Final California 2018 Integrated Report (303(d) List/305(b) Report)

Supporting Information

Regional Board 5 - Central Valley Region

Water Body Name: Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
Water Body ID: CAR5192200020070510154406
Water Body Type: River & Stream
 
DECISION ID
92234
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Bifenthrin
Final Listing Decision: Do Not Delist from 303(d) list (being addressed with USEPA approved TMDL)
Last Listing Cycle's Final Listing Decision: List on 303(d) list (TMDL required list)(2016)
Revision Status Revised
Sources: A Source Unknown
TMDL Name: Phase 2 (Pyrethroids)Sacramento and San Joaquin Pesticides Basin Plan Amendment and TMDLs
TMDL Project Code: 872
Date TMDL Approved by USEPA: 04/22/2019
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: This pollutant is being considered for removal on the CWA section 303(d) List under sections 2.2 and 4.11 of the Listing Policy. Under 4.11 of the Policy, a minimum of one line of evidence is needed to assess listing status.

Two lines of evidence are available in the administrative record to assess this pollutant.

Based on the readily available data and information, the weight of evidence indicates that there is sufficient justification against removing this water segment-pollutant combination from the CWA section 303(d) List. There is sufficient justification to place it in the Being Addressed portion of the CWA 303(d) List because a TMDL has been completed and approved by RWQCB and USEPA, and is expected to result in attainment of the standard.

This conclusion is based on the staff findings that:
1. The data used satisfies the data quality requirements of section 6.1.4 of the Policy.
2. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy.
3. Fourteen of the 14 samples exceed the evaluation guideline for COLD and this sample size is sufficient to determine beneficial use support, with the power and confidence of the Listing Policy. There is an associated sediment toxicity data as required by Section 3.6 of the Listing Policy.
4. The Central Valley Pyrethroid Pesticides TMDL and Basin Plan Amendment was approved by USEPA in 2019.
5. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should not be removed from the section 303(d) list because applicable water quality standards for the pollutant are being exceeded.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation:
 
 
Line of Evidence (LOE) for Decision ID 92234, Bifenthrin
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59090
 
Pollutant: Toxicity
LOE Subgroup: Toxicity
Matrix: Sediment
Fraction: None
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 14
Number of Exceedances: 14
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: One-tenth the organic carbon normalized LC50 values for sediment-bound pyrethroids were used as toxicity thresholds in a toxicity unit (TU) analysis. Samples containing at least 2 pyrethroids with concentrations above the reporting limit were assessed for additive toxicity.14 of 14 sediment samples indicated a calculated TU > 1, suggesting that samples had pyrethroid pesticides at levels expected to exert additive, chronic toxicity. A combination of 2 or more of the pyrethroids, bifenthrin, fenpropathrin, lambda-cyhalothrin, permethrin, cyfluthrin, cypermethrin, esfenvalerate, and deltamethrin were present in the assessed samples.
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: "The narrative toxicity objective states, ""All waters shall be maintained free of toxic substances in concentrations that produce detrimental physiological responses in human, plant, animal, or aquatic life. This objective applies regardless of whether the toxicity is caused by a single substance or the interactive effect of multiple substances."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for the TU analysis is based on the following: "The concentration of each toxic substance is divided by its toxicologic limit. The resulting ratios are added for substances having similar toxicologic effects and, separately, for carcinogens. The additive toxicity criterion has been violated if the sum of the ratios is >1 (CV Basin Plan, 2011)."
Guideline Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Spatial Representation: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
Line of Evidence (LOE) for Decision ID 92234, Bifenthrin
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59018
 
Pollutant: Bifenthrin
LOE Subgroup: Pollutant-Sediment
Matrix: Sediment
Fraction: Total
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 14
Number of Exceedances: 14
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: A total of 14 individual sediment samples were collected; 14 of 14 samples exceeded the evaluation guideline (0.043 ug/g OC).
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: The narrative objective for pesticides states, "No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. Discharges shall not result in pesticide concentrations in bottom sediments or aquatic life that adversely affect beneficial uses."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for bifenthrin, 0.043 ug/g OC, is one-tenth of the median lethal concentration for H. azteca (LC50; 0.43 ug/g OC). The LC50 (0.43 ug/g OC) is the geometric mean of OC normalized 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: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
 
DECISION ID
94047
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Cyfluthrin
Final Listing Decision: Do Not Delist from 303(d) list (being addressed with USEPA approved TMDL)
Last Listing Cycle's Final Listing Decision: List on 303(d) list (TMDL required list)(2016)
Revision Status Revised
Sources: A Source Unknown
TMDL Name: Phase 2 (Pyrethroids)Sacramento and San Joaquin Pesticides Basin Plan Amendment and TMDLs
TMDL Project Code: 872
Date TMDL Approved by USEPA: 04/22/2019
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: This pollutant is being considered for removal on the CWA section 303(d) List under sections 2.2 and 4.11 of the Listing Policy. Under 4.11 of the Policy, a minimum of one line of evidence is needed to assess listing status.

Two lines of evidence are available in the administrative record to assess this pollutant.

Based on the readily available data and information, the weight of evidence indicates that there is sufficient justification against removing this water segment-pollutant combination from the CWA section 303(d) List. There is sufficient justification to place it in the Being Addressed portion of the CWA 303(d) List because a TMDL has been completed and approved by RWQCB and USEPA, and is expected to result in attainment of the standard.

