment Chemistry Data, File 1 (feb06)
|
|
Final Data File used for assessment: DHS Sediment Chemistry Data, File 2 (sed06)
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SAC_DHS - Salinas River at Chualar River Rd. bridge] |
Temporal Representation: |
Data was collected over the time period 1/24/1995-8/1/1995. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
No QAPP was provided for this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
18616 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Department of Health Services (R3_DHS1) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 31 samples exceed the criterion for chlorpyrifos. |
Data Reference: |
Final Data File used for assessment: DHS Sediment Chemistry Data, File 1 (feb06)
|
|
Final Data File used for assessment: DHS Sediment Chemistry Data, File 2 (sed06)
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV_DHS - Salinas River at Davis Rd, 309SAC_DHS - Salinas River at Chualar River Rd. bridge, DHS011 - Salinas River at Del Monte Rd] |
Temporal Representation: |
Data was collected over the time period 1/24/1995-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
No QAPP was provided for this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
16232 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
Final Data File used for assessment: SWAMP Sediment Chemistry Data from Region 3 Harbors, 2004
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
18677 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
25 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Department of Health Services (R3_DHS1) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 25 samples exceed the criterion for Chlorpyrifos Oxygen Analogue. |
Data Reference: |
Final Data File used for assessment: DHS Sediment Chemistry Data, File 1 (feb06)
|
|
Final Data File used for assessment: DHS Sediment Chemistry Data, File 2 (sed06)
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SAC_DHS - Salinas River at Chualar River Rd. bridge] |
Temporal Representation: |
Data was collected over the time period 1/24/1995-8/1/1995. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
No QAPP was provided for this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
18617 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Department of Health Services (R3_DHS1) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 31 samples exceed the criterion for chlorpyrifos. |
Data Reference: |
Final Data File used for assessment: DHS Sediment Chemistry Data, File 1 (feb06)
|
|
Final Data File used for assessment: DHS Sediment Chemistry Data, File 2 (sed06)
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV_DHS - Salinas River at Davis Rd, 309SAC_DHS - Salinas River at Chualar River Rd. bridge, DHS011 - Salinas River at Del Monte Rd] |
Temporal Representation: |
Data was collected over the time period 1/24/1995-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
No QAPP was provided for this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15202 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 8/24/2006-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15096 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Department of Pesticide Regulation_Lower Salinas (DPR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for chlorpyrifos. |
Data Reference: |
e-mail providing Standard operating procedures and Quality Assurance information |
|
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309DAV_DPR - Salinas River at Davis Road, 309SBR_DPR - Salinas River at Del Monte Rd] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57238 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57225 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57224 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57237 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for chlorpyrifos is the median lethal concentration (LC50) of 1.77 ug/g and is normalized by the percentage of organic carbon in the sediment sample (Amweg and Weston, 2007). |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57240 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 4 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57253 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for chlorpyrifos is 2 µg/L. |
Guideline Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108246, Chlorpyrifos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57239 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 4 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater criterion continuous concentration to protect aquatic organisms is 0.015 ug/L (Siepmann and Finlayson 2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game (with minor corrections to significant figures as described in Beaulaurier et al., 2005). |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163849 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163687 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153393 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Diazinon . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for diazinon is the median lethal concentration (LC50) of 11 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 11 ug/g is the geometric mean of LC50 values for diazinon from Ding et al. (2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163682 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164172 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164005 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
16 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 16 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13) |
Temporal Representation: |
The samples were collected between the dates of 2011-04-26 and 2017-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153394 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 4 samples exceeded the evaluation guideline for Diazinon . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for diazinon is the median lethal concentration (LC50) of 11 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 11 ug/g is the geometric mean of LC50 values for diazinon from Ding et al. (2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-06-22 to 2013-06-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164071 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149212 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Diazinon. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163490 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163728 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153554 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Diazinon . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for diazinon is the median lethal concentration (LC50) of 11 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 11 ug/g is the geometric mean of LC50 values for diazinon from Ding et al. (2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153476 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Diazinon . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for diazinon is the median lethal concentration (LC50) of 11 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 11 ug/g is the geometric mean of LC50 values for diazinon from Ding et al. (2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163919 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149162 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Diazinon. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163793 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164020 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164154 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-06-05 and 2012-06-05 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153474 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 4 samples exceeded the evaluation guideline for Diazinon . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for diazinon is the median lethal concentration (LC50) of 11 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 11 ug/g is the geometric mean of LC50 values for diazinon from Ding et al. (2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-06-22 to 2013-06-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163686 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
16 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 16 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13) |
Temporal Representation: |
The samples were collected between the dates of 2011-04-26 and 2017-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164077 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-06-05 and 2012-06-05 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149206 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Diazinon. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164046 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164047 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163663 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57115 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceed the criterion for DIAZINON. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15133 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Department of Pesticide Regulation_Lower Salinas (DPR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for diazinon. |
Data Reference: |
e-mail providing Standard operating procedures and Quality Assurance information |
|
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309DAV_DPR - Salinas River at Davis Road, 309SBR_DPR - Salinas River at Del Monte Rd] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57103 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 4 samples exceed the criterion for Diazinon. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
48626 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 5 samples exceed the criterion for Diazinon. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309SSP - Salinas River (Lower) at Spreckles, 309SAC-Salinas River at Chualar bridge on River Road, 309SAG-Salinas River at Gonzales bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-8/25/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
18696 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Department of Health Services (R3_DHS1) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 31 samples exceed the criterion for diazinon. |
Data Reference: |
Final Data File used for assessment: DHS Sediment Chemistry Data, File 1 (feb06)
|
|
Final Data File used for assessment: DHS Sediment Chemistry Data, File 2 (sed06)
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV_DHS - Salinas River at Davis Rd, 309SAC_DHS - Salinas River at Chualar River Rd. bridge, DHS011 - Salinas River at Del Monte Rd] |
Temporal Representation: |
Data was collected over the time period 1/24/1995-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
No QAPP was provided for this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
16641 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Diazinon. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
Final Data File used for assessment: SWAMP Sediment Chemistry Data from Region 3 Harbors, 2004
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15203 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Diazinon. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 8/24/2006-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57116 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Diazinon. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for diazinon is 1 µg/L. |
Guideline Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57117 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceed the criterion for DIAZINON. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for diazinon is 1 µg/L. |
Guideline Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57104 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceed the criterion for DIAZINON. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57102 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 4 samples exceed the criterion for Diazinon. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
18697 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Department of Health Services (R3_DHS1) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 31 samples exceed the criterion for diazinon. |
Data Reference: |
Final Data File used for assessment: DHS Sediment Chemistry Data, File 1 (feb06)
|
|
Final Data File used for assessment: DHS Sediment Chemistry Data, File 2 (sed06)
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV_DHS - Salinas River at Davis Rd, 309SAC_DHS - Salinas River at Chualar River Rd. bridge, DHS011 - Salinas River at Del Monte Rd] |
Temporal Representation: |
Data was collected over the time period 1/24/1995-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
No QAPP was provided for this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
16654 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Diazinon. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
Final Data File used for assessment: SWAMP Sediment Chemistry Data from Region 3 Harbors, 2004
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
48627 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 5 samples exceed the criterion for Diazinon. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309SSP - Salinas River (Lower) at Spreckles, 309SAC-Salinas River at Chualar bridge on River Road, 309SAG-Salinas River at Gonzales bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-8/25/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15134 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Department of Pesticide Regulation_Lower Salinas (DPR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for diazinon. |
Data Reference: |
e-mail providing Standard operating procedures and Quality Assurance information |
|
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309DAV_DPR - Salinas River at Davis Road, 309SBR_DPR - Salinas River at Del Monte Rd] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15204 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Diazinon. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 8/24/2006-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57308 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Diazinon. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for diazinon is the median lethal concentration (LC50) of 11 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 11 ug/g is the geometric mean of LC50 values for diazinon from Ding et al. (2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57101 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Diazinon. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for diazinon is the median lethal concentration (LC50) of 11 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 11 ug/g is the geometric mean of LC50 values for diazinon from Ding et al. (2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57307 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Diazinon. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for diazinon is the median lethal concentration (LC50) of 11 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 11 ug/g is the geometric mean of LC50 values for diazinon from Ding et al. (2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57309 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Diazinon. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for diazinon is the median lethal concentration (LC50) of 11 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 11 ug/g is the geometric mean of LC50 values for diazinon from Ding et al. (2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153354 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Diazinon . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for diazinon is the median lethal concentration (LC50) of 11 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 11 ug/g is the geometric mean of LC50 values for diazinon from Ding et al. (2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149165 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Diazinon. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108249, Diazinon
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163495 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Diazinon. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12723 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
14 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 14 of 24 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 4/24/2000-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57467 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
32 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 32 of 38 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12905 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 7/6/2001-8/29/2001. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
13719 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
17 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Central Coast Watershed Studies (R3_CCOWS) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 17 of 38 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCoWS (Central Coast Watershed Studies) Water Quality Data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ Davis Rd, Del Monte Rd] |
Temporal Representation: |
Data was collected over the time period 3/13/2002-10/21/2003. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
232649 |
|
Pollutant: |
Benthic-Macroinvertebrate Bioassessments |
LOE Subgroup: |
Population/Community Degradation |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
Benthic macroinvertebrate surveys |
Data Used to Assess Water Quality: |
Water Board staff assessed data for 309PS0370 to determine beneficial use support and the results are as follows: 1 of 1 samples exceeded the threshold. CSCI scores were from 0.55 to 0.55. |
Data Reference: |
California Stream Condition Index (CSCI) Scores for the 2020 Integrated Report for Region 3.
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Stream Condition Index (CSCI) is a biological scoring tool that helps aquatic resource managers translate complex data about benthic macroinvertebrates found living in a stream into an overall measure of stream health. The CSCI score is calculated by comparing the expected condition with actual (observed) results (Rehn, A.C. et al., 2015). CSCI scores range from 0 (highly degraded) to greater than 1 (equivalent to reference). CSCI scoring of biological condition are as follows (per the scientific paper supporting the development of the CSCI scoring tool): greater than or equal to 0.92 = likely intact condition, 0.91 to 0.80 = possibly altered condition, 0.79 to 0.63 = likely altered condition, less than or equal to 0.62 = very likely altered condition. Sites with scores below 0.79 are considered to have exceeded the water quality objective for the aquatic life beneficial use. |
Guideline Reference: |
Bioassessment in complex environments: designing an
index for consistent meaning in different settings
|
|
Spatial Representation: |
Samples were collected from station 309PS0370. |
Temporal Representation: |
Samples were collected from 6/13/2017 to 6/13/2017. |
Environmental Conditions: |
|
QAPP Information: |
Data collected following SWAMP QA protocols. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14491 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
26 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 26 of 44 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15313 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
194 |
Number of Exceedances: |
85 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 85 of 194 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-10/10/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
80737 |
|
Pollutant: |
Benthic-Macroinvertebrate Bioassessments |
LOE Subgroup: |
Population/Community Degradation |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
Benthic macroinvertebrate surveys |
Data Used to Assess Water Quality: |
The CSCI scores for this site are 0.276787181 and 0.349628982. Both samples are below the 0.79 threshold and are exceeding the water quality objective for the aquatic life beneficial use. |
Data Reference: |
Coastal Confluences 2008 2009 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
The California Stream Condition Index (CSCI) is a biological scoring tool that helps aquatic resource managers translate complex data about benthic macroinvertebrates found living in a stream into an overall measure of stream health. The CSCI score is calculated by comparing the expected condition with actual (observed) results (Rhen, A.C. et al., 2015). CSCI scores range from 0 (highly degraded) to greater than 1 (equivalent to reference). CSCI scoring of biological condition are as follows: greater than or equal to 0.92 = likely intact condition, 0.91 to 0.80 = possibly altered condition, 0.79 to 0.63 = likely altered condition, less than or equal to 0.62 = very likely altered condition. Sites with scores below 0.79 are considered to have exceeded the water quality objective for aquatic life beneficial use support. |
Guideline Reference: |
Bioassessment in complex environments: designing an
index for consistent meaning in different settings
|
|
Spatial Representation: |
Surveys done at the following station: 309DAVxxx-Salinas River at Davis Road. |
Temporal Representation: |
Surveys done on May 3, 2005 and April, 4 2007. |
Environmental Conditions: |
|
QAPP Information: |
Data were collected following SWAMP QA Protocols for the Central Coast Ambient Monitoring Program. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57038 |
|
Pollutant: |
Benthic-Macroinvertebrate Bioassessments |
LOE Subgroup: |
Population/Community Degradation |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
Benthic macroinvertebrate surveys |
Data Used to Assess Water Quality: |
Both of the IBI scores are 39 or below and therefore are below the impairment threshold of the Southern California IBI. In both 2005 and 2007, a methods comparison study was conducted in this waterbody resulting in the collection of more than one sample at the Salinas River at Davis Road station and more than one IBI score was reported for each event. These samples are not spatially or temporally independent as defined in the Listing Policy. For the purposes of this assessment, staff will use the IBI score from the samples that were collected following the SWAMP Reach Wide Benthos method that is modified for low gradient reaches to include the habitat on the margins. This method is identified in the data as RWB-MCM. The two RWB-MCM samples included in this assessment have the following IBI scores: The 2005 sample IBI score was 7 and the 2007 sample IBI score was 24. |
Data Reference: |
Coastal Confluences 2008 2009 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
The IBI is a multi-metric assessment that employs biological metrics that respond to a habitat or water quality impairment. Each of the biological metrics measured at a site are converted to an IBI score then summed. These cumulative scores are then ranked. For the Southern California IBI, sites with scores of 39 or less are considered to have impaired conditions. |
Guideline Reference: |
A Quantitative Tool for Assessing the Integrity of Southern Coastal California Streams. Environmental Management. Volume 35, number 1 (2005): pp. 1-13
|
|
Spatial Representation: |
Surveys done at the following station: 309DAVxxx-Salinas River at Davis Road. |
Temporal Representation: |
Surveys done on May 3, 2005 and April, 4 2007. |
Environmental Conditions: |
|
QAPP Information: |
Data were collected following SWAMP QA Protocols for the Central Coast Ambient Monitoring Program. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
16232 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
Final Data File used for assessment: SWAMP Sediment Chemistry Data from Region 3 Harbors, 2004
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann and Finlayson (2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
30008 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Fish Migration | Fish Spawning | Preservation of Rare & Endangered Species | Warm Freshwater Habitat | Wildlife Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Nine samples were analyzed by solid phase extraction after an approximately 30 day exposure, in-situ, to known volumes of water. Nine separate sample events were conducted by CCLEAN staff. Two of the 9 samples exceed the Criteria Continuous Concentration. |
Data Reference: |
Final Data CCLEAN Mussel Tissue and Solid Phase Extraction data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentration which are toxic to, or which produce detrimental physiological responses in human, plant, animal, or aquatic life (Central Coast Water Quality Control Plan, general Objective, Section II.A.2.a). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
The Criteria Continuous Concentration (CCC) or the the highest concentration of a pollutant to which aquatic life can be exposed for an extended period of time (4 days) without deleterious effects for 4,4'-DDT is 0.001 ug/L (USEPA. Federal Register, 40 CFR Part 131 (Vol.65, No. 97. May 18, 2000.) ) |
Guideline Reference: |
Water Quality Standards; Establishment of Numeric Criteria for Priority Toxic Pollutants for the State of California; Rule. 40 CFR Part 131. U.S. Environmental Protection Agency, Region IX, Water Division, San Francisco, CA |
|
Spatial Representation: |
Single sample location, Salinas River 1.6 miles below Blanco Road on north shore (Lat, N 36.6950, Long, W 121.7502) |
Temporal Representation: |
Nine separate (approximate 30 day) sample events. The first was initiated on October 5th, 2002 and the ninth event was initiated on October 10th, 2006. |
Environmental Conditions: |
Water from the sample source (i.e., river) is pumped sequentially through a 0.45 micron glass-fiber particle filter, then through a column packed with XAD-2 resin beads, to which nonpolar compounds adsorb. Sampling rates are set to optimum volumes to ensure maximum extraction of target compounds from the sample water. Samples are pumped on a flow-proportioned basis to achieve the desired sample volumes over an approximately 30-day period. This requires predictions of total river discharges during the sampling period, which predictions are not always borne out, resulting in either longer sampling periods or higher or lower than the targeted sample volume. Higher sample volumes provide lower analytical detection limits. Both the particle filter and resin beads are extracted in the laboratory and the extracts are combined and analyzed to provide a total concentration of each compound in the extracted volume of water. |
QAPP Information: |
CCLEAN has an approved QAPP |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57103 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 4 samples exceed the criterion for Diazinon. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52835 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
30 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 30 of 31 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Staff Report Division of Water Quality Nutrient Screening Tools for Use in the Clean Water Act Section 303(d) Listing Process |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/7/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
48626 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 5 samples exceed the criterion for Diazinon. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309SSP - Salinas River (Lower) at Spreckles, 309SAC-Salinas River at Chualar bridge on River Road, 309SAG-Salinas River at Gonzales bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-8/25/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24485 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24564 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-5/26/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24556 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Toxicity, Hyalella azteca 10-day survival %. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SBR-Salinas River at Highway 1 ]. |
Temporal Representation: |
Data was collected on a single day 2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24528 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
11 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 11 samples exceed the criterion for Toxicity, Ceriodaphnia dubia Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles]. |
Temporal Representation: |
Data was collected over the time period 2/17/2005-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24520 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 5 samples exceed the criterion for Toxicity, Ceriodaphnia dubia Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 6/14/2006-2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57417 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 8 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Staff Report Division of Water Quality Nutrient Screening Tools for Use in the Clean Water Act Section 303(d) Listing Process |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 3/25/2009-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28145 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
15 |
Number of Exceedances: |
10 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28122 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
60 |
Number of Exceedances: |
49 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: CCAMP (Salinas). Fourty-nine of the 60 of the samples exceed the evaluation guideline for nitrate. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ]. |
Temporal Representation: |
Data was collected over the time period 2/1/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. The Salinas Watershed Rotation Area has been monitored twice, in 1999 and in 2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28119 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
51 |
Number of Exceedances: |
43 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: CCAMP Coastal Confluences.
Fourty-three of the 51 of the samples exceed the evaluation guideline for nitrate. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ]. |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28108 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth). Five of the 7 samples exceed the evaluation guideline for nitrate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-12/13/2005. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28159 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
107 |
Number of Exceedances: |
81 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: Central Coast Watershed Studies (R3_CCOWS) |
Data Reference: |
Final Data File used for assessment: CCoWS (Central Coast Watershed Studies) Water Quality Data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 6 monitoring sites [ River Rd (Nr East Garrison), Davis Rd, Del Monte Rd, Chualar River Rd, Blanco Rd, Hwy 68] |
Temporal Representation: |
Data was collected over the time period 10/20/2000-6/10/2003. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28132 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
181 |
Number of Exceedances: |
168 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: National Estuarine Research Reserve Monitoring Program (R3_ESNERR). Monitoring was conducted approximately monthly and 168 of 181 samples exceed the evaluation guideline. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-12/4/2006. Monitoring was conducted approximately monthly. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51463 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 4 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SBR-Salinas River at Highway 1 , 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51448 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
33 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 33 of 40 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28163 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
34 |
Number of Exceedances: |
32 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: Central Coast Long Term Environmental Assessment Program (R3_CCLEAN) |
Data Reference: |
Final Data File used for assessment: CCLEAN (Central Coast Long Term Environmental Assessment Program data) Water Quality Data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLR_CCL - Salinas River at Davis Road] |
Temporal Representation: |
Data was collected over the time period 1/22/2002-5/4/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57451 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity. None of the samples exhibited significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at stations 309DAVxxx. |
Temporal Representation: |
The sample was collected in June 2008. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79704 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Five samples were collected to evaluate sediment toxicity. None of the 5 samples exhibited significant toxicity.
The toxicity tests included growth and survival of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location. Samples collected in 2005 and 2006, in the data file associated with this LOE, are not included in this LOE because they were included in the previous assessment cycle. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant effect is defined here using a two-tier approach consistent with the method used by the SWAMP program. The effect must be significant when compared to the control sample based on statistical test alpha level of 0.05 (Probability field in data set) AND the mean must be more than 20 percent different from the control (PercentControl field in data set). |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at two lower Salinas River stations (309SAC and 309SSP). |
Temporal Representation: |
The samples were collected in annually in April 2007-2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. QAPP for the Cooperative Monitoring program for Agriculture in Region 3. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57440 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity and did not exhibit significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Coastal Confluences 2008 2009 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The sample was collected at stations 309DAV - Salinas River at Davis Road. |
Temporal Representation: |
The sample was collected in May 2009. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79703 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Three samples were collected to evaluate sediment toxicity. One of the three samples exhibited significant toxicity. The toxicity tests included survival and growth of Hyalella azteca. Statistically significant effects on Hyalella azteca were observed in the sample collected on 10/28/2009. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity was defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. The t-test is used to determine if there is a statistically significant decrease in organism response in the sample as compared to the control. In the SWAMP data format, a Significance Effect Code of SL denotes toxic test results. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) station 309DAV-Salinas River at Davis Road. |
Temporal Representation: |
The samples were collected in July and October 2008 and October 2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79757 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Nine samples were collected to evaluate water toxicity. Two of the nine samples exhibited significant toxicity. All nine samples were tested for toxicity to Ceriodaphnia dubia and one of those samples was also tested using Hyalella azteca. Statistically significant effects on Hyalella azteca were observed in the sample collected on 10/14/09. Statistically significant effects on Ceriodaphnia dubia were observed in the sample collected on 10/22/2009. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity was defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. The t-test is used to determine if there is a statistically significant decrease in organism response in the sample as compared to the control. In the SWAMP data format, a Significance Effect Code of SL denotes toxic test results. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) station 309DAV-Salinas River at Davis Road. |
Temporal Representation: |
The samples were collected between January 2008 and October 2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79755 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Nine samples were collected to evaluate water toxicity. Five of the 9 samples exhibited significant toxicity. The toxicity tests for the samples included survival and reproduction of Ceriodaphnia dubia, survival and growth of Pimephales promelas and total cell count (growth) of Selenastrum capricornutum. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location. Samples collected from station 309SAC resulted in toxic effects to Ceriodaphnia dubia on 1/24/08 and 2/23/08 and to Pimephales promelas on 2/28/08. Samples collected from station 309SSP resulted in toxic effects to Ceriodaphnia dubia on 1/24/08 and 1/20/10 and to Pimephales promelas 2/23/08.
Samples collected in 2005 and 2006, in the data file associated with this LOE, are not included in this LOE because they were included in the previous assessment cycle. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant effect is defined here using a two-tier approach consistent with the method used by the SWAMP program. The effect must be significant when compared to the control sample based on statistical test alpha level of 0.05 (Probability field in data set) AND the mean must be more than 20 percent different from the control (PercentControl field in data set). |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at two station in the lower Salinas River (309SAC and 309SSP). |
Temporal Representation: |
The samples were collected from January 2008 to March 2010. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. QAPP for the Cooperative Monitoring program for Agriculture in Region 3. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
59001 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Two samples were collected to evaluate water toxicity. One of the samples exhibited significant toxicity to Selenastrum capricornutum but had no significant effects to either Ceriodaphnia dubia, or Pimephales promelas. The significant effect to S. capricornutum is not counted as an exceedance here because the conductivity of the sample water was above the threshold for which a high salinity control should have been used to evaluate the toxicity of the sample. SWAMP guidance (July 2013) for Selenastrum capricornutum toxicity testing is twofold; 1) inclusion of appropriate salinity controls when sample conductivities exceed 1500 uS/cm and 2) if conductivity exceeds 3000 uS/cm, use alternate species or forgo testing. The conductivity of the sample water from September 22, 2009 was higher than 1500 uS/cm but the significance of the toxic effect for the sample result was not calculated using the high salinity control sample and therefore should not be counted as an exceedance. |
Data Reference: |
Coastal Confluences 2008 2009 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at stations 309DAVxxx - Salinas River (lower) at Davis Road. |
Temporal Representation: |
The samples were collected in March and September 2009. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51331 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 4 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51193 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
14 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 14 of 39 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52965 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 5 of 8 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/10/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 131921, Benthic Community Effects
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12888 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
45 |
Number of Exceedances: |
23 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 23 of 45 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57407 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for DDT, Total. Data assessed were suspended sediment samples isolated from the whole water sample. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for total DDTs is 572 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-2/25/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155975 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155929 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 7 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155866 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156038 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155885 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 7 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155990 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155927 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155917 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155898 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155799 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155852 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57243 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for DDT. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDT is 62.9 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57242 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for DDT. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDT is 62.9 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57256 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for DDT. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDT is 62.9 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57257 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for DDT. Data assessed were suspended sediment samples isolated from the whole water sample. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDT is 62.9 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-2/25/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57406 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for DDT, Total. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for total DDTs is 572 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57405 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for DDT, Total. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for total DDTs is 572 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156021 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Total DDTs from MacDonald et al., 2000a which states that the probable effect concentration for Total DDTs is 572 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57390 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for DDT, Total. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for total DDTs is 572 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153036 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153074 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153188 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153176 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153152 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153130 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153248 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153153 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153190 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153289 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153327 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153053 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for DDT (Dichlorodiphenyltrichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDT from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDT is 62.9 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57226 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDT(p,p). Nine sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The DDT criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater is 0.001 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57228 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDT(p,p). Nine sample result(s) were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The DDT criteria for the protection of human health from consumption of organisms only is 0.00059 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57227 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDT(p,p). Nine sample result(s) were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The DDT(p,p) criteria for the protection of human health from the consumption of water and organisms is 0.00059 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57229 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDT(p,p). Nine sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The DDT criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater is 0.001 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
30008 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Fish Migration | Fish Spawning | Preservation of Rare & Endangered Species | Warm Freshwater Habitat | Wildlife Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Nine samples were analyzed by solid phase extraction after an approximately 30 day exposure, in-situ, to known volumes of water. Nine separate sample events were conducted by CCLEAN staff. Two of the 9 samples exceed the Criteria Continuous Concentration. |
Data Reference: |
Final Data CCLEAN Mussel Tissue and Solid Phase Extraction data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentration which are toxic to, or which produce detrimental physiological responses in human, plant, animal, or aquatic life (Central Coast Water Quality Control Plan, general Objective, Section II.A.2.a). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
The Criteria Continuous Concentration (CCC) or the the highest concentration of a pollutant to which aquatic life can be exposed for an extended period of time (4 days) without deleterious effects for 4,4'-DDT is 0.001 ug/L (USEPA. Federal Register, 40 CFR Part 131 (Vol.65, No. 97. May 18, 2000.) ) |
Guideline Reference: |
Water Quality Standards; Establishment of Numeric Criteria for Priority Toxic Pollutants for the State of California; Rule. 40 CFR Part 131. U.S. Environmental Protection Agency, Region IX, Water Division, San Francisco, CA |
|
Spatial Representation: |
Single sample location, Salinas River 1.6 miles below Blanco Road on north shore (Lat, N 36.6950, Long, W 121.7502) |
Temporal Representation: |
Nine separate (approximate 30 day) sample events. The first was initiated on October 5th, 2002 and the ninth event was initiated on October 10th, 2006. |
Environmental Conditions: |
Water from the sample source (i.e., river) is pumped sequentially through a 0.45 micron glass-fiber particle filter, then through a column packed with XAD-2 resin beads, to which nonpolar compounds adsorb. Sampling rates are set to optimum volumes to ensure maximum extraction of target compounds from the sample water. Samples are pumped on a flow-proportioned basis to achieve the desired sample volumes over an approximately 30-day period. This requires predictions of total river discharges during the sampling period, which predictions are not always borne out, resulting in either longer sampling periods or higher or lower than the targeted sample volume. Higher sample volumes provide lower analytical detection limits. Both the particle filter and resin beads are extracted in the laboratory and the extracts are combined and analyzed to provide a total concentration of each compound in the extracted volume of water. |
QAPP Information: |
CCLEAN has an approved QAPP |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
30001 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Nine samples were analyzed by solid phase extraction after an approximately 30 day exposure, in-situ, to known volumes of water. Nine separate sample events were conducted by CCLEAN staff. Three of the 9 samples exceed the Human Health Criteria. |
Data Reference: |
Final Data CCLEAN Mussel Tissue and Solid Phase Extraction data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Human Health Criteria, for the consumption of water, set for 4,4'-DDT is 0.00059 ug/L (USEPA. Federal Register, 40 CFR Part 131 (Vol.65, No. 97. May 18, 2000)). |
Objective/Criterion Reference: |
Water Quality Standards; Establishment of Numeric Criteria for Priority Toxic Pollutants for the State of California; Rule. 40 CFR Part 131. U.S. Environmental Protection Agency, Region IX, Water Division, San Francisco, CA |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Single sample location, Salinas River 1.6 miles below Blanco Road on north shore (Lat, N 36.6950, Long, W 121.7502) |
Temporal Representation: |
Nine separate (approximate 30 day) sample events. The first was initiated on October 5th, 2002 and the ninth event was initiated on October 10th, 2006. |
Environmental Conditions: |
Water from the sample source (i.e., river) is pumped sequentially through a 0.45 micron glass-fiber particle filter, then through a column packed with XAD-2 resin beads, to which nonpolar compounds adsorb. Sampling rates are set to optimum volumes to ensure maximum extraction of target compounds from the sample water. Samples are pumped on a flow-proportioned basis to achieve the desired sample volumes over an approximately 30-day period. This requires predictions of total river discharges during the sampling period, which predictions are not always borne out, resulting in either longer sampling periods or higher or lower than the targeted sample volume. Higher sample volumes provide lower analytical detection limits. Both the particle filter and resin beads are extracted in the laboratory and the extracts are combined and analyzed to provide a total concentration of each compound in the extracted volume of water. |
QAPP Information: |
CCLEAN has an approved QAPP |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57255 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for DDT. Data assessed were suspended sediment samples isolated from the whole water sample. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDT is 62.9 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-2/25/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57241 |
|
Pollutant: |
DDT (Dichlorodiphenyltrichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for DDT. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDT is 62.9 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57421 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for DDT, Total. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for total DDTs is 572 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 129832, DDT (Dichlorodiphenyltrichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57422 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for DDT, Total. Data assessed were suspended sediment samples isolated from the whole water sample. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for total DDTs is 572 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-2/25/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182162 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
47 |
Number of Exceedances: |
31 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 31 of 47 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 40 NTU or greater can cause a reduced foraging efficiency and a shift in prey selection in piscivorous fish (largemouth bass) due to interference with their ability to find prey (Shoup, D.E. and Wahl D.H., 2009). |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183060 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
36 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 36 of 44 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183062 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
13 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 13 of 31 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2014-09-09 and 2017-04-12 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183086 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
17 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 17 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182098 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
47 |
Number of Exceedances: |
39 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 39 of 47 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51331 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 4 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51193 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
14 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 14 of 39 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52965 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 5 of 8 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/10/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57467 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
32 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 32 of 38 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12723 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
14 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 14 of 24 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 4/24/2000-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12888 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
45 |
Number of Exceedances: |
23 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 23 of 45 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12905 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 7/6/2001-8/29/2001. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
13719 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
17 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Central Coast Watershed Studies (R3_CCOWS) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 17 of 38 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCoWS (Central Coast Watershed Studies) Water Quality Data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ Davis Rd, Del Monte Rd] |
Temporal Representation: |
Data was collected over the time period 3/13/2002-10/21/2003. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14491 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
26 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 26 of 44 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15313 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
194 |
Number of Exceedances: |
85 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 85 of 194 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-10/10/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51470 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Turbidities of 40 NTU or greater can cause a reduction in piscivorous fish (largemouth bass) growth due to interference with their ability to find food (Shoup, D.E. and Wahl D.H., 2009). |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12906 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 7/6/2001-8/29/2001. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52973 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 8 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 40 NTU or greater can cause a reduction in piscivorous fish (largemouth bass) growth due to interference with their ability to find food (Shoup, D.E. and Wahl D.H., 2009). |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/10/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
13720 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
17 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Central Coast Watershed Studies (R3_CCOWS) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 17 of 38 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCoWS (Central Coast Watershed Studies) Water Quality Data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ Davis Rd, Del Monte Rd] |
Temporal Representation: |
Data was collected over the time period 3/13/2002-10/21/2003. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57454 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
26 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 26 of 38 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Shoup, D.E. and D.H. Wahl (2009) states that largemouth bass had more difficulty in capturing rapidly moving fish prey at 40 NTU and the overall foraging rate was much lower. |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51469 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
9 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 9 of 39 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Turbidities of 40 NTU or greater can cause a reduction in piscivorous fish (largemouth bass) growth due to interference with their ability to find food (Shoup, D.E. and Wahl D.H., 2009). |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182264 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
14 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 6 of 14 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 40 NTU or greater can cause a reduced foraging efficiency and a shift in prey selection in piscivorous fish (largemouth bass) due to interference with their ability to find prey (Shoup, D.E. and Wahl D.H., 2009). |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182079 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
14 |
Number of Exceedances: |
9 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 9 of 14 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182056 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
17 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 17 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 40 NTU or greater can cause a reduced foraging efficiency and a shift in prey selection in piscivorous fish (largemouth bass) due to interference with their ability to find prey (Shoup, D.E. and Wahl D.H., 2009). |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14492 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
26 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 26 of 44 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182353 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
10 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 10 of 31 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 40 NTU or greater can cause a reduced foraging efficiency and a shift in prey selection in piscivorous fish (largemouth bass) due to interference with their ability to find prey (Shoup, D.E. and Wahl D.H., 2009). |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2014-09-09 and 2017-04-12 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182118 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 40 NTU or greater can cause a reduced foraging efficiency and a shift in prey selection in piscivorous fish (largemouth bass) due to interference with their ability to find prey (Shoup, D.E. and Wahl D.H., 2009). |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182329 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
18 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 18 of 38 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 40 NTU or greater can cause a reduced foraging efficiency and a shift in prey selection in piscivorous fish (largemouth bass) due to interference with their ability to find prey (Shoup, D.E. and Wahl D.H., 2009). |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182266 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
95 |
Number of Exceedances: |
31 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 31 of 95 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 40 NTU or greater can cause a reduced foraging efficiency and a shift in prey selection in piscivorous fish (largemouth bass) due to interference with their ability to find prey (Shoup, D.E. and Wahl D.H., 2009). |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183041 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
27 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 27 of 38 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183231 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182084 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
29 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 29 of 44 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 40 NTU or greater can cause a reduced foraging efficiency and a shift in prey selection in piscivorous fish (largemouth bass) due to interference with their ability to find prey (Shoup, D.E. and Wahl D.H., 2009). |
Guideline Reference: |
The Effects of Turbidity on Prey Selection by Piscivorous Largemouth Bass |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12724 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
14 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 14 of 24 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 4/24/2000-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15314 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
194 |
Number of Exceedances: |
85 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 85 of 194 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-10/10/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12889 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
45 |
Number of Exceedances: |
23 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 23 of 45 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108294, Turbidity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182993 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
95 |
Number of Exceedances: |
40 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 40 of 95 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. (Basin Plan) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Turbidities of 25 NTU or greater can cause a reduction in juvenile salmonid growth due to interference with their ability to find food (Sigler et al. 1984). |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57501 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
40 |
Number of Exceedances: |
21 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 21 of 40 samples exceed the criterion for pH. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Region Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52890 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 6 of 8 samples exceed the criterion for pH. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Region Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/10/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
47826 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Region 3 - Central Coast Region staff assessed R3 public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 9 samples exceed the criterion for pH. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Region Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009 3:40:00 PM. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
A QAPP was not specifically written for this project. However, staff conducting data collection and laboratory analysis are also SWAMP contractors. All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in |
QAPP Information Reference(s): |
2002. Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. California Department of Fish and Game, Monterey, CA |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
11008 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
51 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 3 of 51 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51427 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for pH. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Region Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51410 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
39 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 39 samples exceed the criterion for pH. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Region Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
11273 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
27 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 7 of 27 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 11/30/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
11030 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 4 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 7/6/2001-8/14/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
11046 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 4 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 7/6/2001-8/14/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
10987 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
27 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 3 of 27 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 11/30/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
11009 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
51 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 51 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57500 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
17 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 17 of 40 samples exceed the criterion for pH. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 7.0 or raised above 8.5 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52914 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 8 samples exceed the criterion for pH. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 7.0 or raised above 8.5 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/10/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51192 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for pH. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 7.0 or raised above 8.5 (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51191 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 39 samples exceed the criterion for pH. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 7.0 or raised above 8.5 (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
47827 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Region 3 - Central Coast Region staff assessed R3 public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 9 samples exceed the criterion for pH. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 7.0 or raised above 8.5 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009 3:40:00 PM. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
A QAPP was not specifically written for this project. However, staff conducting data collection and laboratory analysis are also SWAMP contractors. All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in |
QAPP Information Reference(s): |
2002. Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. California Department of Fish and Game, Monterey, CA |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
19096 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
15 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 15 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15304 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
184 |
Number of Exceedances: |
102 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 102 of 184 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-10/10/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14760 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
43 |
Number of Exceedances: |
9 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 9 of 43 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51373 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
39 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 39 samples exceed the criterion for pH. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 6.5 or raised above 8.3 (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51374 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 4 samples exceed the criterion for pH. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 6.5 or raised above 8.3 (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57499 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
40 |
Number of Exceedances: |
24 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 24 of 40 samples exceed the criterion for pH. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 6.5 or raised above 8.3 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15305 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
184 |
Number of Exceedances: |
123 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 123 of 184 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin, Section II.A.2. Municipal and Domestic Supply Objectives, Section II.A.2.a states the following: The pH value shall neither be depressed below 6.5 or raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-10/10/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
11010 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
51 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 7 of 51 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin, Section II.A.2. Municipal and Domestic Supply Objectives, Section II.A.2.a states the following: The pH value shall neither be depressed below 6.5 or raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
47828 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Region 3 - Central Coast Region staff assessed R3 public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 9 samples exceed the criterion for pH. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 6.5 or raised above 8.3 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009 3:40:00 PM. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
A QAPP was not specifically written for this project. However, staff conducting data collection and laboratory analysis are also SWAMP contractors. All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in |
QAPP Information Reference(s): |
2002. Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. California Department of Fish and Game, Monterey, CA |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14761 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
43 |
Number of Exceedances: |
18 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 18 of 43 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin, Section II.A.2. Municipal and Domestic Supply Objectives, Section II.A.2.a states the following: The pH value shall neither be depressed below 6.5 or raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
10988 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
27 |
Number of Exceedances: |
12 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 12 of 27 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin, Section II.A.2. Municipal and Domestic Supply Objectives, Section II.A.2.a states the following: The pH value shall neither be depressed below 6.5 or raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 11/30/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
11047 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 4 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin, Section II.A.2. Municipal and Domestic Supply Objectives, Section II.A.2.a states the following: The pH value shall neither be depressed below 6.5 or raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 7/6/2001-8/14/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52917 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 6 of 8 samples exceed the criterion for pH. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 6.5 or raised above 8.3 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/10/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
19112 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
15 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 15 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin, Section II.A.2. Municipal and Domestic Supply Objectives, Section II.A.2.a states the following: The pH value shall neither be depressed below 6.5 or raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
47829 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
9 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Region 3 - Central Coast Region staff assessed R3 public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 9 samples exceed the criterion for pH. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall neither be depressed below 6.5 nor raised above 8.3 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009 3:40:00 PM. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
A QAPP was not specifically written for this project. However, staff conducting data collection and laboratory analysis are also SWAMP contractors. All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in |
QAPP Information Reference(s): |
2002. Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. California Department of Fish and Game, Monterey, CA |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57482 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
40 |
Number of Exceedances: |
24 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 24 of 40 samples exceed the criterion for pH. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall neither be depressed below 6.5 nor raised above 8.3 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
19113 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
15 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 15 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
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Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
11048 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
4 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 4 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
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Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 7/6/2001-8/14/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15320 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
184 |
Number of Exceedances: |
123 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 123 of 184 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-10/10/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14762 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
43 |
Number of Exceedances: |
18 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 18 of 43 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
11011 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
51 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 7 of 51 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
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Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52950 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
8 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 6 of 8 samples exceed the criterion for pH. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall neither be depressed below 6.5 nor raised above 8.3 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/10/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51412 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
4 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 4 samples exceed the criterion for pH. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall neither be depressed below 6.5 nor raised above 8.3 (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51411 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
39 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 39 samples exceed the criterion for pH. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall neither be depressed below 6.5 nor raised above 8.3 (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178382 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
47 |
Number of Exceedances: |
19 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 19 of 47 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177599 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-22 and 2012-07-22 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178075 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-22 and 2012-07-22 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178469 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
31 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 31 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2014-09-09 and 2017-04-12 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177663 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309PS0370) |
Temporal Representation: |
The samples were collected between the dates of 2017-06-13 and 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
176903 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-22 and 2012-07-22 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
176905 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
18 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 18 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178015 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177228 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178057 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-08-15 and 2012-08-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
176883 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177752 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178809 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
99 |
Number of Exceedances: |
9 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 9 of 99 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177650 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 38 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178173 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
31 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 31 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2014-09-09 and 2017-04-12 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178527 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
44 |
Number of Exceedances: |
8 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 8 of 44 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177226 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
18 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 7 of 18 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179648 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179268 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179562 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
9 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 9 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2014-06-18 and 2018-11-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177912 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179227 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 38 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
176746 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 44 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
176907 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178559 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178171 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179319 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178344 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-22 and 2012-07-22 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178624 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
9 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 9 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2014-06-18 and 2018-11-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177189 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
18 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 7 of 18 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178197 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-08-15 and 2012-08-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178029 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
47 |
Number of Exceedances: |
21 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 21 of 47 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178870 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
24 |
Number of Exceedances: |
14 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 14 of 24 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178763 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 9 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2014-06-18 and 2018-11-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177894 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
18 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 7 of 18 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177351 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
38 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 38 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177685 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-22 and 2012-07-22 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179274 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179589 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
99 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 5 of 99 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179462 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 44 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177801 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 9 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2014-06-18 and 2018-11-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
176955 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
176878 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 7 of 24 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177699 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
31 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 31 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2014-09-09 and 2017-04-12 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
176888 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
47 |
Number of Exceedances: |
15 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 15 of 47 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177005 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 9 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2014-06-18 and 2018-11-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179391 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 31 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2014-09-09 and 2017-04-12 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178907 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
99 |
Number of Exceedances: |
11 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 11 of 99 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177208 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 31 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2014-09-09 and 2017-04-12 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
10989 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
27 |
Number of Exceedances: |
12 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 12 of 27 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 11/30/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
19114 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
15 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 15 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57481 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
17 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 17 of 40 samples exceed the criterion for pH. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 7.0 or raised above 8.5 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15321 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
184 |
Number of Exceedances: |
102 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 102 of 184 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-10/10/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14489 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
43 |
Number of Exceedances: |
9 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 9 of 43 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
11027 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
51 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 51 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
10990 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
27 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 3 of 27 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 11/30/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52958 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 8 samples exceed the criterion for pH. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 7.0 or raised above 8.5 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/10/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
11049 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 4 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 7/6/2001-8/14/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51468 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for pH. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 7.0 or raised above 8.5 (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51467 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 39 samples exceed the criterion for pH. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 7.0 or raised above 8.5 (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
19095 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
15 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 15 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177248 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
24 |
Number of Exceedances: |
14 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 14 of 24 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177780 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
44 |
Number of Exceedances: |
8 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 8 of 44 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178174 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
99 |
Number of Exceedances: |
11 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 11 of 99 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178735 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-22 and 2012-07-22 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178866 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177302 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178099 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178329 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
31 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 31 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2014-09-09 and 2017-04-12 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179269 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177402 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177870 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
47 |
Number of Exceedances: |
21 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 21 of 47 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178397 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-08-15 and 2012-08-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178405 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
44 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 44 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178736 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-08-15 and 2012-08-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178361 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177932 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309PS0370) |
Temporal Representation: |
The samples were collected between the dates of 2017-06-13 and 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
176718 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
24 |
Number of Exceedances: |
9 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 9 of 24 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177754 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178170 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178439 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178649 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177606 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-08-15 and 2012-08-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179427 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
18 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 18 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179979 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309PS0370) |
Temporal Representation: |
The samples were collected between the dates of 2017-06-13 and 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177731 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
99 |
Number of Exceedances: |
11 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 11 of 99 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178201 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
24 |
Number of Exceedances: |
14 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 14 of 24 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178460 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177128 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
99 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 5 of 99 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179488 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 7 of 24 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179077 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
176705 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309PS0370) |
Temporal Representation: |
The samples were collected between the dates of 2017-06-13 and 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178000 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 9 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2014-06-18 and 2018-11-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178811 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179367 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
47 |
Number of Exceedances: |
15 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 15 of 47 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
179275 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
44 |
Number of Exceedances: |
8 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 8 of 44 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178592 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309PS0370) |
Temporal Representation: |
The samples were collected between the dates of 2017-06-13 and 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178982 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for warm fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
176856 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for cold fresh water habitat (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 7.0 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-08-15 and 2012-08-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177148 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309PS0370) |
Temporal Representation: |
The samples were collected between the dates of 2017-06-13 and 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177872 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
38 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 38 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178010 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
38 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 38 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178562 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
18 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 7 of 18 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
177385 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178628 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
47842 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Region 3 - Central Coast Region staff assessed R3 public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 9 samples exceed the criterion for pH. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The pH value shall not be depressed below 7.0 or raised above 8.5 (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009 3:40:00 PM. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
A QAPP was not specifically written for this project. However, staff conducting data collection and laboratory analysis are also SWAMP contractors. All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in |
QAPP Information Reference(s): |
2002. Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. California Department of Fish and Game, Monterey, CA |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15195 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
184 |
Number of Exceedances: |
113 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 113 of 184 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-10/10/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14759 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
43 |
Number of Exceedances: |
9 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 9 of 43 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178030 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
38 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 38 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178959 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108279, pH
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
178355 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
47 |
Number of Exceedances: |
21 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 21 of 47 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for municipal and domestic supply (Section 3.3.2 Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries) states that the pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172497 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 5 of 5 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2016-05-07 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
173246 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when nitrate exceeds 30 mg/L (NO3 as N) in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-10 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172117 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-11 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172155 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172475 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
97 |
Number of Exceedances: |
80 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 80 of 97 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57416 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 8 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Staff Report Division of Water Quality Nutrient Screening Tools for Use in the Clean Water Act Section 303(d) Listing Process |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 3/25/2009-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52891 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 5 of 5 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Staff Report Division of Water Quality Nutrient Screening Tools for Use in the Clean Water Act Section 303(d) Listing Process |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 3/5/2007-2/3/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51465 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 4 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SBR-Salinas River at Highway 1 , 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51464 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
33 |
Number of Exceedances: |
29 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 29 of 33 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
48631 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
47 |
Number of Exceedances: |
20 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 20 of 47 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SSP - Salinas River (Lower) at Spreckles, and 309SAC-Salinas River at Chualar bridge on River Road]. |
Temporal Representation: |
Data was collected over the time period 1/30/2007-3/31/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171811 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-11 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171652 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
8 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 8 of 8 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149529 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality standard for Nitrate + Nitrite as N. 1 of these samples were estimates. |
Data Reference: |
CMP water quality data 10/17/2018--12/20/2018. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data were collected from 1 station. Station Code(s): 309SSP |
Temporal Representation: |
Data for this waterbody were collected on 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Data was collected verified in accordance with the Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171734 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
44 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 44 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) is 10. mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171826 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 7 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) is 10. mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171844 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 4 of 7 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171682 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
26 |
Number of Exceedances: |
23 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 23 of 26 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149527 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality standard for Nitrate + Nitrite as N. 1 of these samples were estimates. |
Data Reference: |
CMP water quality data 10/17/2018--12/20/2018. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data were collected from 1 station. Station Code(s): 309SSP |
Temporal Representation: |
Data for this waterbody were collected on 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Data was collected verified in accordance with the Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171475 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) is 10. mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-11 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171817 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
16 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 16 of 39 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171819 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 5 of 8 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) is 10. mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171839 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
39 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 39 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nitrate + nitrite for livestock watering as 100 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171845 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
26 |
Number of Exceedances: |
23 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 23 of 26 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171970 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
8 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 8 of 8 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171971 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nitrate + nitrite for livestock watering as 100 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2011-10-05 and 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171882 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
45 |
Number of Exceedances: |
14 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 14 of 45 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149526 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Nitrate + Nitrite as N. 1 of these samples were estimates. |
Data Reference: |
CMP water quality data 10/17/2018--12/20/2018. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nitrate + nitrite for livestock watering as 100 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data were collected from 1 station. Station Code(s): 309SSP |
Temporal Representation: |
Data for this waterbody were collected on 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Data was collected verified in accordance with the Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171655 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nitrate + nitrite for livestock watering as 100 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171773 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
16 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 16 of 44 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171866 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
44 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 44 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nitrate + nitrite for livestock watering as 100 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171539 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
26 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 7 of 26 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) is 10. mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171710 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
45 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 45 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nitrate + nitrite for livestock watering as 100 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171712 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nitrate + nitrite for livestock watering as 100 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-11 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171987 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
39 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 39 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) is 10. mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171860 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
16 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 16 of 39 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171958 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
26 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 26 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nitrate + nitrite for livestock watering as 100 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171416 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
45 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 45 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) is 10. mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171733 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
16 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 16 of 44 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
173248 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when nitrate exceeds 30 mg/L (NO3 as N) in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172478 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-11 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171718 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
14 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 14 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate (as N) 10.0 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172557 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
97 |
Number of Exceedances: |
13 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 13 of 97 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when nitrate exceeds 30 mg/L (NO3 as N) in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172549 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172950 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when nitrate exceeds 30 mg/L (NO3 as N) in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172576 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
14 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 14 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when nitrate exceeds 30 mg/L (NO3 as N) in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172118 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
97 |
Number of Exceedances: |
80 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 80 of 97 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172551 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when nitrate exceeds 30 mg/L (NO3 as N) in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172106 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when nitrate exceeds 30 mg/L (NO3 as N) in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172136 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate (as N) 10.0 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172225 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
14 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 4 of 14 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171776 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate (as N) 10.0 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-11 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171757 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate (as N) 10.0 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172093 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when nitrate exceeds 30 mg/L (NO3 as N) in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2016-05-07 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172218 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
23 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 23 of 23 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172430 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171992 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 3 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172021 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
14 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 4 of 14 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172061 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate (as N) 10.0 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172250 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
23 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 23 of 23 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172252 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 5 of 5 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2016-05-07 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171798 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 3 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172077 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate (as N) 10.0 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172085 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171738 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 5 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate (as N) 10.0 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2016-05-07 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172040 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
23 |
Number of Exceedances: |
9 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 9 of 23 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate (as N) 10.0 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172144 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172146 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines listed in the Central Coast Basin Plan and identified as the level that severe problems may occur when nitrate exceeds 30 mg/L (NO3 as N) in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
172237 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171700 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
97 |
Number of Exceedances: |
49 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 49 of 97 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate (as N) 10.0 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
13732 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
107 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Central Coast Watershed Studies (R3_CCOWS) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 5 of 107 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCoWS (Central Coast Watershed Studies) Water Quality Data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 6 monitoring sites [ River Rd (Nr East Garrison), Davis Rd, Del Monte Rd, Chualar River Rd, Blanco Rd, Hwy 68] |
Temporal Representation: |
Data was collected over the time period 10/20/2000-6/10/2003. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51388 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SBR-Salinas River at Highway 1 , 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57404 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 3/25/2009-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51387 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
40 |
Number of Exceedances: |
12 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 12 of 40 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52829 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
31 |
Number of Exceedances: |
8 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 8 of 31 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/7/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
13956 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
34 |
Number of Exceedances: |
10 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Central Coast Long Term Environmental Assessment Program (R3_CCLEAN) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 10 of 34 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCLEAN (Central Coast Long Term Environmental Assessment Program data) Water Quality Data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLR_CCL - Salinas River at Davis Road] |
Temporal Representation: |
Data was collected over the time period 1/22/2002-5/4/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
EPA Approved QAPP. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15172 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
181 |
Number of Exceedances: |
25 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 25 of 181 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-12/4/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
9531 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
51 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 7 of 51 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14320 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-12/13/2005. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
9518 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
60 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 3 of 60 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 2/1/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28163 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
34 |
Number of Exceedances: |
32 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: Central Coast Long Term Environmental Assessment Program (R3_CCLEAN) |
Data Reference: |
Final Data File used for assessment: CCLEAN (Central Coast Long Term Environmental Assessment Program data) Water Quality Data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLR_CCL - Salinas River at Davis Road] |
Temporal Representation: |
Data was collected over the time period 1/22/2002-5/4/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51432 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
33 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 33 of 40 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28146 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
15 |
Number of Exceedances: |
10 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28164 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
34 |
Number of Exceedances: |
32 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: Central Coast Long Term Environmental Assessment Program (R3_CCLEAN) |
Data Reference: |
Final Data File used for assessment: CCoWS (Central Coast Watershed Studies) Water Quality Data |
|
Final Data File used for assessment: CCLEAN (Central Coast Long Term Environmental Assessment Program data) Water Quality Data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLR_CCL - Salinas River at Davis Road] |
Temporal Representation: |
Data was collected over the time period 1/22/2002-5/4/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52853 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
30 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 30 of 31 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Staff Report Division of Water Quality Nutrient Screening Tools for Use in the Clean Water Act Section 303(d) Listing Process |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/7/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28121 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
60 |
Number of Exceedances: |
49 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: CCAMP (Salinas). Fourty-nine of the 60 of the samples exceed the evaluation guideline for nitrate. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ]. |
Temporal Representation: |
Data was collected over the time period 2/1/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. The Salinas Watershed Rotation Area has been monitored twice, in 1999 and in 2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28120 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
51 |
Number of Exceedances: |
43 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: CCAMP Coastal Confluences.
Fourty-three of the 51 of the samples exceed the evaluation guideline for nitrate. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ]. |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28133 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
181 |
Number of Exceedances: |
168 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: National Estuarine Research Reserve Monitoring Program (R3_ESNERR). Monitoring was conducted approximately monthly and 168 of 181 samples exceed the evaluation guideline. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-12/4/2006. Monitoring was conducted approximately monthly. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51433 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 4 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SBR-Salinas River at Highway 1 , 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
18450 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
15 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 15 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57417 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 8 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Staff Report Division of Water Quality Nutrient Screening Tools for Use in the Clean Water Act Section 303(d) Listing Process |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 3/25/2009-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28108 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth). Five of the 7 samples exceed the evaluation guideline for nitrate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-12/13/2005. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52835 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
30 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 30 of 31 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Staff Report Division of Water Quality Nutrient Screening Tools for Use in the Clean Water Act Section 303(d) Listing Process |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/7/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51463 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 4 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SBR-Salinas River at Highway 1 , 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51448 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
33 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 33 of 40 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28122 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
60 |
Number of Exceedances: |
49 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: CCAMP (Salinas). Fourty-nine of the 60 of the samples exceed the evaluation guideline for nitrate. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ]. |
Temporal Representation: |
Data was collected over the time period 2/1/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. The Salinas Watershed Rotation Area has been monitored twice, in 1999 and in 2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28119 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
51 |
Number of Exceedances: |
43 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: CCAMP Coastal Confluences.
Fourty-three of the 51 of the samples exceed the evaluation guideline for nitrate. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ]. |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28132 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
181 |
Number of Exceedances: |
168 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: National Estuarine Research Reserve Monitoring Program (R3_ESNERR). Monitoring was conducted approximately monthly and 168 of 181 samples exceed the evaluation guideline. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-12/4/2006. Monitoring was conducted approximately monthly. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28159 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
107 |
Number of Exceedances: |
81 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: Central Coast Watershed Studies (R3_CCOWS) |
Data Reference: |
Final Data File used for assessment: CCoWS (Central Coast Watershed Studies) Water Quality Data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 6 monitoring sites [ River Rd (Nr East Garrison), Davis Rd, Del Monte Rd, Chualar River Rd, Blanco Rd, Hwy 68] |
Temporal Representation: |
Data was collected over the time period 10/20/2000-6/10/2003. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28145 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
15 |
Number of Exceedances: |
10 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
18451 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
15 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 15 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin Objective for municipal and domestic supply uses of inland surface waters (Section II.A.2) states the following: waters shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Article 4, Chapter 15, Section 64435, Tables 2 and 3 as listed in Table 3-2. The maximum contaminant level listed in Table 3-2 (inorganic and fluoride concentrations not to be exceeded in domestic or municipal supply) for nitrate is 10.0 mg/L (NO3 as N). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Title 22, Division 4, Ch. 15, Article 4, Section 64431, Table 64431-A |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51355 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
40 |
Number of Exceedances: |
22 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 22 of 40 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate (NO3 as N) incorporated by reference in the Basin Plan is 10.0 mg/L (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
13957 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
34 |
Number of Exceedances: |
20 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Central Coast Long Term Environmental Assessment Program (R3_CCLEAN) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 20 of 34 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCLEAN (Central Coast Long Term Environmental Assessment Program data) Water Quality Data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin Objective for municipal and domestic supply uses of inland surface waters (Section II.A.2) states the following: waters shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Article 4, Chapter 15, Section 64435, Tables 2 and 3 as listed in Table 3-2. The maximum contaminant level listed in Table 3-2 (inorganic and fluoride concentrations not to be exceeded in domestic or municipal supply) for nitrate is 10.0 mg/L (NO3 as N). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Title 22, Division 4, Ch. 15, Article 4, Section 64431, Table 64431-A |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLR_CCL - Salinas River at Davis Road] |
Temporal Representation: |
Data was collected over the time period 1/22/2002-5/4/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
EPA Approved QAPP. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
13747 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
107 |
Number of Exceedances: |
18 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Central Coast Watershed Studies (R3_CCOWS) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 18 of 107 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCoWS (Central Coast Watershed Studies) Water Quality Data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin Objective for municipal and domestic supply uses of inland surface waters (Section II.A.2) states the following: waters shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Article 4, Chapter 15, Section 64435, Tables 2 and 3 as listed in Table 3-2. The maximum contaminant level listed in Table 3-2 (inorganic and fluoride concentrations not to be exceeded in domestic or municipal supply) for nitrate is 10.0 mg/L (NO3 as N). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Title 22, Division 4, Ch. 15, Article 4, Section 64431, Table 64431-A |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 6 monitoring sites [ River Rd (Nr East Garrison), Davis Rd, Del Monte Rd, Chualar River Rd, Blanco Rd, Hwy 68] |
Temporal Representation: |
Data was collected over the time period 10/20/2000-6/10/2003. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
9532 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
51 |
Number of Exceedances: |
14 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 14 of 51 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin Objective for municipal and domestic supply uses of inland surface waters (Section II.A.2) states the following: waters shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Article 4, Chapter 15, Section 64435, Tables 2 and 3 as listed in Table 3-2. The maximum contaminant level listed in Table 3-2 (inorganic and fluoride concentrations not to be exceeded in domestic or municipal supply) for nitrate is 10.0 mg/L (NO3 as N). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Title 22, Division 4, Ch. 15, Article 4, Section 64431, Table 64431-A |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14321 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin Objective for municipal and domestic supply uses of inland surface waters (Section II.A.2) states the following: waters shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Article 4, Chapter 15, Section 64435, Tables 2 and 3 as listed in Table 3-2. The maximum contaminant level listed in Table 3-2 (inorganic and fluoride concentrations not to be exceeded in domestic or municipal supply) for nitrate is 10.0 mg/L (NO3 as N). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Title 22, Division 4, Ch. 15, Article 4, Section 64431, Table 64431-A |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-12/13/2005. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15173 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
181 |
Number of Exceedances: |
102 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 102 of 181 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin Objective for municipal and domestic supply uses of inland surface waters (Section II.A.2) states the following: waters shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Article 4, Chapter 15, Section 64435, Tables 2 and 3 as listed in Table 3-2. The maximum contaminant level listed in Table 3-2 (inorganic and fluoride concentrations not to be exceeded in domestic or municipal supply) for nitrate is 10.0 mg/L (NO3 as N). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Title 22, Division 4, Ch. 15, Article 4, Section 64431, Table 64431-A |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-12/4/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51356 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate (NO3 as N) incorporated by reference in the Basin Plan is 10.0 mg/L (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SBR-Salinas River at Highway 1 , 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
9503 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
60 |
Number of Exceedances: |
16 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 16 of 60 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin Objective for municipal and domestic supply uses of inland surface waters (Section II.A.2) states the following: waters shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Article 4, Chapter 15, Section 64435, Tables 2 and 3 as listed in Table 3-2. The maximum contaminant level listed in Table 3-2 (inorganic and fluoride concentrations not to be exceeded in domestic or municipal supply) for nitrate is 10.0 mg/L (NO3 as N). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
Objective/Criterion Reference: |
Title 22, Division 4, Ch. 15, Article 4, Section 64431, Table 64431-A |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 2/1/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57403 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate (NO3 as N) incorporated by reference in the Water Quality Control Plan, Central Coast Region is 10.0 mg/L (Water Quality Control Plan, Central Coast Region). |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 3/25/2009-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52839 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
31 |
Number of Exceedances: |
24 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 24 of 31 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate (NO3 as N) incorporated by reference in the Basin Plan is 10.0 mg/L (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/7/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28109 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth). Five of the 7 samples exceed the evaluation guideline for nitrate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-12/13/2005. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
28160 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
107 |
Number of Exceedances: |
81 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Data for this assessment unit was collected by one monitoring project: Central Coast Watershed Studies (R3_CCOWS) |
Data Reference: |
Final Data File used for assessment: CCoWS (Central Coast Watershed Studies) Water Quality Data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 6 monitoring sites [ River Rd (Nr East Garrison), Davis Rd, Del Monte Rd, Chualar River Rd, Blanco Rd, Hwy 68] |
Temporal Representation: |
Data was collected over the time period 10/20/2000-6/10/2003. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51372 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) that is incorporated by reference in the Basin Plan is 10.0 mg/L (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SBR-Salinas River at Highway 1 , 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51371 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
33 |
Number of Exceedances: |
18 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 18 of 33 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) that is incorporated by reference in the Basin Plan is 10.0 mg/L (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15171 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 5 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
OEHHA public Health Goals for Nitrate and Nitrogen in Drinking Water (December 1997). Page 6. |
Objective/Criterion Reference: |
Public health goals for nitrate and nitrite in drinking water |
|
Evaluation Guideline: |
OEHHA Public Health Goal states that sum of the concentration of nitrate + nitrite shall not exceed 10 mg/L (NO3+NO2 expressed as N). |
Guideline Reference: |
Public health goals for nitrate and nitrite in drinking water |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/10/2006-11/7/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14482 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
34 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 34 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
OEHHA public Health Goals for Nitrate and Nitrogen in Drinking Water (December 1997). Page 6. |
Objective/Criterion Reference: |
Public health goals for nitrate and nitrite in drinking water |
|
Evaluation Guideline: |
OEHHA Public Health Goal states that sum of the concentration of nitrate + nitrite shall not exceed 10 mg/L (NO3+NO2 expressed as N). |
Guideline Reference: |
Public health goals for nitrate and nitrite in drinking water |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52894 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 5 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) that is incorporated by reference in the Basin Plan is 10.0 mg/L (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 3/5/2007-2/3/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57401 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
47 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 47 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) that is incorporated by reference in the Water Quality Control Plan, Central Coast Region is 10.0 mg/L (California Code of Regulation, Title 22, Division 4, Chapter 15, Section 64431, Table 64431-A). |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-3/31/2010. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51434 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
33 |
Number of Exceedances: |
29 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 29 of 33 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
48639 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
47 |
Number of Exceedances: |
20 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 20 of 47 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SSP - Salinas River (Lower) at Spreckles, 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-3/31/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51449 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 4 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SBR-Salinas River at Highway 1 , 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52857 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 5 of 5 samples exceed the criterion for Nitrate/Nitrite as N. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Staff Report Division of Water Quality Nutrient Screening Tools for Use in the Clean Water Act Section 303(d) Listing Process |
Guideline Reference: |
Technical Approach to Develop Nutrient Numeric Endpoints for California. U.S. EPA Region IX. State Water Resources Control Board. 68-C-02-108-To-111 |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 3/5/2007-2/3/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171696 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 2 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2011-10-05 and 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171880 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 2 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2011-10-05 and 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171611 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 2 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) is 10. mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2011-10-05 and 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171531 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 4 of 7 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171395 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-11 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171573 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
45 |
Number of Exceedances: |
14 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 14 of 45 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Technical approach to develop nutrient numeric endpoints for California, Tetra Tech, June 2006. The Central Coast Region numeric target for maximum nitrate concentration is based on the Tetra Tech NNE (Nutrient Numeric Endpoint) Model and CCAMP data for 193 sites, monitored monthly for at least 1 year between January 1998 and December 2006. The model numeric target for aquatic life habitats in the Central Coast Region is 1.0 mg/L Nitrate as N. |
Guideline Reference: |
Central Coast RegionTechnical Paper: Interpreting Narrative Objectives for Biostimulatory Substances for California Central Coast Waters. This method uses the Technical Approach for Developing California Nutrient Numeric Endpoints. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149528 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Nitrate + Nitrite as N. 1 of these samples were estimates. |
Data Reference: |
CMP water quality data 10/17/2018--12/20/2018. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) is 10. mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
Data were collected from 1 station. Station Code(s): 309SSP |
Temporal Representation: |
Data for this waterbody were collected on 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Data was collected verified in accordance with the Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 128101, Nitrate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171891 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 7 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nitrate + nitrite for livestock watering as 100 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2012-08-08 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24514 |
|
Pollutant: |
Plant Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 9 samples exceed the criterion for Toxicity, Selenastrum capricornutum Growth (Cell Density) 4 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction in cell count of test organism relative to the control (alpha < 0.05) and cell count <80% of control. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 2/17/2005-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57451 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity. None of the samples exhibited significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at stations 309DAVxxx. |
Temporal Representation: |
The sample was collected in June 2008. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79704 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Five samples were collected to evaluate sediment toxicity. None of the 5 samples exhibited significant toxicity.
The toxicity tests included growth and survival of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location. Samples collected in 2005 and 2006, in the data file associated with this LOE, are not included in this LOE because they were included in the previous assessment cycle. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant effect is defined here using a two-tier approach consistent with the method used by the SWAMP program. The effect must be significant when compared to the control sample based on statistical test alpha level of 0.05 (Probability field in data set) AND the mean must be more than 20 percent different from the control (PercentControl field in data set). |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at two lower Salinas River stations (309SAC and 309SSP). |
Temporal Representation: |
The samples were collected in annually in April 2007-2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. QAPP for the Cooperative Monitoring program for Agriculture in Region 3. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57440 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity and did not exhibit significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Coastal Confluences 2008 2009 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The sample was collected at stations 309DAV - Salinas River at Davis Road. |
Temporal Representation: |
The sample was collected in May 2009. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79703 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Three samples were collected to evaluate sediment toxicity. One of the three samples exhibited significant toxicity. The toxicity tests included survival and growth of Hyalella azteca. Statistically significant effects on Hyalella azteca were observed in the sample collected on 10/28/2009. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity was defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. The t-test is used to determine if there is a statistically significant decrease in organism response in the sample as compared to the control. In the SWAMP data format, a Significance Effect Code of SL denotes toxic test results. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) station 309DAV-Salinas River at Davis Road. |
Temporal Representation: |
The samples were collected in July and October 2008 and October 2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79702 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity and did not exhibit significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Coastal Confluences 2008 2009 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The sample was collected at stations 309DAV - Salinas River at Davis Road. |
Temporal Representation: |
The sample was collected in May 2009. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57424 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Five samples were collected to evaluate sediment toxicity. None of the 5 samples exhibited significant toxicity.
The toxicity tests included growth and survival of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location. Samples collected in 2005 and 2006, in the data file associated with this LOE, are not included in this LOE because they were included in the previous assessment cycle. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant effect is defined here using a two-tier approach consistent with the method used by the SWAMP program. The effect must be significant when compared to the control sample based on statistical test alpha level of 0.05 (Probability field in data set) AND the mean must be more than 20 percent different from the control (PercentControl field in data set). |
Guideline Reference: |
Major and Trace Element Analytical Methods of the National Status and Trends Program: 2000-2006. |
|
Spatial Representation: |
The samples were collected at two lower Salinas River stations (309SAC and 309SSP). |
Temporal Representation: |
The samples were collected in annually in April 2007-2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. QAPP for the Cooperative Monitoring program for Agriculture in Region 3. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57439 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Three samples were collected to evaluate sediment toxicity. One of the three samples exhibited significant toxicity. The toxicity tests included survival and growth of Hyalella azteca. Statistically significant effects on Hyalella azteca were observed in the sample collected on 10/28/2009. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity was defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. The t-test is used to determine if there is a statistically significant decrease in organism response in the sample as compared to the control. In the SWAMP data format, a Significance Effect Code of SL denotes toxic test results. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
Guideline Reference: |
Short-term Methods for Estimating the Chronic Toxicity of Effluents and Receiving Waters to Freshwater Organisms. Fourth Edition. Office of Water, U.S. Environmental Protection Agency. Washington, D.C. EPA-821-R-02-013 |
|
Spatial Representation: |
The samples were collected at Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) station 309DAV-Salinas River at Davis Road. |
Temporal Representation: |
The samples were collected in July and October 2008 and October 2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79701 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity. None of the samples exhibited significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at stations 309DAVxxx. |
Temporal Representation: |
The sample was collected in June 2008. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79757 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Nine samples were collected to evaluate water toxicity. Two of the nine samples exhibited significant toxicity. All nine samples were tested for toxicity to Ceriodaphnia dubia and one of those samples was also tested using Hyalella azteca. Statistically significant effects on Hyalella azteca were observed in the sample collected on 10/14/09. Statistically significant effects on Ceriodaphnia dubia were observed in the sample collected on 10/22/2009. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity was defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. The t-test is used to determine if there is a statistically significant decrease in organism response in the sample as compared to the control. In the SWAMP data format, a Significance Effect Code of SL denotes toxic test results. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) station 309DAV-Salinas River at Davis Road. |
Temporal Representation: |
The samples were collected between January 2008 and October 2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79755 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Nine samples were collected to evaluate water toxicity. Five of the 9 samples exhibited significant toxicity. The toxicity tests for the samples included survival and reproduction of Ceriodaphnia dubia, survival and growth of Pimephales promelas and total cell count (growth) of Selenastrum capricornutum. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location. Samples collected from station 309SAC resulted in toxic effects to Ceriodaphnia dubia on 1/24/08 and 2/23/08 and to Pimephales promelas on 2/28/08. Samples collected from station 309SSP resulted in toxic effects to Ceriodaphnia dubia on 1/24/08 and 1/20/10 and to Pimephales promelas 2/23/08.
Samples collected in 2005 and 2006, in the data file associated with this LOE, are not included in this LOE because they were included in the previous assessment cycle. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant effect is defined here using a two-tier approach consistent with the method used by the SWAMP program. The effect must be significant when compared to the control sample based on statistical test alpha level of 0.05 (Probability field in data set) AND the mean must be more than 20 percent different from the control (PercentControl field in data set). |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at two station in the lower Salinas River (309SAC and 309SSP). |
Temporal Representation: |
The samples were collected from January 2008 to March 2010. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. QAPP for the Cooperative Monitoring program for Agriculture in Region 3. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
59001 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Two samples were collected to evaluate water toxicity. One of the samples exhibited significant toxicity to Selenastrum capricornutum but had no significant effects to either Ceriodaphnia dubia, or Pimephales promelas. The significant effect to S. capricornutum is not counted as an exceedance here because the conductivity of the sample water was above the threshold for which a high salinity control should have been used to evaluate the toxicity of the sample. SWAMP guidance (July 2013) for Selenastrum capricornutum toxicity testing is twofold; 1) inclusion of appropriate salinity controls when sample conductivities exceed 1500 uS/cm and 2) if conductivity exceeds 3000 uS/cm, use alternate species or forgo testing. The conductivity of the sample water from September 22, 2009 was higher than 1500 uS/cm but the significance of the toxic effect for the sample result was not calculated using the high salinity control sample and therefore should not be counted as an exceedance. |
Data Reference: |
Coastal Confluences 2008 2009 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at stations 309DAVxxx - Salinas River (lower) at Davis Road. |
Temporal Representation: |
The samples were collected in March and September 2009. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57438 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Nine samples were collected to evaluate water toxicity. Five of the 9 samples exhibited significant toxicity. The toxicity tests for the samples included survival and reproduction of Ceriodaphnia dubia, survival and growth of Pimephales promelas and total cell count (growth) of Selenastrum capricornutum. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location. Samples collected from station 309SAC resulted in toxic effects to Ceriodaphnia dubia on 1/24/08 and 2/23/08 and to Pimephales promelas on 2/28/08. Samples collected from station 309SSP resulted in toxic effects to Ceriodaphnia dubia on 1/24/08 and 1/20/10 and to Pimephales promelas 2/23/08.
Samples collected in 2005 and 2006, in the data file associated with this LOE, are not included in this LOE because they were included in the previous assessment cycle. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant effect is defined here using a two-tier approach consistent with the method used by the SWAMP program. The effect must be significant when compared to the control sample based on statistical test alpha level of 0.05 (Probability field in data set) AND the mean must be more than 20 percent different from the control (PercentControl field in data set). |
Guideline Reference: |
Major and Trace Element Analytical Methods of the National Status and Trends Program: 2000-2006. |
|
Spatial Representation: |
The samples were collected at two station in the lower Salinas River (309SAC and 309SSP). |
Temporal Representation: |
The samples were collected from January 2008 to March 2010. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. QAPP for the Cooperative Monitoring program for Agriculture in Region 3. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79754 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Two samples were collected to evaluate water toxicity. One of the samples exhibited significant toxicity to Selenastrum capricornutum but had no significant effects to either Ceriodaphnia dubia, or Pimephales promelas. The significant effect to S. capricornutum is not counted as an exceedance here because the conductivity of the sample water was above the threshold for which a high salinity control should have been used to evaluate the toxicity of the sample. SWAMP guidance (July 2013) for Selenastrum capricornutum toxicity testing is twofold; 1) inclusion of appropriate salinity controls when sample conductivities exceed 1500 uS/cm and 2) if conductivity exceeds 3000 uS/cm, use alternate species or forgo testing. The conductivity of the sample water from September 22, 2009 was higher than 1500 uS/cm but the significance of the toxic effect for the sample result was not calculated using the high salinity control sample and therefore should not be counted as an exceedance. |
Data Reference: |
Coastal Confluences 2008 2009 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at stations 309DAVxxx - Salinas River (lower) at Davis Road. |
Temporal Representation: |
The samples were collected in March and September 2009. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
59003 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Nine samples were collected to evaluate water toxicity. Two of the nine samples exhibited significant toxicity. All nine samples were tested for toxicity to Ceriodaphnia dubia and one of those samples was also tested using Hyalella azteca. Statistically significant effects on Hyalella azteca were observed in the sample collected on 10/14/09. Statistically significant effects on Ceriodaphnia dubia were observed in the sample collected on 10/22/2009. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity was defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. The t-test is used to determine if there is a statistically significant decrease in organism response in the sample as compared to the control. In the SWAMP data format, a Significance Effect Code of SL denotes toxic test results. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) station 309DAV-Salinas River at Davis Road. |
Temporal Representation: |
The samples were collected between January 2008 and October 2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24538 |
|
Pollutant: |
Vertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Toxicity, Cyprinodon variegatus Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected on a single day 2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
23983 |
|
Pollutant: |
Vertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 9 samples exceed the criterion for Toxicity, Pimephales promelas Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 2/17/2005-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24503 |
|
Pollutant: |
Vertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Toxicity, Pimephales promelas Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 6/14/2006-2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
23982 |
|
Pollutant: |
Vertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Toxicity, Pimephales promelas Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 6/14/2006-2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24545 |
|
Pollutant: |
Vertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Toxicity, Cyprinodon variegatus Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected on a single day 2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24504 |
|
Pollutant: |
Vertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 9 samples exceed the criterion for Toxicity, Pimephales promelas Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 2/17/2005-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148678 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 1 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Chironomus dilutus, for Survival, Chironomus dilutus, for Growth (wt/surv indiv), Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SBR ) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149068 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00L ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148989 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 7 samples collected by SWAMP RWB3 CCAMP Coastal Confluences for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Selenastrum capricornutum, for Total Cell Count, Pimephales promelas, for Biomass (wt/orig indiv), Chironomus dilutus, for Ash Free Dry Mass, Pimephales promelas, for Survival, Ceriodaphnia dubia, for Young/female, Ceriodaphnia dubia, for Survival, Chironomus dilutus, for Survival, Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2010-02-23 and 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148953 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
2 of the 3 samples collected by RWB3 Salinas Stormwater Project for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Ceriodaphnia dubia, for Survival, Pimephales promelas, for Survival, Pimephales promelas, for Growth (wt/surv indiv), Selenastrum capricornutum, for Total Cell Count, Ceriodaphnia dubia, for Young/female |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SDD ) |
Temporal Representation: |
The samples were collected between the dates of 2011-09-27 and 2012-03-24. |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148676 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
10 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
4 of the 10 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2009-06-16 and 2018-06-05. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148888 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Salinas Rotation for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-23 and 2012-07-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148941 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Chironomus dilutus, for Survival, Hyalella azteca, for Survival, Chironomus dilutus, for Ash Free Dry Mass |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00L ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148792 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAG ) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148830 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00L ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148834 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00U ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148969 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
2 of the 6 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Ceriodaphnia dubia, for Young/female, Chironomus dilutus, for Survival, Pimephales promelas, for Biomass (wt/orig indiv), Ceriodaphnia dubia, for Survival, Pimephales promelas, for Survival, Selenastrum capricornutum, for Total Cell Count |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAG ) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-26 and 2018-03-02. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148926 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Chironomus dilutus, for Survival, Hyalella azteca, for Survival, Chironomus dilutus, for Ash Free Dry Mass |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00L ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148665 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 1 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Chironomus dilutus, for Survival, Chironomus dilutus, for Growth (wt/surv indiv), Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SBR ) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149063 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Confluences for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-23 and 2012-07-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148553 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAG ) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148693 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
10 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
4 of the 10 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2009-06-16 and 2018-06-05. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148717 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 2 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2013-05-28 and 2017-04-26. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148552 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
3 of the 6 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Chironomus dilutus, for Survival, Pimephales promelas, for Survival, Ceriodaphnia dubia, for Young/female, Ceriodaphnia dubia, for Survival, Selenastrum capricornutum, for Total Cell Count, Pimephales promelas, for Biomass (wt/orig indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-26 and 2017-09-27. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148845 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Chironomus dilutus, for Ash Free Dry Mass, Hyalella azteca, for Growth (wt/surv indiv), Chironomus dilutus, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00U ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148976 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Confluences for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-23 and 2012-07-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149049 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00U ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148821 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 6 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Ceriodaphnia dubia, for Young/female, Ceriodaphnia dubia, for Survival, Chironomus dilutus, for Survival, Pimephales promelas, for Survival, Selenastrum capricornutum, for Total Cell Count, Pimephales promelas, for Biomass (wt/orig indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SSP ) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-27 and 2018-04-25. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149022 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 3 samples collected by SWAMP RWB3 CCAMP Salinas Rotation for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Ceriodaphnia dubia, for Young/female, Hyalella azteca, for Survival, Pimephales promelas, for Biomass (wt/orig indiv), Pimephales promelas, for Survival, Ceriodaphnia dubia, for Survival, Chironomus dilutus, for Survival, Chironomus dilutus, for Ash Free Dry Mass, Selenastrum capricornutum, for Total Cell Count |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148711 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 3 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SSP ) |
Temporal Representation: |
The samples were collected between the dates of 2017-07-26 and 2018-04-25. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149038 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 3 samples collected by SWAMP RWB3 CCAMP Salinas Rotation for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Ceriodaphnia dubia, for Young/female, Hyalella azteca, for Survival, Pimephales promelas, for Biomass (wt/orig indiv), Pimephales promelas, for Survival, Ceriodaphnia dubia, for Survival, Chironomus dilutus, for Survival, Chironomus dilutus, for Ash Free Dry Mass, Selenastrum capricornutum, for Total Cell Count |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148983 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
2 of the 6 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Ceriodaphnia dubia, for Young/female, Chironomus dilutus, for Survival, Pimephales promelas, for Biomass (wt/orig indiv), Ceriodaphnia dubia, for Survival, Pimephales promelas, for Survival, Selenastrum capricornutum, for Total Cell Count |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAG ) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-26 and 2018-03-02. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148988 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 7 samples collected by SWAMP RWB3 CCAMP Coastal Confluences for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Selenastrum capricornutum, for Total Cell Count, Pimephales promelas, for Biomass (wt/orig indiv), Chironomus dilutus, for Ash Free Dry Mass, Pimephales promelas, for Survival, Ceriodaphnia dubia, for Young/female, Ceriodaphnia dubia, for Survival, Chironomus dilutus, for Survival, Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2010-02-23 and 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148718 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 2 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2013-05-28 and 2017-04-26. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148955 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
2 of the 3 samples collected by RWB3 Salinas Stormwater Project for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Ceriodaphnia dubia, for Survival, Pimephales promelas, for Survival, Pimephales promelas, for Growth (wt/surv indiv), Selenastrum capricornutum, for Total Cell Count, Ceriodaphnia dubia, for Young/female |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SDD ) |
Temporal Representation: |
The samples were collected between the dates of 2011-09-27 and 2012-03-24. |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148819 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
3 of the 6 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Chironomus dilutus, for Survival, Pimephales promelas, for Survival, Ceriodaphnia dubia, for Young/female, Ceriodaphnia dubia, for Survival, Selenastrum capricornutum, for Total Cell Count, Pimephales promelas, for Biomass (wt/orig indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-26 and 2017-09-27. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148767 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 6 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Ceriodaphnia dubia, for Young/female, Ceriodaphnia dubia, for Survival, Chironomus dilutus, for Survival, Pimephales promelas, for Survival, Selenastrum capricornutum, for Total Cell Count, Pimephales promelas, for Biomass (wt/orig indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SSP ) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-27 and 2018-04-25. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148889 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Salinas Rotation for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-23 and 2012-07-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148712 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 3 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SSP ) |
Temporal Representation: |
The samples were collected between the dates of 2017-07-26 and 2018-04-25. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148897 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Chironomus dilutus, for Ash Free Dry Mass, Hyalella azteca, for Growth (wt/surv indiv), Chironomus dilutus, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00U ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24485 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24564 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-5/26/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24565 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-5/26/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24486 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24556 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Toxicity, Hyalella azteca 10-day survival %. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SBR-Salinas River at Highway 1 ]. |
Temporal Representation: |
Data was collected on a single day 2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24528 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
11 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 11 samples exceed the criterion for Toxicity, Ceriodaphnia dubia Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles]. |
Temporal Representation: |
Data was collected over the time period 2/17/2005-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24520 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 5 samples exceed the criterion for Toxicity, Ceriodaphnia dubia Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 6/14/2006-2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24529 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
11 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 11 samples exceed the criterion for Toxicity, Ceriodaphnia dubia Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 2/17/2005-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24563 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Toxicity, Hyalella azteca sediment 10-day survival %. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected on a single day 2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24527 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 5 samples exceed the criterion for Toxicity, Ceriodaphnia dubia Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 6/14/2006-2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24513 |
|
Pollutant: |
Plant Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 9 samples exceed the criterion for Toxicity, Selenastrum capricornutum Growth (Cell Density) 4 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction in cell count of test organism relative to the control (alpha < 0.05) and cell count <80% of control. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 2/17/2005-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24505 |
|
Pollutant: |
Plant Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Toxicity, Selenastrum capricornutum Growth (Cell Density) 4 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction in cell count of test organism relative to the control (alpha < 0.05) and cell count <80% of control. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 6/14/2006-2/15/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24521 |
|
Pollutant: |
Plant Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Toxicity, Thalassiosira Growth (Cell Density) 4 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction in cell count of test organism relative to the control (alpha < 0.05) and cell count <80% of control. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected on a single day 2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24512 |
|
Pollutant: |
Plant Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Toxicity, Selenastrum capricornutum Growth (Cell Density) 4 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction in cell count of test organism relative to the control (alpha < 0.05) and cell count <80% of control. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 6/14/2006-2/15/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108291, Toxicity
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24522 |
|
Pollutant: |
Plant Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Toxicity, Thalassiosira Growth (Cell Density) 4 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction in cell count of test organism relative to the control (alpha < 0.05) and cell count <80% of control. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected on a single day 2/14/2007. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219577 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Ammonia as N, Unionized. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219407 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 40 samples exceeded the water quality threshold for Ammonia as N, Unionized. Although a total of 92 samples were collected, 52 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2010-07-13 to 2018-11-20 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219406 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 3 of the 39 samples exceeded the water quality threshold for Ammonia as N, Unionized. Although a total of 43 samples were collected, 4 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2010-04-29 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219638 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 3 of the 39 samples exceeded the water quality threshold for Ammonia as N, Unionized. Although a total of 43 samples were collected, 4 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2010-04-29 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219586 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Ammonia as N, Unionized. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-06-26 to 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219435 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 7 samples exceeded the water quality threshold for Ammonia as N, Unionized. Although a total of 15 samples were collected, 8 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2012-01-10 to 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219258 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 9 samples exceeded the water quality threshold for Ammonia as N, Unionized. Although a total of 23 samples were collected, 14 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2012-01-10 to 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219237 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Ammonia as N, Unionized. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149525 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Ammonia as N, Unionized. 1 of these samples were estimates. |
Data Reference: |
CMP water quality data 10/17/2018--12/20/2018. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data were collected from 1 station. Station Code(s): 309SSP |
Temporal Representation: |
Data for this waterbody were collected on 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Data was collected verified in accordance with the Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149524 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Ammonia as N, Unionized. 1 of these samples were estimates. |
Data Reference: |
CMP water quality data 10/17/2018--12/20/2018. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data were collected from 1 station. Station Code(s): 309SSP |
Temporal Representation: |
Data for this waterbody were collected on 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Data was collected verified in accordance with the Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219452 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Ammonia as N, Unionized. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-06-26 to 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219488 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 9 samples exceeded the water quality threshold for Ammonia as N, Unionized. Although a total of 23 samples were collected, 14 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2012-01-10 to 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183724 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
27 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 27 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-05-24 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
184218 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as 'the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure.' |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2011-10-05 and 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183585 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-05-24 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
184095 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183816 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as 'the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure.' |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-11 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183819 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
43 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 43 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as 'the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure.' |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183965 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as 'the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure.' |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
184014 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
14 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 14 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-08 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183841 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-08 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183966 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as 'the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure.' |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
184217 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
39 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 39 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as 'the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure.' |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183808 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
26 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 26 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-05-24 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183744 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
97 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 97 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as 'the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure.' |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183625 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
26 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 26 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-05-24 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183627 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
27 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 27 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-05-24 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
184163 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
60 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 60 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-08-09 and 2018-11-20 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183592 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183747 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as 'the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure.' |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
184343 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183997 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-08 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183913 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149523 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
CMP water quality data 10/17/2018--12/20/2018. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as "the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure." |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
Data were collected from 1 station. Station Code(s): 309SSP |
Temporal Representation: |
Data for this waterbody were collected on 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Data was collected verified in accordance with the Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
184038 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
14 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 14 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-08 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
184041 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
36 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 36 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as 'the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure.' |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183748 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
15 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 15 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as 'the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure.' |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183668 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
60 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 60 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-08-09 and 2018-11-20 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183807 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-05-24 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
183705 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2012 edition of the drinking water standards and health advisories. This Advisory Level is defined as 'the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for a lifetime of exposure.' |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
9499 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 24 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ]. |
Temporal Representation: |
Data was collected over the time period 11/30/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51445 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SBR-Salinas River at Highway 1 , 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/13/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14687 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 39 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57092 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 4 of 40 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51430 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 38 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
9512 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
49 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 49 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road]. |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14694 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 39 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
9500 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 24 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ]. |
Temporal Representation: |
Data was collected over the time period 11/30/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
9513 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
49 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 49 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ]. |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51413 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 38 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57091 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 4 of 40 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51414 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SBR-Salinas River at Highway 1 , 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/13/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51334 |
|
Pollutant: |
Ammonia as Nitrogen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
40 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 40 samples exceed the criterion for Ammonia As N, Total. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2006 edition of the drinking water standards and health advisories. This Advisory Level is defined as "the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for up to ten days of exposure." |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51352 |
|
Pollutant: |
Ammonia as Nitrogen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Ammonia As N, Total. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2006 edition of the drinking water standards and health advisories. This Advisory Level is defined as "the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for up to ten days of exposure." |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SBR-Salinas River at Highway 1 , 309SAC-Salinas River at Chualar bridge on River Road] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57093 |
|
Pollutant: |
Ammonia as Nitrogen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
41 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 41 samples exceed the criterion for Ammonia As N, Total. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. (Basin Plan) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
USEPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2011 edition of the drinking water standards and health advisories. (EPA 822-R-06-013, 2011). |
Guideline Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
9511 |
|
Pollutant: |
Ammonia as Nitrogen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
51 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 51 samples exceed the criterion for Ammonia as N, Total. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
USEPA Health Advisory 2006 Edition of the Drinking Water Standards and Health Advisories (EPA 822-R-06-013, 2006). |
Objective/Criterion Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2006 edition of the drinking water standards and health advisories. This Advisory Level is defined as "the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for up to ten days of exposure." |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
9526 |
|
Pollutant: |
Ammonia as Nitrogen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
60 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 60 samples exceed the criterion for Ammonia as N, Total. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
USEPA Health Advisory 2006 Edition of the Drinking Water Standards and Health Advisories (EPA 822-R-06-013, 2006). |
Objective/Criterion Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2006 edition of the drinking water standards and health advisories. This Advisory Level is defined as "the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for up to ten days of exposure." |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 2/1/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
13972 |
|
Pollutant: |
Ammonia as Nitrogen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
13 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Central Coast Long Term Environmental Assessment Program (R3_CCLEAN) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 13 samples exceed the criterion for Ammonia As N, Total. |
Data Reference: |
Final Data File used for assessment: CCLEAN (Central Coast Long Term Environmental Assessment Program data) Water Quality Data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
USEPA Health Advisory 2006 Edition of the Drinking Water Standards and Health Advisories (EPA 822-R-06-013, 2006). |
Objective/Criterion Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2006 edition of the drinking water standards and health advisories. This Advisory Level is defined as "the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for up to ten days of exposure." |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLR_CCL - Salinas River at Davis Road] |
Temporal Representation: |
Data was collected over the time period 12/2/2003-5/4/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
EPA Approved QAPP. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14483 |
|
Pollutant: |
Ammonia as Nitrogen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
41 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 41 samples exceed the criterion for Ammonia As N, Total. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
USEPA Health Advisory 2006 Edition of the Drinking Water Standards and Health Advisories (EPA 822-R-06-013, 2006). |
Objective/Criterion Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2006 edition of the drinking water standards and health advisories. This Advisory Level is defined as "the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for up to ten days of exposure." |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52920 |
|
Pollutant: |
Ammonia as Nitrogen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
32 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 32 samples exceed the criterion for Ammonia As N, Total. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2006 edition of the drinking water standards and health advisories. This Advisory Level is defined as "the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for up to ten days of exposure." |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/7/2009. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15154 |
|
Pollutant: |
Ammonia as Nitrogen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
172 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 172 samples exceed the criterion for Ammonia As N, Total. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
USEPA Health Advisory 2006 Edition of the Drinking Water Standards and Health Advisories (EPA 822-R-06-013, 2006). |
Objective/Criterion Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Evaluation Guideline: |
EPA's Lifetime Health advisory level for total ammonia is 30.0 mg/L as stated on page 8 of the 2006 edition of the drinking water standards and health advisories. This Advisory Level is defined as "the concentration of a chemical in drinking water that is not expected to cause any adverse noncarcinogenic effects for up to ten days of exposure." |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-12/4/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219266 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 7 samples exceeded the water quality threshold for Ammonia as N, Unionized. Although a total of 15 samples were collected, 8 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2012-01-10 to 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 127637, Ammonia
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
219578 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 40 samples exceeded the water quality threshold for Ammonia as N, Unionized. Although a total of 92 samples were collected, 52 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter 3, Section 3.3.2 (Objectives for all Inland Surface Waters, Enclosed Bays, and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/L (as N) in receiving waters (page 32). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2010-07-13 to 2018-11-20 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160185 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160092 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for cadmium is 0.005 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-18 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151550 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cadmium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for cadmium in 4.98 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159674 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for cadmium for irrigation supply as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159784 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for cadmium is 0.005 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151728 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cadmium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for cadmium in 4.98 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160339 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160316 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151714 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cadmium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for cadmium in 4.98 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159896 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for cadmium for irrigation supply as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160266 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for cadmium is 0.005 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159702 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for cadmium is 0.005 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160248 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160287 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for cadmium for irrigation supply as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-18 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57178 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cadmium. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for cadmium is 4.98 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160166 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159857 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160146 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151530 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Cadmium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for cadmium in 4.98 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151490 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cadmium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for cadmium in 4.98 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151707 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cadmium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for cadmium in 4.98 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159882 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151487 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cadmium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for cadmium in 4.98 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159720 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for cadmium for irrigation supply as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160265 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160389 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159803 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160058 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for cadmium is 0.005 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-18 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160157 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for cadmium for irrigation supply as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159826 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for cadmium for irrigation supply as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159853 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for cadmium is 0.005 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159648 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160035 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160039 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for cadmium is 0.005 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160169 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for cadmium is 0.005 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159825 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for cadmium for irrigation supply as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159993 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for cadmium is 0.005 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159994 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for cadmium is 0.005 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160387 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159957 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for cadmium for irrigation supply as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159651 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for cadmium for irrigation supply as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
160360 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for cadmium for irrigation supply as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2018-09-18 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159635 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151691 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Cadmium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for cadmium in 4.98 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159928 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cadmium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15425 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cadmium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cadmium is 4.98 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15426 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cadmium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cadmium is 4.98 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108240, Cadmium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57179 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cadmium. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for cadmium is 4.98 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57278 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Copper. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for copper is 149 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162503 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162521 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162522 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162630 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152373 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Copper . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for copper in 149 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152382 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Copper . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for copper in 149 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162638 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162470 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162456 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162011 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
91 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 91 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2011-01-04 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162254 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152256 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Copper . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for copper in 149 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162579 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152336 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Copper . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for copper in 149 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162457 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162004 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162859 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
91 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 91 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2011-01-04 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152135 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Copper . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for copper in 149 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162177 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162097 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 8 samples exceeded the water quality threshold for Copper. Although a total of 14 samples were collected, 6 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2012-01-10 to 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162580 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162705 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Copper. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2011-10-05 to 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162369 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162057 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
14 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 14 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162299 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2011-10-05 and 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163014 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163015 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162175 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
72 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 2 of the 72 samples exceeded the water quality threshold for Copper. Although a total of 91 samples were collected, 19 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2011-01-04 to 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162421 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
16 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 2 of the 16 samples exceeded the water quality threshold for Copper. Although a total of 23 samples were collected, 7 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2012-01-10 to 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162860 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2011-10-05 and 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162543 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162608 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162554 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162563 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162678 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162717 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162489 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The Copper criteria for the protection of human health from the consumption of water and organisms is 1.300 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
16035 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Copper. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cooper is 149 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
16048 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Copper. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cooper is 149 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57279 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Copper. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for copper is 149 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162370 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
16 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 2 of the 16 samples exceeded the water quality threshold for Copper. Although a total of 23 samples were collected, 7 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2012-01-10 to 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162629 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163023 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162499 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
14 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 14 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for copper for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162683 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152272 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Copper . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for copper in 149 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162845 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
72 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 2 of the 72 samples exceeded the water quality threshold for Copper. Although a total of 91 samples were collected, 19 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2011-01-04 to 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152356 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Copper . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for copper in 149 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162397 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Copper. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2011-10-05 to 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162548 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 8 samples exceeded the water quality threshold for Copper. Although a total of 14 samples were collected, 6 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2012-01-10 to 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162633 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152237 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Copper . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for copper in 149 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108248, Copper
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
162099 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Copper. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152265 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 4 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2011-09-07 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152218 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163233 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cyfluthrin. Although a total of 12 samples were collected, 12 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-09 to 2017-08-07 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149099 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Cyfluthrin, total. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152539 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163215 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cyfluthrin. Although a total of 5 samples were collected, 5 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-09-21 to 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163216 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cyfluthrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163372 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cyfluthrin. Although a total of 5 samples were collected, 5 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-09-21 to 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152520 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cyfluthrin, total. Although a total of 3 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152387 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cyfluthrin, total. Although a total of 3 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149117 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Cyfluthrin, total. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149118 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Cyfluthrin, total. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163328 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cyfluthrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152463 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 4 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2011-09-07 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149088 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Cyfluthrin, total. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152559 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163311 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cyfluthrin. Although a total of 12 samples were collected, 12 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-09 to 2017-08-07 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152087 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152466 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152576 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152156 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57292 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Cyfluthrin. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57281 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cyfluthrin, total. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57280 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cyfluthrin, total. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57291 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Cyfluthrin. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57304 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support. Six samples were collected however they were all non-detect and the laboratory method detection limit was above the guideline, therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of cyfluthrin does not exceed 0.00005 ug/L and if the 1-h average concentration does not exceed 0.0003 ug/L. For this assessment, the 4-day average concentration was used. Mixtures of cyfluthrin and other pyrethroids should be considered in an additive manner. (Fojut et al. 2012) |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57293 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support. Six samples were collected however they were all non-detect and the laboratory method detection limit was above the guideline, therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of cyfluthrin does not exceed 0.00005 ug/L and if the 1-h average concentration does not exceed 0.0003 ug/L. For this assessment, the 4-day average concentration was used. Mixtures of cyfluthrin and other pyrethroids should be considered in an additive manner. (Fojut et al. 2012) |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163308 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cyfluthrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152197 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152386 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152178 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cyfluthrin, total. Although a total of 4 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163327 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cyfluthrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cyfluthrin does not exceed 0.00005 ug/L (0.05 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152137 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cyfluthrin, total. Although a total of 4 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108321, Cyfluthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152125 |
|
Pollutant: |
Cyfluthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyfluthrin, total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cyfluthrin is the median lethal concentration (LC50) of 1.1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.1 ug/g is the geometric mean of LC50 values for cyfluthrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57114 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support. Six samples were collected however they were all non-detect and the laboratory method detection limit was above the guideline, therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of lambda-cyhalothrin does not exceed 0.0005 ug/L and if the 1-h average concentration does not exceed 0.001 ug/L. For this assessment, the 4-day average concentration was used. Mixtures of lambda-cyhalothrin and other pyrethroids should be considered in an additive manner. (Fojut et al. 2012) |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57113 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support. Six samples were collected however they were all non-detect and the laboratory method detection limit was above the guideline, therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of lambda-cyhalothrin does not exceed 0.0005 ug/L and if the 1-h average concentration does not exceed 0.001 ug/L. For this assessment, the 4-day average concentration was used. Mixtures of lambda-cyhalothrin and other pyrethroids should be considered in an additive manner. (Fojut et al. 2012) |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152423 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152478 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 3 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda-. Although a total of 5 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152596 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167374 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Lambda-cyhalothrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of lambda-cyhalothrin does not exceed 0.0005 ug/L (0.5 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167375 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Lambda-cyhalothrin. Although a total of 12 samples were collected, 12 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of lambda-cyhalothrin does not exceed 0.0005 ug/L (0.5 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-09 to 2017-08-07 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152527 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152477 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152521 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 3 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda-. Although a total of 5 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152459 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152562 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2011-09-07 to 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152577 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152674 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152509 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda-. Although a total of 3 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167437 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Lambda-cyhalothrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of lambda-cyhalothrin does not exceed 0.0005 ug/L (0.5 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167474 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Lambda-cyhalothrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of lambda-cyhalothrin does not exceed 0.0005 ug/L (0.5 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152567 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152497 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2011-09-07 to 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152670 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152635 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda- . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167586 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Lambda-cyhalothrin. Although a total of 12 samples were collected, 12 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of lambda-cyhalothrin does not exceed 0.0005 ug/L (0.5 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-09 to 2017-08-07 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149101 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Cyhalothrin, Total lambda-. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of lambda-cyhalothrin does not exceed 0.0005 ug/L (0.5 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167526 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Lambda-cyhalothrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of lambda-cyhalothrin does not exceed 0.0005 ug/L (0.5 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149102 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Cyhalothrin, Total lambda-. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of lambda-cyhalothrin does not exceed 0.0005 ug/L (0.5 ng/L) more than once every three years on the average (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152468 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cyhalothrin, Total lambda-. Although a total of 3 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57112 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Cyhalothrin, lambda, total. Nine sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Cyhalothrin, lambda, total does not exceed 0.0005 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57100 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Cyhalothrin, lambda, total. Nine sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Cyhalothrin, lambda, total does not exceed 0.0005 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57306 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cyhalothrin, lambda, total. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57099 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: A total of 3 samples were collected, however 1 of the non-detect sample results were compared to the evaluation guideline and the OC Normalized method detection limit result was above the guideline and therefore could not be quantified with the level of certainty required by the Listing Policy. Zero of the remaining 2 quantifiable sample results were exceeding the evaluation guideline. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57098 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: A total of 3 samples were collected, however 1 of the non-detect sample results were compared to the evaluation guideline and the OC Normalized method detection limit result was above the guideline and therefore could not be quantified with the level of certainty required by the Listing Policy. Zero of the remaining 2 quantifiable sample results were exceeding the evaluation guideline. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108323, Cyhalothrin, Lambda
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57305 |
|
Pollutant: |
Cyhalothrin, Lambda |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cyhalothrin, lambda, total. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for lambda-cyhalothrin is the median lethal concentration (LC50) of 0.44 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.44 ug/g is the geometric mean of LC50 values for lambda-cyhalothrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152891 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152930 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 5 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149235 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Cypermethrin, Total. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2011). |
Guideline Reference: |
Water Quality Criteria Report for Cypermethrin |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149240 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Cypermethrin, Total. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2011). |
Guideline Reference: |
Water Quality Criteria Report for Cypermethrin |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163560 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cypermethrin. Although a total of 12 samples were collected, 12 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-09 to 2017-08-07 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163199 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 1 samples exceeded the water quality threshold for Cypermethrin. Although a total of 2 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2016-09-21 to 2017-03-01 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163756 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cypermethrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163516 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cypermethrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152950 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152934 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163241 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cypermethrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153011 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 3 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-04-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152874 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152868 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152646 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163239 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cypermethrin. Although a total of 12 samples were collected, 12 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-09 to 2017-08-07 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163559 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cypermethrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152854 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 5 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152917 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152626 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152918 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153009 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152775 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152665 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149236 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Cypermethrin, Total. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2011). |
Guideline Reference: |
Water Quality Criteria Report for Cypermethrin |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153010 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 3 samples exceeded the evaluation guideline for Cypermethrin, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-04-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163456 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 1 samples exceeded the water quality threshold for Cypermethrin. Although a total of 2 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2016-09-21 to 2017-03-01 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57142 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for CYPERMETHRIN. Nine sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Cypermethrin; Cypermethrin, total does not exceed 0.0002 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57141 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for CYPERMETHRIN. Nine sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Cypermethrin; Cypermethrin, total does not exceed 0.0002 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57140 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: A total of 3 samples were collected, however 1 of the non-detect sample results were compared to the evaluation guideline and the OC Normalized method detection limit result was above the guideline and therefore could not be quantified with the level of certainty required by the Listing Policy. Zero of the remaining 2 quantifiable sample results were exceeding the evaluation guideline. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57127 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cypermethrin, total. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57128 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: A total of 3 samples were collected, however 1 of the non-detect sample results were compared to the evaluation guideline and the OC Normalized method detection limit result was above the guideline and therefore could not be quantified with the level of certainty required by the Listing Policy. Zero of the remaining 2 quantifiable sample results were exceeding the evaluation guideline. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57126 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cypermethrin, total. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for cypermethrin is the median lethal concentration (LC50) of 0.3 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.3 ug/g is the geometric mean of LC50 values for cypermethrin from Maund et al. (2002). |
Guideline Reference: |
Partitioning, bioavailability, and toxicity of the pyrethroid insecticide cypermethrin in sediments. Environmental Toxicology and Chemistry 21:9-15 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57154 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support. Six samples were collected however they were all non-detect and the laboratory method detection limit was above the guideline, therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of cypermethrin does not exceed 0.0002 ug/L and if the 1-h average concentration does not exceed 0.001 ug/L. For this assessment, the 4-day average concentration was used. Mixtures of cypermethrin and other pyrethroids should be considered in an additive manner. (Fojut et al. 2012) |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57153 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support. Six samples were collected however they were all non-detect and the laboratory method detection limit was above the guideline, therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of cypermethrin does not exceed 0.0002 ug/L and if the 1-h average concentration does not exceed 0.001 ug/L. For this assessment, the 4-day average concentration was used. Mixtures of cypermethrin and other pyrethroids should be considered in an additive manner. (Fojut et al. 2012) |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108304, Cypermethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149096 |
|
Pollutant: |
Cypermethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Cypermethrin, Total. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of cypermethrin does not exceed 0.0002 ug/L (0.2 ng/L) more than once every three years on the average (Fojut et al. ,2011). |
Guideline Reference: |
Water Quality Criteria Report for Cypermethrin |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153602 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153498 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225125 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Deltamethrin. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Deltamethrin is the USEPA Aquatic Life Benchmark of 0.0041 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2008-01-07 and 2009-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP not required |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57282 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Deltamethrin. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57284 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Deltamethrin. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153356 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153385 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153540 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163616 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality threshold for Deltamethrin. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Deltamethrin is the USEPA Aquatic Life Benchmark of 0.0041 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2016-09-21 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153500 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153370 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153621 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163700 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Deltamethrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Deltamethrin is the USEPA Aquatic Life Benchmark of 0.0041 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163547 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Deltamethrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Deltamethrin is the USEPA Aquatic Life Benchmark of 0.0041 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153390 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225129 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Deltamethrin. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Deltamethrin is the USEPA Aquatic Life Benchmark of 0.0041 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2008-01-07 and 2009-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP not required |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153601 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153343 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153637 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153525 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153384 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163679 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Deltamethrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Deltamethrin is the USEPA Aquatic Life Benchmark of 0.0041 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153405 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153464 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Deltamethrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163806 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality threshold for Deltamethrin. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Deltamethrin is the USEPA Aquatic Life Benchmark of 0.0041 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2016-09-21 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
163762 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Deltamethrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Deltamethrin is the USEPA Aquatic Life Benchmark of 0.0041 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57269 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Deltamethrin. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108322, Deltamethrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57283 |
|
Pollutant: |
Deltamethrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Deltamethrin. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for deltamethrin is the median lethal concentration (LC50) of 0.79 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.79 ug/g is the geometric mean of LC50 values for deltamethrin from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164519 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2011-04-26 to 2011-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
224877 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2004-09-13 to 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
224894 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2006-08-24 to 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225093 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 4 samples were collected, 4 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2006-08-24 to 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225133 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2004-09-13 to 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225131 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2009-08-25 to 2009-08-25 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
224913 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2004-09-13 to 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164301 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2010-07-20 to 2010-07-20 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149216 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dichlorvos. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149226 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dichlorvos. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164253 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Dichlorvos. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA IRIS one-in-a-million cancer risk estimate from oral exposure for dichlorvos is 0.1 ug/L. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149222 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dichlorvos. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA IRIS one-in-a-million cancer risk estimate from oral exposure for dichlorvos is 0.1 ug/L. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164295 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Dichlorvos. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA IRIS one-in-a-million cancer risk estimate from oral exposure for dichlorvos is 0.1 ug/L. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164238 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2017-09-27 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164297 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2017-09-27 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164377 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2017-09-27 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164441 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dichlorvos. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA IRIS one-in-a-million cancer risk estimate from oral exposure for dichlorvos is 0.1 ug/L. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225152 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2004-09-13 to 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164400 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dichlorvos. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA IRIS one-in-a-million cancer risk estimate from oral exposure for dichlorvos is 0.1 ug/L. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13) |
Temporal Representation: |
The samples were collected between the dates of 2011-04-26 and 2011-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164477 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2017-09-27 to 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164313 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2017-09-27 to 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164460 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2010-07-20 to 2010-07-20 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164444 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2017-09-27 to 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164357 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dichlorvos. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA IRIS one-in-a-million cancer risk estimate from oral exposure for dichlorvos is 0.1 ug/L. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2010-07-20 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164499 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2011-04-26 to 2011-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57156 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for Dichlorvos. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA IRIS one-in-a-million cancer risk estimate from oral exposure for dichlorvos is 0.1 ug/L. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79758 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Dichlorvos. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA IRIS one-in-a-million cancer risk estimate from oral exposure for dichlorvos is 0.1 ug/L. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57145 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Dichlorvos. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA IRIS one-in-a-million cancer risk estimate from oral exposure for dichlorvos is 0.1 ug/L. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SAC, Salinas River (Lower) - 309SSP] |
Temporal Representation: |
Data was collected over the time period 8/24/2006-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225155 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 4 samples were collected, 4 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2006-08-24 to 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225091 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2009-08-25 to 2009-08-25 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108250, Dichlorvos
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225092 |
|
Pollutant: |
Dichlorvos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dichlorvos. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dichlorvos is the USEPA Aquatic Life Benchmark of 0.0058 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2006-08-24 to 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164736 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164702 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164678 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164535 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13) |
Temporal Representation: |
The samples were collected between the dates of 2011-04-26 and 2017-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164713 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164807 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164569 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164578 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164636 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164560 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149167 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dimethoate. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164632 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164749 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-06-05 and 2012-06-05 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149169 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dimethoate. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164853 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13) |
Temporal Representation: |
The samples were collected between the dates of 2011-04-26 and 2017-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
164755 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-06-05 and 2012-06-05 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57159 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Dimethoate. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Department of Health Services notification level for dimethoate is 1 µg/L. |
Guideline Reference: |
Drinking Water Notification and Response Levels: An Overview |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57171 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Department of Health Services notification level for dimethoate is 1 µg/L. |
Guideline Reference: |
Drinking Water Notification Levels and Response Levels |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SAC, Salinas River (Lower) - 309SSP] |
Temporal Representation: |
Data was collected over the time period 8/24/2006-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57172 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Department of Health Services notification level for dimethoate is 1 µg/L. |
Guideline Reference: |
Drinking Water Notification Levels and Response Levels |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
224958 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2006-08-24 and 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
224916 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225118 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225016 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2006-08-24 and 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
224879 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2009-08-25 and 2009-08-25 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225075 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2009-08-25 and 2009-08-25 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225096 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2006-08-24 and 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
224918 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2006-08-24 and 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
224996 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108307, Dimethoate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
224844 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154238 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153666 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154014 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154143 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154056 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154054 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154108 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149312 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Esfenvalerate. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Esfenvalerate is the USEPA Aquatic Life Benchmark of 0.017 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149313 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Esfenvalerate. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Esfenvalerate is the USEPA Aquatic Life Benchmark of 0.017 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154111 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149315 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Esfenvalerate/Fenvalerate, Total. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Esfenvalerate/Fenvalerate is the USEPA Aquatic Life Benchmark of 0.017 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154194 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153977 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154239 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153905 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154127 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 5 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2011-09-07 to 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154016 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149314 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Esfenvalerate/Fenvalerate, Total. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Esfenvalerate/Fenvalerate is the USEPA Aquatic Life Benchmark of 0.017 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57246 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceed the criterion for ESFENVALERATE. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.13 ug/L, as determined in a 96 hour toxicity test using the fathead minnow, Pimephales promelas (USEPA Office of Pesticide Programs Ecotoxicity database). |
Guideline Reference: |
OPP Pesticide Ecotoxicity Database. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57245 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceed the criterion for ESFENVALERATE. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.13 ug/L, as determined in a 96 hour toxicity test using the fathead minnow, Pimephales promelas (USEPA Office of Pesticide Programs Ecotoxicity database). |
Guideline Reference: |
OPP Pesticide Ecotoxicity Database. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57273 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Esfenvalerate. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57260 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Esfenvalerate/Fenvalerate, total. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57272 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Esfenvalerate. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57259 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Esfenvalerate/Fenvalerate, total. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57258 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for Esfenvalerate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.13 ug/L, as determined in a 96 hour toxicity test using the fathead minnow, Pimephales promelas. (USEPA Office of Pesticide Programs Ecotoxicity database) |
Guideline Reference: |
OPP Pesticide Ecotoxicity Database. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57247 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for Esfenvalerate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.13 ug/L, as determined in a 96 hour toxicity test using the fathead minnow, Pimephales promelas. (USEPA Office of Pesticide Programs Ecotoxicity database) |
Guideline Reference: |
OPP Pesticide Ecotoxicity Database. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154087 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 5 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2011-09-07 to 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108326, Esfenvalerate/Fenvalerate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154220 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Esfenvalerate/Fenvalerate, Total . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for esfenvalerate/fenvalerate is the median lethal concentration (LC50) of 1.5 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1.5 ug/g is the geometric mean of LC50 values for esfenvalerate/fenvalerate from Amweg et al. (2005). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
166264 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Fenpropathrin. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
166045 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality threshold for Fenpropathrin. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2016-09-21 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
166441 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Fenpropathrin. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13) |
Temporal Representation: |
The samples were collected between the dates of 2016-04-12 and 2017-08-07 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154524 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149307 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Fenpropathrin. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154247 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 5 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2011-09-07 to 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
165995 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality threshold for Fenpropathrin. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2016-09-21 and 2018-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154209 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154485 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
166266 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Fenpropathrin. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
166440 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Fenpropathrin. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13) |
Temporal Representation: |
The samples were collected between the dates of 2016-04-12 and 2017-08-07 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153987 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154303 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 3 samples exceeded the evaluation guideline for Fenpropathrin. Although a total of 4 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-04-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154002 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149309 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Fenpropathrin. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154204 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154151 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 3 samples exceeded the evaluation guideline for Fenpropathrin. Although a total of 4 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-04-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154525 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154045 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154135 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225441 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Fenpropathrin. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2008-01-07 and 2009-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP not required |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225394 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Fenpropathrin. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2008-01-07 and 2009-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP not required |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
166093 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Fenpropathrin. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57120 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Fenpropathrin. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57121 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Fenpropathrin. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57133 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Fenpropathrin. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154116 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 5 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2011-09-07 to 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154249 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154507 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149297 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Fenpropathrin. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
166480 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Fenpropathrin. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154079 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Fenpropathrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149301 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Fenpropathrin. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.06 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108325, Fenpropathrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57132 |
|
Pollutant: |
Fenpropathrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Fenpropathrin. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for fenpropathrin is the median lethal concentration (LC50) of 1 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 1 ug/g is the geometric mean of LC50 values for fenpropathrin from Ding et al. ( 2011). |
Guideline Reference: |
Toxicity of Sediment-Associated Pesticides to Chironomus dilutus and Hyalella azteca. Arch. Environ. Contam. Toxicol. 61:83¿92. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168579 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Malathion. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2012-02-28 to 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168556 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Malathion. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149335 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Malathion. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149347 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Malathion. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 ug/L. |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57235 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for MALATHION. Nine sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Malathion does not exceed 0.028 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57218 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceed the criterion for MALATHION. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 µg/L. |
Guideline Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57234 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for MALATHION. Nine sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Malathion does not exceed 0.028 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57233 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Malathion. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Malathion does not exceed 0.028 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57248 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Malathion. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Malathion does not exceed 0.028 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SAC, Salinas River (Lower) - 309SSP] |
Temporal Representation: |
Data was collected over the time period 8/24/2006-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57250 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support. Six samples were collected however they were all non-detect and the laboratory method detection limit was above the guideline, therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Malathion does not exceed 0.028 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57208 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Malathion. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 µg/L. |
Guideline Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57220 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for Malathion. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water life-time health advisory for malathion is 500 µg/L. |
Guideline Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57219 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Malathion. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 µg/L. |
Guideline Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SAC, Salinas River (Lower) - 309SSP] |
Temporal Representation: |
Data was collected over the time period 8/24/2006-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57221 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Malathion. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Malathion does not exceed 0.028 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57236 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Malathion. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Malathion does not exceed 0.028 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SAC, Salinas River (Lower) - 309SSP] |
Temporal Representation: |
Data was collected over the time period 8/24/2006-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57249 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support. Six samples were collected however they were all non-detect and the laboratory method detection limit was above the guideline, therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Malathion does not exceed 0.028 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168685 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 ug/L. |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168705 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 ug/L. |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168494 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Malathion. Although a total of 4 samples were collected, 4 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2010-07-20 to 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149366 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Malathion. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169029 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 ug/L. |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-06-05 and 2012-06-05 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149370 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Malathion. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168428 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168412 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 2 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168514 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 ug/L. |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168479 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Malathion. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149343 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Malathion. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168381 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 ug/L. |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13) |
Temporal Representation: |
The samples were collected between the dates of 2011-04-26 and 2017-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168587 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 2 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168492 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 ug/L. |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168419 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Malathion. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2012-02-28 to 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168398 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168601 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 ug/L. |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168691 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 ug/L. |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168613 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
20 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 20 samples exceeded the water quality threshold for Malathion. Although a total of 23 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2011-04-26 to 2017-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168678 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
20 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 20 samples exceeded the water quality threshold for Malathion. Although a total of 23 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2011-04-26 to 2017-09-11 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168620 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Malathion. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168522 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Malathion. Although a total of 4 samples were collected, 4 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2010-07-20 to 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168430 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149354 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Malathion. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 ug/L. |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168642 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for malathion is 500 ug/L. |
Guideline Reference: |
2018 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168454 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Malathion. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108264, Malathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168396 |
|
Pollutant: |
Malathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Malathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of malathion does not exceed 0.028 ug/L more than once every three years on the average (Faria et al., 2010). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57261 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Mercury. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for mercury is 1.06 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169215 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 7 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 0.051 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2015-11-10 and 2017-11-30 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154899 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Mercury . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for mercury in 1.06 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169431 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents known to be deleterious to fish or wildlife (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The Criterion Continuous Concentration for freshwater aquatic life is 0.77 ug/L (National Recommended Water Quality Criteria, EPA 2016) |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Current as of 08/03/2016. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169205 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents known to be deleterious to fish or wildlife (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The Criterion Continuous Concentration for freshwater aquatic life is 0.77 ug/L (National Recommended Water Quality Criteria, EPA 2016) |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Current as of 08/03/2016. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148529 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends Project (SPoT) data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Mercury. |
Data Reference: |
SPoT sediment data: 6/5/2018--6/13/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for mercury in 1.06 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV |
Temporal Representation: |
Data for this waterbody were collected on 06/05/2018. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPP and the SWAMP-SPoT QAPP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169369 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 0.051 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148530 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends Project (SPoT) data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Mercury. |
Data Reference: |
SPoT sediment data: 6/5/2018--6/13/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for mercury in 1.06 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR |
Temporal Representation: |
Data for this waterbody were collected on 06/13/2018. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPP and the SWAMP-SPoT QAPP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169532 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 7 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents known to be deleterious to fish or wildlife (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The Criterion Continuous Concentration for freshwater aquatic life is 0.77 ug/L (National Recommended Water Quality Criteria, EPA 2016) |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Current as of 08/03/2016. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2015-11-10 and 2017-11-30 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169291 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 7 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The mercury criteria for the protection of human health from the consumption of water and organisms for mercury is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2015-11-10 and 2017-11-30 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169242 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for mercury for livestock watering as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169535 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The mercury criteria for the protection of human health from the consumption of water and organisms for mercury is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169133 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for mercury for livestock watering as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169541 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 7 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for mercury for livestock watering as 0.01 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2015-11-10 and 2017-11-30 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154979 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Mercury . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for mercury in 1.06 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154696 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Mercury . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for mercury in 1.06 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148531 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends Project (SPoT) data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Mercury. |
Data Reference: |
SPoT sediment data: 6/5/2018--6/13/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for mercury in 1.06 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR |
Temporal Representation: |
Data for this waterbody were collected on 06/13/2018. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPP and the SWAMP-SPoT QAPP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169217 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 0.051 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169501 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents known to be deleterious to fish or wildlife (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The Criterion Continuous Concentration for freshwater aquatic life is 0.77 ug/L (National Recommended Water Quality Criteria, EPA 2016) |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Current as of 08/03/2016. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154814 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Mercury . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for mercury in 1.06 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155001 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Mercury . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for mercury in 1.06 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169474 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The mercury criteria for the protection of human health from the consumption of water and organisms for mercury is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148528 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends Project (SPoT) data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Mercury. |
Data Reference: |
SPoT sediment data: 6/5/2018--6/13/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for mercury in 1.06 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV |
Temporal Representation: |
Data for this waterbody were collected on 06/05/2018. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPP and the SWAMP-SPoT QAPP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154817 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Mercury . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for mercury in 1.06 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169234 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents known to be deleterious to fish or wildlife (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The Criterion Continuous Concentration for freshwater aquatic life is 0.77 ug/L (National Recommended Water Quality Criteria, EPA 2016) |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Current as of 08/03/2016. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169168 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 7 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents known to be deleterious to fish or wildlife (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The Criterion Continuous Concentration for freshwater aquatic life is 0.77 ug/L (National Recommended Water Quality Criteria, EPA 2016) |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Current as of 08/03/2016. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2015-11-10 and 2017-11-30 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
17203 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Mercury. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for mercury is 1.06 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
17204 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Mercury. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for mercury is 1.06 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 130755, Mercury
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57262 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Mercury. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for mercury is 1.06 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169711 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57263 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceed the criterion for METHIDATHION. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Based on USEPA IRIS reference dose (RfD) as a drinking water level, the drinking water health advisory level for methidathion is 0.7 µg/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, and 20% relative source contribution from drinking water. An additional uncertainty factor of 10 is used for Class C carcinogens. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169813 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
17 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 17 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13) |
Temporal Representation: |
The samples were collected between the dates of 2011-04-26 and 2016-09-13 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169757 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Based on USEPA IRIS reference dose (RfD) as a drinking water level, the drinking water health advisory level for methidathion is 0.7 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, and 20% relative source contribution from drinking water. An additional uncertainty factor of 10 is used for Class C carcinogens. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169646 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Based on USEPA IRIS reference dose (RfD) as a drinking water level, the drinking water health advisory level for methidathion is 0.7 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, and 20% relative source contribution from drinking water. An additional uncertainty factor of 10 is used for Class C carcinogens. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169604 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225236 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2008-01-07 and 2009-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP not required |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169685 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-06-05 and 2012-06-05 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169609 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Based on USEPA IRIS reference dose (RfD) as a drinking water level, the drinking water health advisory level for methidathion is 0.7 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, and 20% relative source contribution from drinking water. An additional uncertainty factor of 10 is used for Class C carcinogens. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-06-05 and 2012-06-05 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225254 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2008-01-07 and 2009-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP not required |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225319 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225316 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225276 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225214 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2009-08-25 and 2009-08-25 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225255 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225233 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2009-08-25 and 2009-08-25 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57264 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for Methidathion. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Based on USEPA IRIS reference dose (RfD) as a drinking water level, the drinking water health advisory level for methidathion is 0.7 µg/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, and 20% relative source contribution from drinking water. An additional uncertainty factor of 10 is used for Class C carcinogens. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169737 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
17 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 17 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13) |
Temporal Representation: |
The samples were collected between the dates of 2011-04-26 and 2016-09-13 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169643 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
17 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 17 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Based on USEPA IRIS reference dose (RfD) as a drinking water level, the drinking water health advisory level for methidathion is 0.7 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, and 20% relative source contribution from drinking water. An additional uncertainty factor of 10 is used for Class C carcinogens. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13) |
Temporal Representation: |
The samples were collected between the dates of 2011-04-26 and 2016-09-13 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149378 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Methidathion. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149386 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Methidathion. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Based on USEPA IRIS reference dose (RfD) as a drinking water level, the drinking water health advisory level for methidathion is 0.7 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, and 20% relative source contribution from drinking water.¿ An additional uncertainty factor of 10 is used for Class C carcinogens.¿ |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169859 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-06-05 and 2012-06-05 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170142 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169561 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169958 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169625 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Based on USEPA IRIS reference dose (RfD) as a drinking water level, the drinking water health advisory level for methidathion is 0.7 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, and 20% relative source contribution from drinking water. An additional uncertainty factor of 10 is used for Class C carcinogens. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169592 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169714 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149391 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Methidathion. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169710 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Based on USEPA IRIS reference dose (RfD) as a drinking water level, the drinking water health advisory level for methidathion is 0.7 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, and 20% relative source contribution from drinking water. An additional uncertainty factor of 10 is used for Class C carcinogens. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169655 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169745 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169796 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Based on USEPA IRIS reference dose (RfD) as a drinking water level, the drinking water health advisory level for methidathion is 0.7 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, and 20% relative source contribution from drinking water. An additional uncertainty factor of 10 is used for Class C carcinogens. |
Guideline Reference: |
IRIS Database Calculations (summary) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108305, Methidathion
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
169606 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
18249 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
15 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 15 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15301 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
168 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 5 of 168 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-10/10/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14743 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
43 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 3 of 43 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12870 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
52 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 52 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12090 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
17 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 17 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 7/6/1999-8/31/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12850 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
62 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 62 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 2/1/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175461 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 38 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175150 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 44 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174913 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 24 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174918 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174919 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
47 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 47 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175541 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-08-08 and 2012-08-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51451 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15286 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
168 |
Number of Exceedances: |
16 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 16 of 168 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, Cold Water Habitat Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-10/10/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52873 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 8 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/10/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57420 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 5 of 40 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12796 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
62 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 62 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, Cold Water Habitat Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 2/1/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14742 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
43 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 6 of 43 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, Cold Water Habitat Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
18248 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
15 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 15 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, Cold Water Habitat Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51188 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
47909 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Region 3 - Central Coast Region staff assessed R3 public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 7 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009 3:40:00 PM. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
A QAPP was not specifically written for this project. However, staff conducting data collection and laboratory analysis are also SWAMP contractors. All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in |
QAPP Information Reference(s): |
2002. Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. California Department of Fish and Game, Monterey, CA |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12782 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
17 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 17 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, Cold Water Habitat Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 7/6/1999-8/31/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12869 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
52 |
Number of Exceedances: |
13 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 13 of 52 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, Cold Water Habitat Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51466 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 7 of 39 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57418 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 40 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52848 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 8 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/10/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174657 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175179 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
34 |
Number of Exceedances: |
13 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 13 of 34 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2014-09-04 and 2017-04-12 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174893 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174630 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 24 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174916 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174669 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2015-06-09 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175522 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
104 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 4 of 104 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175462 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
47 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 4 of 47 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175313 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
104 |
Number of Exceedances: |
9 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 9 of 104 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174891 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-19 and 2012-07-22 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175653 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175203 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174654 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
18 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 18 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174927 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-19 and 2012-07-22 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174618 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 44 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174938 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 38 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174565 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
18 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 18 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175555 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309PS0370) |
Temporal Representation: |
The samples were collected between the dates of 2017-06-13 and 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175707 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175309 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175312 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309PS0370) |
Temporal Representation: |
The samples were collected between the dates of 2017-06-13 and 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175210 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-08-08 and 2012-08-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174868 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2015-06-09 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
47825 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
7 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Region 3 - Central Coast Region staff assessed R3 public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 7 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009 3:40:00 PM. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
A QAPP was not specifically written for this project. However, staff conducting data collection and laboratory analysis are also SWAMP contractors. All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in |
QAPP Information Reference(s): |
2002. Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. California Department of Fish and Game, Monterey, CA |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51450 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 39 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174870 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
175114 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
34 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 34 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2014-09-04 and 2017-04-12 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108277, Oxygen, Dissolved
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
174986 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180368 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The National Academy of Sciences health advisory for phorate is 0.7 ug/L. This was calculated using the no-adverse-effect dosage of 0.01 mg/kg, assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and divided by 100 for a factor of safety. |
Guideline Reference: |
National Academy of Sciences - Volume I Drinking Water and Health |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180271 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180282 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The National Academy of Sciences health advisory for phorate is 0.7 ug/L. This was calculated using the no-adverse-effect dosage of 0.01 mg/kg, assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and divided by 100 for a factor of safety. |
Guideline Reference: |
National Academy of Sciences - Volume I Drinking Water and Health |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180288 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180174 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The National Academy of Sciences health advisory for phorate is 0.7 ug/L. This was calculated using the no-adverse-effect dosage of 0.01 mg/kg, assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and divided by 100 for a factor of safety. |
Guideline Reference: |
National Academy of Sciences - Volume I Drinking Water and Health |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149425 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Phorate. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180183 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180353 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180229 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180388 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180391 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The National Academy of Sciences health advisory for phorate is 0.7 ug/L. This was calculated using the no-adverse-effect dosage of 0.01 mg/kg, assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and divided by 100 for a factor of safety. |
Guideline Reference: |
National Academy of Sciences - Volume I Drinking Water and Health |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149414 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Phorate. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180168 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180151 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57551 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Phorate. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The National Academy of Sciences health advisory for phorate is 0.7 µg/L. This was calculated using the no-adverse-effect dosage of 0.01 mg/kg, assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and divided by 100 for a factor of safety. |
Guideline Reference: |
National Academy of Sciences - Volume I Drinking Water and Health |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 2/15/2007-3/22/2007. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57552 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Phorate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The national health advisory level for phorate is 0.7 µg/L. This was calculated using the no-adverse-effect dosage of 0.01 mg/kg, assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and divided by 100 for a factor of safety. |
Guideline Reference: |
National Academy of Sciences - Volume I Drinking Water and Health |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SAC, Salinas River (Lower) - 309SSP] |
Temporal Representation: |
Data was collected over the time period 8/24/2006-9/28/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57553 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for Phorate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The national health advisory level for phorate is 0.7 µg/L. This was calculated using the no-adverse-effect dosage of 0.01 mg/kg, assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and divided by 100 for a factor of safety. |
Guideline Reference: |
National Academy of Sciences - Volume I Drinking Water and Health |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225244 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2009-08-25 and 2009-08-25 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180192 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The National Academy of Sciences health advisory for phorate is 0.7 ug/L. This was calculated using the no-adverse-effect dosage of 0.01 mg/kg, assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and divided by 100 for a factor of safety. |
Guideline Reference: |
National Academy of Sciences - Volume I Drinking Water and Health |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-02-28 and 2012-09-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180416 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225178 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180305 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-20 and 2013-06-18 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225160 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225414 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2006-08-24 and 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225458 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225182 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2006-08-24 and 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225484 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2004-09-13 and 2005-05-03 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225159 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2006-08-24 and 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225286 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2009-08-25 and 2009-08-25 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
225243 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for a invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2006-08-24 and 2007-03-22 |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108313, Phorate
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149420 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Phorate. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The National Academy of Sciences health advisory for phorate is 0.7 ug/L. This was calculated using the no-adverse-effect dosage of 0.01 mg/kg, assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and divided by 100 for a factor of safety. |
Guideline Reference: |
National Academy of Sciences - Volume I Drinking Water and Health |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156933 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
90 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 90 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2011-01-04 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
17683 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Zinc. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for zinc is 459 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
17684 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Zinc. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for zinc is 459 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57470 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Zinc. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for zinc is 459 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57469 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Zinc. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for zinc is 459 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156771 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
14 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 14 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182835 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
14 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 14 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156604 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156672 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2011-10-05 and 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182774 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
14 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 14 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182694 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155816 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Zinc . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for zinc in 459 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182849 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156015 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Zinc . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for zinc in 459 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155815 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Zinc . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for zinc in 459 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156733 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156862 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156778 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182866 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156833 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156747 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156653 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182862 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182863 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182864 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
90 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 90 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2011-01-04 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182817 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2011-10-05 and 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182762 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
23 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 23 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155967 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Zinc . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for zinc in 459 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156815 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156951 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182739 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155846 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Zinc . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for zinc in 459 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155905 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Zinc . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for zinc in 459 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156679 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155891 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Zinc . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for zinc in 459 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182701 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155940 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Zinc . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for zinc in 459 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156937 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156863 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2011-10-05 and 2012-03-24 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156643 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
182857 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
90 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 90 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for zinc for irrigation supply as 2.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2011-01-04 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108295, Zinc
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
156915 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Zinc. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
157803 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for arsenic for irrigation supply as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158184 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for Arsenic is 10 ug/L. |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158384 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for Arsenic is 10 ug/L. |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151332 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Arsenic . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000a). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151374 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Arsenic . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000a). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158459 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for Arsenic is 10 ug/L. |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
157688 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for Arsenic is 10 ug/L. |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158205 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for arsenic for irrigation supply as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158078 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for arsenic for irrigation supply as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151373 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Arsenic . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000a). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158162 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for Arsenic is 10 ug/L. |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158417 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for arsenic for irrigation supply as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151394 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Arsenic . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000a). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158100 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for arsenic for irrigation supply as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151189 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Arsenic . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000a). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158502 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for Arsenic is 10 ug/L. |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158320 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for arsenic for irrigation supply as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151210 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Arsenic . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000a). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158501 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 2 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for Arsenic is 10 ug/L. |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158148 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for Arsenic is 10 ug/L. |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158248 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for arsenic for irrigation supply as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151357 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Arsenic . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000a). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151131 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Arsenic . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000a). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57034 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Arsenic. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15641 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Arsenic. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57033 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Arsenic. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158400 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Arsenic. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for arsenic for irrigation supply as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108235, Arsenic
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15640 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Arsenic. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57265 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Chromium. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for chromium is 111 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
16071 |
|
Pollutant: |
Chromium (total) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Chromium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for chromium is 111 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
16084 |
|
Pollutant: |
Chromium (total) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Chromium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for chromium is 111 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24486 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24485 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24564 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-5/26/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24565 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-5/26/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149068 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00L ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148676 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
10 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
4 of the 10 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2009-06-16 and 2018-06-05. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57440 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity and did not exhibit significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Coastal Confluences 2008 2009 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The sample was collected at stations 309DAV - Salinas River at Davis Road. |
Temporal Representation: |
The sample was collected in May 2009. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79704 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Five samples were collected to evaluate sediment toxicity. None of the 5 samples exhibited significant toxicity.
The toxicity tests included growth and survival of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location. Samples collected in 2005 and 2006, in the data file associated with this LOE, are not included in this LOE because they were included in the previous assessment cycle. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant effect is defined here using a two-tier approach consistent with the method used by the SWAMP program. The effect must be significant when compared to the control sample based on statistical test alpha level of 0.05 (Probability field in data set) AND the mean must be more than 20 percent different from the control (PercentControl field in data set). |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at two lower Salinas River stations (309SAC and 309SSP). |
Temporal Representation: |
The samples were collected in annually in April 2007-2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. QAPP for the Cooperative Monitoring program for Agriculture in Region 3. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148678 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 1 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Chironomus dilutus, for Survival, Chironomus dilutus, for Growth (wt/surv indiv), Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SBR ) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57439 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Three samples were collected to evaluate sediment toxicity. One of the three samples exhibited significant toxicity. The toxicity tests included survival and growth of Hyalella azteca. Statistically significant effects on Hyalella azteca were observed in the sample collected on 10/28/2009. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity was defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. The t-test is used to determine if there is a statistically significant decrease in organism response in the sample as compared to the control. In the SWAMP data format, a Significance Effect Code of SL denotes toxic test results. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
Guideline Reference: |
Short-term Methods for Estimating the Chronic Toxicity of Effluents and Receiving Waters to Freshwater Organisms. Fourth Edition. Office of Water, U.S. Environmental Protection Agency. Washington, D.C. EPA-821-R-02-013 |
|
Spatial Representation: |
The samples were collected at Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) station 309DAV-Salinas River at Davis Road. |
Temporal Representation: |
The samples were collected in July and October 2008 and October 2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79701 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity. None of the samples exhibited significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at stations 309DAVxxx. |
Temporal Representation: |
The sample was collected in June 2008. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148888 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Salinas Rotation for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-23 and 2012-07-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148889 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Salinas Rotation for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-23 and 2012-07-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148718 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 2 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2013-05-28 and 2017-04-26. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148792 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAG ) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149063 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Confluences for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-23 and 2012-07-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57451 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity. None of the samples exhibited significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at stations 309DAVxxx. |
Temporal Representation: |
The sample was collected in June 2008. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161937 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Chromium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for chromium for irrigation supply is 0.10 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151814 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Chromium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for chromium in 111 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161872 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Chromium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for total chromium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161766 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Chromium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for total chromium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161811 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Chromium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for chromium for irrigation supply is 0.10 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161787 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chromium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for chromium for irrigation supply is 0.10 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161965 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chromium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for total chromium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79702 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity and did not exhibit significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Coastal Confluences 2008 2009 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The sample was collected at stations 309DAV - Salinas River at Davis Road. |
Temporal Representation: |
The sample was collected in May 2009. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79703 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Three samples were collected to evaluate sediment toxicity. One of the three samples exhibited significant toxicity. The toxicity tests included survival and growth of Hyalella azteca. Statistically significant effects on Hyalella azteca were observed in the sample collected on 10/28/2009. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity was defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. The t-test is used to determine if there is a statistically significant decrease in organism response in the sample as compared to the control. In the SWAMP data format, a Significance Effect Code of SL denotes toxic test results. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) station 309DAV-Salinas River at Davis Road. |
Temporal Representation: |
The samples were collected in July and October 2008 and October 2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148553 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAG ) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152076 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 1 samples exceeded the evaluation guideline for Chromium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for chromium in 111 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161875 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chromium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for chromium for irrigation supply is 0.10 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152063 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 1 samples exceeded the evaluation guideline for Chromium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for chromium in 111 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151900 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Chromium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for chromium in 111 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151939 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Chromium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for chromium in 111 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161702 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chromium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for total chromium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161763 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chromium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for total chromium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151818 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Chromium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for chromium in 111 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152002 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 6 samples exceeded the evaluation guideline for Chromium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for chromium in 111 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
161873 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chromium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for chromium for irrigation supply is 0.10 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151958 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 6 samples exceeded the evaluation guideline for Chromium . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for chromium in 111 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108324, Chromium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57266 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Chromium. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for chromium is 111 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57169 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for DDD. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDD is 28.0 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148676 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
10 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
4 of the 10 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2009-06-16 and 2018-06-05. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57155 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDD(p,p). Nine sample result(s) were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The DDD(p,p) criteria for the protection of human health from the consumption of water and organisms is 0.00083 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
29999 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Nine samples were analyzed by solid phase extraction after an approximately 30 day exposure, in-situ, to known volumes of water. Nine separate sample events were conducted by CCLEAN staff. One of the 9 samples exceed the Human Health Criteria. |
Data Reference: |
Final Data CCLEAN Mussel Tissue and Solid Phase Extraction data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Human Health Criteria, for the consumption of water, set for 4,4'-DDD is 0.00083 ug/L (USEPA. Federal Register, 40 CFR Part 131 (Vol.65, No. 97. May 18, 2000)). |
Objective/Criterion Reference: |
Water Quality Standards; Establishment of Numeric Criteria for Priority Toxic Pollutants for the State of California; Rule. 40 CFR Part 131. U.S. Environmental Protection Agency, Region IX, Water Division, San Francisco, CA |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Single sample location, Salinas River 1.6 miles below Blanco Road on north shore (Lat, N 36.6950, Long, W 121.7502) |
Temporal Representation: |
Nine separate (approximate 30 day) sample events. The first was initiated on October 5th, 2002 and the ninth event was initiated on October 10th, 2006. |
Environmental Conditions: |
Water from the sample source (i.e., river) is pumped sequentially through a 0.45 micron glass-fiber particle filter, then through a column packed with XAD-2 resin beads, to which nonpolar compounds adsorb. Sampling rates are set to optimum volumes to ensure maximum extraction of target compounds from the sample water. Samples are pumped on a flow-proportioned basis to achieve the desired sample volumes over an approximately 30-day period. This requires predictions of total river discharges during the sampling period, which predictions are not always borne out, resulting in either longer sampling periods or higher or lower than the targeted sample volume. Higher sample volumes provide lower analytical detection limits. Both the particle filter and resin beads are extracted in the laboratory and the extracts are combined and analyzed to provide a total concentration of each compound in the extracted volume of water. |
QAPP Information: |
CCLEAN has an approved QAPP |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57183 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for DDD. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDD is 28.0 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57184 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for DDD. Data assessed were suspended sediment samples isolated from the whole water sample. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDD is 28.0 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-2/25/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57168 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for DDD. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDD is 28.0 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57170 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for DDD. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDD is 28.0 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57182 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for DDD. Data assessed were suspended sediment samples isolated from the whole water sample. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for sum of DDD is 28.0 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-2/25/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153099 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153101 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152752 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152963 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
153121 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152945 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152764 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 2 of the 6 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152946 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152823 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 2 of the 6 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2015-06-09 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152985 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2010-05-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152812 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
152751 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for DDD (Dichlorodiphenyldichloroethane) . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for Sum DDD from MacDonald et al., 2000a which states that the probable effect concentration for Sum DDD is 28 ug/kg. (dw = Dry Weight) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148678 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 1 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Chironomus dilutus, for Survival, Chironomus dilutus, for Growth (wt/surv indiv), Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SBR ) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148693 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
10 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
4 of the 10 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2009-06-16 and 2018-06-05. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148711 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 3 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SSP ) |
Temporal Representation: |
The samples were collected between the dates of 2017-07-26 and 2018-04-25. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148665 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 1 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Chironomus dilutus, for Survival, Chironomus dilutus, for Growth (wt/surv indiv), Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SBR ) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148712 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 3 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SSP ) |
Temporal Representation: |
The samples were collected between the dates of 2017-07-26 and 2018-04-25. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 130065, DDD (Dichlorodiphenyldichloroethane)
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57167 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDD(p,p). Nine sample result(s) were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The DDD criteria for the protection of human health from consumption of organisms only is 0.00084 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
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Line of Evidence (LOE) for Decision ID 108261, Lead
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Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
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LOE ID: |
168148 |
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Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
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SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
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Evaluation Guideline: |
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Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
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LOE ID: |
167381 |
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Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
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Beneficial Use: |
Municipal & Domestic Supply |
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Number of Samples: |
1 |
Number of Exceedances: |
1 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
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|
SWAMP Data: |
Non-SWAMP |
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Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
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Evaluation Guideline: |
The California Public Health Goal for lead in sources of drinking water is 0.0002 mg/L. (OEHHA 2009) |
Guideline Reference: |
Public Health Goal for Lead in Drinking Water |
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Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
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Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
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LOE ID: |
168006 |
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Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
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Beneficial Use: |
Agricultural Supply |
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Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
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|
SWAMP Data: |
Non-SWAMP |
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Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for lead for livestock watering as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
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Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
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LOE ID: |
154789 |
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Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
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Beneficial Use: |
Warm Freshwater Habitat |
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Number of Samples: |
1 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Lead . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
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SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
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Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for lead in 128 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
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Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
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QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
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LOE ID: |
167688 |
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Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
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Beneficial Use: |
Warm Freshwater Habitat |
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Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
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Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
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LOE ID: |
168300 |
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Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
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Beneficial Use: |
Cold Freshwater Habitat |
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Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167976 |
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Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
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Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167756 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167939 |
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Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
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Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Public Health Goal for lead in sources of drinking water is 0.0002 mg/L. (OEHHA 2009) |
Guideline Reference: |
Public Health Goal for Lead in Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167848 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Public Health Goal for lead in sources of drinking water is 0.0002 mg/L. (OEHHA 2009) |
Guideline Reference: |
Public Health Goal for Lead in Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167878 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for lead for livestock watering as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167362 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
8 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 8 of 9 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Public Health Goal for lead in sources of drinking water is 0.0002 mg/L. (OEHHA 2009) |
Guideline Reference: |
Public Health Goal for Lead in Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167888 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for lead for livestock watering as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154751 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Lead . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for lead in 128 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167788 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Public Health Goal for lead in sources of drinking water is 0.0002 mg/L. (OEHHA 2009) |
Guideline Reference: |
Public Health Goal for Lead in Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167320 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for lead for livestock watering as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167682 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167689 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168057 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Public Health Goal for lead in sources of drinking water is 0.0002 mg/L. (OEHHA 2009) |
Guideline Reference: |
Public Health Goal for Lead in Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167735 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Public Health Goal for lead in sources of drinking water is 0.0002 mg/L. (OEHHA 2009) |
Guideline Reference: |
Public Health Goal for Lead in Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167892 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168008 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for lead for livestock watering as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168303 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Public Health Goal for lead in sources of drinking water is 0.0002 mg/L. (OEHHA 2009) |
Guideline Reference: |
Public Health Goal for Lead in Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154849 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Lead . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for lead in 128 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167357 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for lead for livestock watering as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167731 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167747 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168159 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Public Health Goal for lead in sources of drinking water is 0.0002 mg/L. (OEHHA 2009) |
Guideline Reference: |
Public Health Goal for Lead in Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154735 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Lead . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for lead in 128 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154602 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Lead . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for lead in 128 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167382 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for lead for livestock watering as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167596 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 2 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Public Health Goal for lead in sources of drinking water is 0.0002 mg/L. (OEHHA 2009) |
Guideline Reference: |
Public Health Goal for Lead in Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167847 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for lead for livestock watering as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167750 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for lead for livestock watering as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167984 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for lead for livestock watering as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154892 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Lead . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for lead in 128 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168238 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167834 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Public Health Goal for lead in sources of drinking water is 0.0002 mg/L. (OEHHA 2009) |
Guideline Reference: |
Public Health Goal for Lead in Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167999 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168009 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168186 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
168299 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167937 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for lead for livestock watering as 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
17370 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Lead. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for lead is 128 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
17371 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Lead. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for lead is 128 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57205 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Lead. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for lead is 128 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57191 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Lead. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for lead is 128 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154732 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 6 samples exceeded the evaluation guideline for Lead . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for lead in 128 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154646 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Lead . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for lead in 128 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108261, Lead
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
167881 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Lead. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148665 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 1 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Chironomus dilutus, for Survival, Chironomus dilutus, for Growth (wt/surv indiv), Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SBR ) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148712 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 3 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SSP ) |
Temporal Representation: |
The samples were collected between the dates of 2017-07-26 and 2018-04-25. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148717 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 2 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAC ) |
Temporal Representation: |
The samples were collected between the dates of 2013-05-28 and 2017-04-26. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148830 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00L ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148834 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00U ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57424 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Five samples were collected to evaluate sediment toxicity. None of the 5 samples exhibited significant toxicity.
The toxicity tests included growth and survival of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location. Samples collected in 2005 and 2006, in the data file associated with this LOE, are not included in this LOE because they were included in the previous assessment cycle. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant effect is defined here using a two-tier approach consistent with the method used by the SWAMP program. The effect must be significant when compared to the control sample based on statistical test alpha level of 0.05 (Probability field in data set) AND the mean must be more than 20 percent different from the control (PercentControl field in data set). |
Guideline Reference: |
Major and Trace Element Analytical Methods of the National Status and Trends Program: 2000-2006. |
|
Spatial Representation: |
The samples were collected at two lower Salinas River stations (309SAC and 309SSP). |
Temporal Representation: |
The samples were collected in annually in April 2007-2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. QAPP for the Cooperative Monitoring program for Agriculture in Region 3. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148976 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Confluences for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-23 and 2012-07-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149068 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00L ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148553 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by RWB3 Cooperative Monitoring Program for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAG ) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148676 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
10 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
4 of the 10 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Growth (wt/surv indiv), Hyalella azteca, for Survival |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309DAV ) |
Temporal Representation: |
The samples were collected between the dates of 2009-06-16 and 2018-06-05. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79704 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Five samples were collected to evaluate sediment toxicity. None of the 5 samples exhibited significant toxicity.
The toxicity tests included growth and survival of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location. Samples collected in 2005 and 2006, in the data file associated with this LOE, are not included in this LOE because they were included in the previous assessment cycle. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Significant effect is defined here using a two-tier approach consistent with the method used by the SWAMP program. The effect must be significant when compared to the control sample based on statistical test alpha level of 0.05 (Probability field in data set) AND the mean must be more than 20 percent different from the control (PercentControl field in data set). |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
|
Spatial Representation: |
The samples were collected at two lower Salinas River stations (309SAC and 309SSP). |
Temporal Representation: |
The samples were collected in annually in April 2007-2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. QAPP for the Cooperative Monitoring program for Agriculture in Region 3. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57440 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity and did not exhibit significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Coastal Confluences 2008 2009 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The sample was collected at stations 309DAV - Salinas River at Davis Road. |
Temporal Representation: |
The sample was collected in May 2009. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
148678 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
1 of the 1 samples collected by SWAMP Stream Pollution Trends for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Chironomus dilutus, for Survival, Chironomus dilutus, for Growth (wt/surv indiv), Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SBR ) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149049 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
0 of the 1 samples collected by SWAMP RWB3 CCAMP Coastal Lagoons for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) exhibited toxicity. A sample may have multiple toxicity test results, but will only be counted once. A sample is defined as being collected on the same day, at the same location with the same lab sample ID (if provided). The following organisms and parameters were utilized for the toxicity tests: Hyalella azteca, for Survival, Hyalella azteca, for Growth (wt/surv indiv) |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coastal Basin Plan 2019). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 station. Monitoring site: ( 309SAL00U ) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
79701 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
One sample was collected to evaluate sediment toxicity. None of the samples exhibited significant toxicity. The toxicity test included survival and growth of Hyalella azteca. One sample can have multiple toxicity test results but will be counted only once. One sample is defined as being collected on the same day at the same location with the same lab sample id (if provided). |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. Region 3 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity is defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. For SWAMP data exceedances are counted with the significant effect code SL. SL is defined as the result being significant compared to the negative control based on a statistical test, less than stated the alpha level, AND less than the evaluation threshold. |
Guideline Reference: |
Methods for Measuring the Toxicity and Bioaccumulation of Sediment-associated Contaminants with Freshwater Invertebrates, Second Edition. U.S. Environmental Protection Agency Office of Research and Development, Duluth, MI , U.S. Environmental Protection Agency Office of Water, Washington, DC EPA-600/R-99/064 |
Guideline Reference: |
SWAMP_Memo_Toxicity_Data_Intrepretation |
|
Spatial Representation: |
The samples were collected at stations 309DAVxxx. |
Temporal Representation: |
The sample was collected in June 2008. |
Environmental Conditions: |
|
QAPP Information: |
The SWAMP QAPP (2002) was followed. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57439 |
|
Pollutant: |
Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Three samples were collected to evaluate sediment toxicity. One of the three samples exhibited significant toxicity. The toxicity tests included survival and growth of Hyalella azteca. Statistically significant effects on Hyalella azteca were observed in the sample collected on 10/28/2009. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in, human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Toxicity was defined as a statistically significant effect in the sample exposure compared to the control using EPA-recommended hypothesis testing. The t-test is used to determine if there is a statistically significant decrease in organism response in the sample as compared to the control. In the SWAMP data format, a Significance Effect Code of SL denotes toxic test results. |
Guideline Reference: |
Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms, Fifth Edition. EPA-821-R-02-012 |
Guideline Reference: |
Short-term Methods for Estimating the Chronic Toxicity of Effluents and Receiving Waters to Freshwater Organisms. Fourth Edition. Office of Water, U.S. Environmental Protection Agency. Washington, D.C. EPA-821-R-02-013 |
|
Spatial Representation: |
The samples were collected at Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) station 309DAV-Salinas River at Davis Road. |
Temporal Representation: |
The samples were collected in July and October 2008 and October 2009. |
Environmental Conditions: |
|
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170713 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170727 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2 (Water Quality Control Plan, Central Coast Basin) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The maximum contaminant level of nickel in public water systems shall be 0.1 mg/L (California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155129 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Nickel . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for nickel in 48.6 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155067 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Nickel . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for nickel in 48.6 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171263 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2 (Water Quality Control Plan, Central Coast Basin) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The maximum contaminant level of nickel in public water systems shall be 0.1 mg/L (California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170552 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170395 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171085 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170882 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170910 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155068 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Nickel . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for nickel in 48.6 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171157 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2 (Water Quality Control Plan, Central Coast Basin) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The maximum contaminant level of nickel in public water systems shall be 0.1 mg/L (California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170551 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nickel for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170277 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170759 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2 (Water Quality Control Plan, Central Coast Basin) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The maximum contaminant level of nickel in public water systems shall be 0.1 mg/L (California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170655 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170305 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
154963 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 5 of the 6 samples exceeded the evaluation guideline for Nickel . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for nickel in 48.6 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170876 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170884 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170420 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170681 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170355 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nickel for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170580 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170349 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170250 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nickel for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171330 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2 (Water Quality Control Plan, Central Coast Basin) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The maximum contaminant level of nickel in public water systems shall be 0.1 mg/L (California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170716 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2 (Water Quality Control Plan, Central Coast Basin) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The maximum contaminant level of nickel in public water systems shall be 0.1 mg/L (California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170280 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170753 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170901 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155069 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 5 of the 6 samples exceeded the evaluation guideline for Nickel . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for nickel in 48.6 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2009-06-16 to 2018-06-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170252 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171039 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2 (Water Quality Control Plan, Central Coast Basin) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The maximum contaminant level of nickel in public water systems shall be 0.1 mg/L (California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170550 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nickel for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170234 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nickel for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155092 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Nickel . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for nickel in 48.6 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170576 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170324 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nickel for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171048 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155109 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 1 samples exceeded the evaluation guideline for Nickel . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for nickel in 48.6 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170831 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
17092 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Nickel. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for nickel is 48.6 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
17093 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Nickel. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for nickel is 48.6 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57152 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Nickel. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for nickel is 48.6 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57151 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Nickel. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity for sediment-dwelling organisms) for nickel is 48.6 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24564 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-5/26/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24485 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24486 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected on a single day 3/29/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
24565 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPnorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Toxicity, Hyalella azteca Survival (%) 10 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 4/14/2005-5/26/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170687 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170820 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170711 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nickel for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170570 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nickel for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171305 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2 (Water Quality Control Plan, Central Coast Basin) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The maximum contaminant level of nickel in public water systems shall be 0.1 mg/L (California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170591 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2 (Water Quality Control Plan, Central Coast Basin) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The maximum contaminant level of nickel in public water systems shall be 0.1 mg/L (California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
171260 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2 (Water Quality Control Plan, Central Coast Basin) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The maximum contaminant level of nickel in public water systems shall be 0.1 mg/L (California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170869 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170877 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Human health risk associated with organism consumption is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170886 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2 (Water Quality Control Plan, Central Coast Basin) |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The maximum contaminant level of nickel in public water systems shall be 0.1 mg/L (California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170650 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170282 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nickel for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170423 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nickel for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
155130 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 1 of the 1 samples exceeded the evaluation guideline for Nickel . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
In freshwater sediments the probable effect concentration (predictive of sediment toxicity) for nickel in 48.6 mg/Kg dry weight (MacDonald et al. 2000a) |
Guideline Reference: |
Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Environmental Contamination and Toxicology. 39: 20-31 |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SBR. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2018-06-13 to 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108270, Nickel
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
170909 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nickel. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for nickel for irrigation supply as 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181063 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180926 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181147 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181405 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for selenium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181088 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181123 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for selenium for irrigation supply as 0.02 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180820 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180787 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 6 of 9 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181259 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181153 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180943 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for selenium for irrigation supply as 0.02 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181462 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for selenium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181081 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181121 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181514 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for selenium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181143 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 4 of 9 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for selenium for irrigation supply as 0.02 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181163 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for selenium for irrigation supply as 0.02 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181540 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 9 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for selenium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181408 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for selenium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181132 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for selenium for irrigation supply as 0.02 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181513 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for selenium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181221 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for selenium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180868 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for selenium for irrigation supply as 0.02 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180920 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180771 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-06-28 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180794 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for selenium for irrigation supply as 0.02 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181169 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2017-09-27 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181515 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All inland surface waters, enclosed bays, and estuaries shall not contain concentrations of inorganic chemicals in excess of the maximum contaminant levels for primary drinking water standards specified in California Code of Regulations, Title 22, Division 4, Chapter 15, Sections 64431 and 64433.2. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The California Maximum Contaminant Level for selenium is 0.05 mg/L (California Code of Regulations, Title 22). |
Guideline Reference: |
California MCLs - Title 17 and Title 22 documents for 2019 - California Regulations Related to Drinking Water |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180784 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. In addition, waters used for irrigation and livestock watering shall not exceed concentrations for those chemicals listed in the Central Coast Basin Plan and identified as the maximum concentration for selenium for irrigation supply as 0.02 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180913 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
181510 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 6 of 9 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-18 and 2018-12-04 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108285, Selenium
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
180979 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 2 samples exceeded the water quality threshold for Selenium. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The criterion continuous concentration to protect aquatic life in freshwater is 0.005 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-28 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216966 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
103 |
Number of Exceedances: |
20 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 20 of 103 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2010-07-13 and 2018-12-05 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216876 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
217057 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2018-06-13 and 2018-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216633 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
10 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 4 of 10 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-11 and 2018-11-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216826 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-33) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2013-05-04 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216776 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U) |
Temporal Representation: |
The samples were collected between the dates of 2016-08-23 and 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216843 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 24 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SBR) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-12-11 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216917 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309PS0370) |
Temporal Representation: |
The samples were collected between the dates of 2017-06-13 and 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216742 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309DAV) |
Temporal Representation: |
The samples were collected between the dates of 2012-07-22 and 2012-07-22 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216646 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Dissolved Oxygen Study data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-08-15 and 2012-08-15 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216746 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed MBNMS Snapshot Day data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309-SALIN-32) |
Temporal Representation: |
The samples were collected between the dates of 2011-05-07 and 2012-05-05 |
Environmental Conditions: |
|
QAPP Information: |
Monterey Bay NMS. 2003. California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP). |
QAPP Information Reference(s): |
California Coast Wide Snapshot Day 2003 Quality Assurance Project Plan (QAPP) |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216918 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
47 |
Number of Exceedances: |
16 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 16 of 47 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SSP) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-29 and 2018-11-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216903 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
38 |
Number of Exceedances: |
13 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 13 of 38 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAG) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-09-18 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
18631 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
13 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Coastal Watershed Council (Snapshot day monitoring) (R3_Snap) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 13 samples exceed the criterion for Water Temperature. |
Data Reference: |
Final Data File used for assessment: Monterey Bay National Marine Sanctuary Volunteer Monitoring Network Data. 2003-2006
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (General Objective in Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Inland Fishes of California (Moyle 1976) states that for rainbow trout the optimum range for growth and completion of most life stages is 13-21 degrees C (page 129). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 4 monitoring sites [ 309-SALIN-31 - Salinas River at Gypse Camp, 309-SALIN-32 - Salinas River at Davis Road, 309-SALIN-33 - Salinas River at Chualar Bridge, 309-SKYLI-31 - Skyline] |
Temporal Representation: |
Data was collected over the time period 5/17/2003-5/6/2006. Coastal Watershed Council Snapshot Day Monitoring is conducted annually. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
State Board approved QAPP. Multiple errors were identified in data and were flagged or fixed by RB staff (in communication with Project staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12867 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
62 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Salinas (Salinas) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 6 of 62 samples exceed the criterion for Water Temperature. |
Data Reference: |
Final Data File used for assessment: CCAMP Salinas Toxicity data |
|
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (General Objective in Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Inland Fishes of California (Moyle 1976) states that for rainbow trout the optimum range for growth and completion of most life stages is 13-21 degrees C (page 129). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 2/1/1999-12/12/2006. Salinas watershed is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
13768 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed Central Coast Watershed Studies (R3_CCOWS) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Water Temperature. |
Data Reference: |
Final Data File used for assessment: CCoWS (Central Coast Watershed Studies) Water Quality Data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (General Objective in Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Inland Fishes of California (Moyle 1976) states that for rainbow trout the optimum range for growth and completion of most life stages is 13-21 degrees C (page 129). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ Chualar River Rd, Davis Rd] |
Temporal Representation: |
Data was collected on a single day 1/3/2002. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
Data quality is good and Standard Operating Procedures are well documented in QAPP. However, data documentation is poor and replicate samples and other quality assurance measurements are not consistently documented in this data set. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57375 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
12 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff assessed CMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 12 of 40 samples exceed the criterion for Water Temperature. |
Data Reference: |
Data from Region 3 Conditional Waiver Cooperative Monitoring Program, Jan. 2007-Jun. 2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River (Lower) - 309SSP, Salinas River (Lower) - 309SAC] |
Temporal Representation: |
Data was collected over the time period 1/30/2007-12/8/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the CCRWQCB Cooperative Monitoring Program for Agriculture data and provided in SWAMP format. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51333 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Water Temperature. |
Data Reference: |
Salinas Rotation field data 2007 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-2/14/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
51332 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 39 samples exceed the criterion for Water Temperature. |
Data Reference: |
Coastal Confluences field data 2007-2010 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Data for Various Pollutants in Westside San Joaquin Water Quality Coalition, 2004-2009.
|
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-6/14/2010. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
14505 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
43 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCWQP Northern Area Ag-Waiver Monitoring (R3_CMPNorth) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 7 of 43 samples exceed the criterion for Water Temperature. |
Data Reference: |
Final Data File used for assessment: Central Coast Water Quality Preservation Inc toxicity data
|
|
Final Data File used for assessment: Central Coast Water Quality Preservation Inc water quality data
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (General Objective in Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Inland Fishes of California (Moyle 1976) states that for rainbow trout the optimum range for growth and completion of most life stages is 13-21 degrees C (page 129). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 2 monitoring sites [ 309SAC-Salinas River at Chualar bridge on River Road, 309SSP - Salinas River at Spreckles] |
Temporal Representation: |
Data was collected over the time period 1/27/2005-12/13/2006. Cooperative Monitoring Program (CMP) staff conduct monitoring for conventional pollutants at all Ag Waiver monitoring sites monthly. CMP staff also conduct water toxicity monitoring quarterly and sediment toxicity monitoring annually (in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the Cooperative Monitoring Program QAPP, (Clark and Ogle 2006). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12904 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
52 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 4 of 52 samples exceed the criterion for Water Temperature. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (General Objective in Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Inland Fishes of California (Moyle 1976) states that for rainbow trout the optimum range for growth and completion of most life stages is 13-21 degrees C (page 129). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 7/25/2001-12/12/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
15245 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
198 |
Number of Exceedances: |
39 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed National Estuarine Research Reserve Monitoring Program (R3_ESNERR) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 39 of 198 samples exceed the criterion for Water Temperature. |
Data Reference: |
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Field Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 2006
|
|
Final Data File used for assessment: ESNERR (Elkhorn Slough National Reserve) Water Quality Data from 94-04
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (General Objective in Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Inland Fishes of California (Moyle 1976) states that for rainbow trout the optimum range for growth and completion of most life stages is 13-21 degrees C (page 129). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River Bridge] |
Temporal Representation: |
Data was collected over the time period 1/20/1990-10/10/2006. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
QAPP was adopted for work conducted since 2005. Prior to 2005 no QAPP was in place and data entry was completed by volunteers. Multiple errors were identified in data and were flagged by RB staff (in communication with Elkhorn Slough Program staff) prior to assessment of data. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
47844 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
9 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Region 3 - Central Coast Region staff assessed R3 public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 1 of 9 samples exceed the criterion for Water Temperature. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309DAV-Salinas River at Davis Road ] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009 3:40:00 PM. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
A QAPP was not specifically written for this project. However, staff conducting data collection and laboratory analysis are also SWAMP contractors. All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in |
QAPP Information Reference(s): |
2002. Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. California Department of Fish and Game, Monterey, CA |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
52935 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Water Board Central Coast Water Board Staff assessed public submissions data for Salinas River (Lower) to determine beneficial use support and results are as follows: 2 of 8 samples exceed the criterion for Water Temperature. |
Data Reference: |
Data from Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program, Jan. 2007-Jul. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 1 monitoring site [ 309SLRBRG - Salinas River at the Highway 1/Railroad Bridge ] |
Temporal Representation: |
Data was collected over the time period 1/8/2007-7/10/2007. |
Environmental Conditions: |
Central Coast Water Board Staff are not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Data was collected following the Quality Assurance Project Plan for Elkhorn Slough National Estuarine Research Reserve's Volunteer Monthly Water Quality Program. Replicate data were identified in data and were qualified by RB Central Coast Water Board S |
QAPP Information Reference(s): |
Quality Assurance Project Plan, Elkhorn Slough National Estuarine Research Reserve Volunteer Monthly Water Quality Program. May 15, 2009, Ver.1.3 |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
12093 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
17 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for Salinas River (Lower) to determine beneficial use support and results are as follows: 3 of 17 samples exceed the criterion for Water Temperature. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (General Objective in Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Inland Fishes of California (Moyle 1976) states that for rainbow trout the optimum range for growth and completion of most life stages is 13-21 degrees C (page 129). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (Lower) was collected at 3 monitoring sites [ 309DAV-Salinas River at Davis Road , 309SAC-Salinas River at Chualar bridge on River Road, 309SBR-Salinas River at Highway 1 ] |
Temporal Representation: |
Data was collected over the time period 7/6/1999-8/31/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216830 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP SpecialStudies data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SALDDM) |
Temporal Representation: |
The samples were collected between the dates of 2013-06-26 and 2013-06-26 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216797 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
31 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Salinas Stormwater Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 5 of 31 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SDD) |
Temporal Representation: |
The samples were collected between the dates of 2014-09-09 and 2017-04-12 |
Environmental Conditions: |
|
QAPP Information: |
Pacific EcoRisk. 2012. QAPP for the City of Salinas Stormwater Monitoring Program. |
QAPP Information Reference(s): |
QAPP for the City of Salinas Stormwater Monitoring Program |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216844 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
44 |
Number of Exceedances: |
12 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 12 of 44 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2010-04-28 and 2018-07-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 126134, Temperature, water
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
216927 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
18 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 3 of 18 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Board that such alteration in temperature does not adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The optimum range for growth and completion of most life stages of rainbow trout is 13-21 degrees Celsius (Moyle 1976). |
Guideline Reference: |
Inland Fishes of California |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAC) |
Temporal Representation: |
The samples were collected between the dates of 2012-01-10 and 2018-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151748 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 5 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2011-09-07 to 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159195 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Bifenthrin. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Water quality criteria report for Bifenthrin. Phase III: application of the pesticide water quality criteria methodology. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2016-09-21 and 2016-09-21 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158983 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Bifenthrin. Although a total of 12 samples were collected, 12 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Water quality criteria report for Bifenthrin. Phase III: application of the pesticide water quality criteria methodology. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-09 to 2017-08-07 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151305 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151329 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159151 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Bifenthrin. Although a total of 12 samples were collected, 12 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Water quality criteria report for Bifenthrin. Phase III: application of the pesticide water quality criteria methodology. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (Monterey 13). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-09 to 2017-08-07 |
Environmental Conditions: |
|
QAPP Information: |
Data is exempt from QAPP requirement |
QAPP Information Reference(s): |
This is a placeholder reference for data that was collected after QAPP requirements were developed, but exempt from the requirements. |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151681 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
158851 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Bifenthrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Water quality criteria report for Bifenthrin. Phase III: application of the pesticide water quality criteria methodology. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57164 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for BIFENTHRIN. Nine sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Bifenthrin does not exceed 0.0006 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57163 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for BIFENTHRIN. Nine sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life (Central Coast Basin Plan General Objective). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of Bifenthrin does not exceed 0.0006 ug/L. |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 1/7/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The data was collected for the Watershed-scale Evaluation of Agricultural BMP Effectiveness Protecting Critical Coastal Habitats project. A QAPP was provided and the data was analyzed at the Marine Pollution Studies Laboratory and submitted in SWAMP format. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57385 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: A total of 3 samples were collected, however 1 of the non-detect sample results were compared to the evaluation guideline and the OC Normalized method detection limit result was above the guideline and therefore could not be quantified with the level of certainty required by the Listing Policy. Zero of the remaining 2 quantifiable sample results were exceeding the evaluation guideline. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of three toxicity LC50 values from Amweg et al. (2005) and one toxicity LC50 value from Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57046 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Bifenthrin. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of three toxicity LC50 values from Amweg et al. (2005) and one toxicity LC50 value from Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57045 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Bifenthrin. |
Data Reference: |
Statewide Stream Pollution Trends Study 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coast Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of three toxicity LC50 values from Amweg et al. (2005) and one toxicity LC50 value from Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAVxxx] |
Temporal Representation: |
Data was collected on a single day 6/17/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
SWAMP data collected before September 2008 followed the QAMP (2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57047 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: A total of 3 samples were collected, however 1 of the non-detect sample results were compared to the evaluation guideline and the OC Normalized method detection limit result was above the guideline and therefore could not be quantified with the level of certainty required by the Listing Policy. Zero of the remaining 2 quantifiable sample results were exceeding the evaluation guideline. |
Data Reference: |
Data for various pollutants in the Pajaro, Salinas, and Santa Maria River estuaries, Jan. 2008-Oct. 2009 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. There shall be no increase in pesticide concentrations found in bottom sediments or aquatic life (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of three toxicity LC50 values from Amweg et al. (2005) and one toxicity LC50 value from Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 1 monitoring site [ Salinas River at Davis Road - 309DAV] |
Temporal Representation: |
Data was collected over the time period 7/2/2008-10/28/2009. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
QAPP Information Reference(s): |
Quality Assurance Project Plan from UC Davis Marine Pollution Studies Laboratory. |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57387 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support. Six samples were collected however they were all non-detect and the laboratory method detection limit was above the guideline, therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of bifenthrin does not exceed 0.0006 ug/L and if the 1-h average concentration does not exceed 0.004 ug/L. For this assessment, the 4-day average concentration was used. Mixtures of bifenthrin and other pyrethroids should be considered in an additive manner (Fojut et al. 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
57386 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed DPR data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support. Six samples were collected however they were all non-detect and the laboratory method detection limit was above the guideline, therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Final Data File used for assessment: Department of Pesticide Regulation Data_ 2003-2005
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan for the Central Coastal Basin (CCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses. (Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the 4-day average concentration of bifenthrin does not exceed 0.0006 ug/L and if the 1-h average concentration does not exceed 0.004 ug/L. For this assessment, the 4-day average concentration was used. Mixtures of bifenthrin and other pyrethroids should be considered in an additive manner (Fojut et al. 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data for this line of evidence for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) was collected at 2 monitoring sites [ Salinas River at Davis Road - 309DAV, Salinas River - 309SBR] |
Temporal Representation: |
Data was collected over the time period 9/13/2004-5/3/2005. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
All data was collected and analyzed following Department of Pesticide Regulation Standard Operating Procedures (Available online at http://www.cdpr.ca.gov/docs/emon/pubs/sop.htm). |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149129 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Bifenthrin. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149124 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality standard for Bifenthrin. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151138 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 3 samples exceeded the evaluation guideline for Bifenthrin. Although a total of 4 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-04-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159152 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 CCLEAN data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Bifenthrin. |
Data Reference: |
Tissue, Water or the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Water quality criteria report for Bifenthrin. Phase III: application of the pesticide water quality criteria methodology. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (SalRiv2) |
Temporal Representation: |
The samples were collected between the dates of 2016-09-21 and 2016-09-21 |
Environmental Conditions: |
|
QAPP Information: |
Applied Marine Sciences. 2019. Central Coast Long-Term Environmental Assessment Network. |
QAPP Information Reference(s): |
Central Coast Long-Term Environmental Assessment Network |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151409 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 3 samples exceeded the evaluation guideline for Bifenthrin. Although a total of 4 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SSP. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2018-04-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151139 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00U. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149122 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Bifenthrin. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected on 2018-08-15. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151157 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151265 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151558 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAL00L. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151327 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Salinas Rotation data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Tissue, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159078 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Bifenthrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Water quality criteria report for Bifenthrin. Phase III: application of the pesticide water quality criteria methodology. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
149128 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Surface Water Monitoring Project data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality standard for Bifenthrin. |
Data Reference: |
CCAMP organic chemistry data from 08/15/2018. |
|
CCAMP organic chemistry data from 12/5/2018. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: ll. Pyrethroid insecticides. Reviews of Environmental Contamination and Toxicology 216:51-103. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected on 2018-12-05. |
Environmental Conditions: |
|
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAPrP. QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159006 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Bifenthrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Water quality criteria report for Bifenthrin. Phase III: application of the pesticide water quality criteria methodology. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00L). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151406 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Stream Pollution Trends data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 5 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2011-09-07 to 2017-06-13 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151502 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Confluences data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309DAV. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2012-07-23 to 2012-07-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008, SWAMP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
159388 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB3 CCAMP Coastal Lagoons data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Bifenthrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall reach concentrations that adversely affect beneficial uses (Water Quality Control Plan, Central Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
Aquatic life should not be affected unacceptably if the four-day average concentration of bifenthrin does not exceed 0.0006 ug/L (Fojut et al., 2012). |
Guideline Reference: |
Water quality criteria report for Bifenthrin. Phase III: application of the pesticide water quality criteria methodology. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (309SAL00U). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2016-08-23 to 2016-08-23 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP 2008 and SPoT 2012 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151122 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151661 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAC. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-04-26 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|
Line of Evidence (LOE) for Decision ID 108303, Bifenthrin
|
Region 3 |
Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) |
|
|
LOE ID: |
151123 |
|
Pollutant: |
Bifenthrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB3 Cooperative Monitoring Program data for Salinas River (lower, estuary to near Gonzales Rd crossing, watersheds 30910 and 30920) to determine beneficial use support and the results are as follows: 0 of the 2 samples exceeded the evaluation guideline for Bifenthrin . |
Data Reference: |
Field, Habitat, Sediment, Toxicity, Water data for the 2020/2022 integrated report in Region 3.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan for the Central Coastal Basin |
|
Evaluation Guideline: |
The evaluation guideline for bifenthrin is the median lethal concentration (LC50) of 0.43 ug/g and is normalized by the percentage of organic carbon in the sediment sample. The LC50 0.43 ug/g is the geometric mean of LC50 values for bifenthrin from Amweg et al. (2005) and Amweg and Weston (2007). |
Guideline Reference: |
Use and Toxicity of Pyrethroid Pesticides in the Central Valley, California, USA. Environmental Toxicology and Chemistry, 24:966-972, with erratum 24:No. 5 |
Guideline Reference: |
Whole-sediment toxicity identification evaluation tools for pyrethroid insecticides: I. piperonyl butoxide addition. Environ. Toxicol. Chem. 26:2389-2396. |
|
Spatial Representation: |
Data were collected from 1 station(s). Station Code(s): 309SAG. |
Temporal Representation: |
Data for this waterbody were collected over the date range 2010-05-24 to 2017-09-27 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for Monitoring for the Region 3 Conditional Ag Waiver Cooperative Monitoring Program, Revision 6 |
|