1. The data used satisfies the data quality requirements of section 6.1.4 of the Policy.
2. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy.
3. Ten of the 14 samples exceed the evaluation guideline for COLD and this sample size is sufficient to determine beneficial use support, with the power and confidence of the Listing Policy. There is an associated sediment toxicity data as required by Section 3.6 of the Listing Policy.
4. The Central Valley Pyrethroid Pesticides TMDL and Basin Plan Amendment was approved by USEPA in 2019.
5. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should not be removed from the section 303(d) list because applicable water quality standards for the pollutant are being exceeded.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation:
 
 
Line of Evidence (LOE) for Decision ID 94047, Cyfluthrin
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59090
 
Pollutant: Toxicity
LOE Subgroup: Toxicity
Matrix: Sediment
Fraction: None
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 14
Number of Exceedances: 14
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: One-tenth the organic carbon normalized LC50 values for sediment-bound pyrethroids were used as toxicity thresholds in a toxicity unit (TU) analysis. Samples containing at least 2 pyrethroids with concentrations above the reporting limit were assessed for additive toxicity.14 of 14 sediment samples indicated a calculated TU > 1, suggesting that samples had pyrethroid pesticides at levels expected to exert additive, chronic toxicity. A combination of 2 or more of the pyrethroids, bifenthrin, fenpropathrin, lambda-cyhalothrin, permethrin, cyfluthrin, cypermethrin, esfenvalerate, and deltamethrin were present in the assessed samples.
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: "The narrative toxicity objective states, ""All waters shall be maintained free of toxic substances in concentrations that produce detrimental physiological responses in human, plant, animal, or aquatic life. This objective applies regardless of whether the toxicity is caused by a single substance or the interactive effect of multiple substances."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for the TU analysis is based on the following: "The concentration of each toxic substance is divided by its toxicologic limit. The resulting ratios are added for substances having similar toxicologic effects and, separately, for carcinogens. The additive toxicity criterion has been violated if the sum of the ratios is >1 (CV Basin Plan, 2011)."
Guideline Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Spatial Representation: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
Line of Evidence (LOE) for Decision ID 94047, Cyfluthrin
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59054
 
Pollutant: Cyfluthrin
LOE Subgroup: Pollutant-Sediment
Matrix: Sediment
Fraction: Total
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 14
Number of Exceedances: 10
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: A total of 14 individual sediment samples were collected; 10 of 14 exceeded the evaluation guideline (0.11 ug/g OC).
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: The narrative objective for pesticides states, "No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. Discharges shall not result in pesticide concentrations in bottom sediments or aquatic life that adversely affect beneficial uses."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for cyfluthrin, 0.11 ug/g OC, is one-tenth of the median lethal concentration for H. azteca (LC50; 1.1 ug/g OC). The LC50 (1.1 ug/g OC) is the geometric mean of OC normalized 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: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
 
DECISION ID
94048
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Cyhalothrin, Lambda
Final Listing Decision: Do Not Delist from 303(d) list (being addressed with USEPA approved TMDL)
Last Listing Cycle's Final Listing Decision: List on 303(d) list (TMDL required list)(2016)
Revision Status Revised
Sources: A Source Unknown
TMDL Name: Phase 2 (Pyrethroids)Sacramento and San Joaquin Pesticides Basin Plan Amendment and TMDLs
TMDL Project Code: 872
Date TMDL Approved by USEPA: 04/22/2019
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: This pollutant is being considered for removal on the CWA section 303(d) List under sections 2.2 and 4.11 of the Listing Policy. Under 4.11 of the Policy, a minimum of one line of evidence is needed to assess listing status.

Two lines of evidence are available in the administrative record to assess this pollutant.

Based on the readily available data and information, the weight of evidence indicates that there is sufficient justification against removing this water segment-pollutant combination from the CWA section 303(d) List. There is sufficient justification to place it in the Being Addressed portion of the CWA 303(d) List because a TMDL has been completed and approved by RWQCB and USEPA, and is expected to result in attainment of the standard.

This conclusion is based on the staff findings that:
1. The data used satisfies the data quality requirements of section 6.1.4 of the Policy.
2. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy.
3. Four of the 13 samples exceed the evaluation guideline for COLD and this sample size is insufficient to determine beneficial use support, with the power and confidence of the Listing Policy. There is an associated sediment toxicity data as required by Section 3.6 of the Listing Policy
4. The Central Valley Pyrethroid Pesticides TMDL and Basin Plan Amendment was approved by USEPA in 2019.
5. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should not be removed from the section 303(d) list because applicable water quality standards for the pollutant are being exceeded.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation:
 
 
Line of Evidence (LOE) for Decision ID 94048, Cyhalothrin, Lambda
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59035
 
Pollutant: Cyhalothrin, Lambda
LOE Subgroup: Pollutant-Sediment
Matrix: Sediment
Fraction: Total
 
Beneficial 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: A total of 14 individual sediment samples were collected; 1 sample was below both the reporting limit (0.1 ug/kg dry weight) and the organic carbon normalized evaluation guideline (0.044 ug/g OC) and could not be quantified with the level of certainty required by the listing policy. 4 of 13 samples exceeded the evaluation guideline.
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: The narrative objective for pesticides states, "No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. Discharges shall not result in pesticide concentrations in bottom sediments or aquatic life that adversely affect beneficial uses."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for lambda-cyhalothrin, 0.044 ug/g OC, is one-tenth of the median lethal concentration for H. azteca (LC50; 0.44 ug/g OC). The LC50 (0.44 ug/g OC) is the geometric mean of OC normalized 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: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
Line of Evidence (LOE) for Decision ID 94048, Cyhalothrin, Lambda
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59090
 
Pollutant: Toxicity
LOE Subgroup: Toxicity
Matrix: Sediment
Fraction: None
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 14
Number of Exceedances: 14
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: One-tenth the organic carbon normalized LC50 values for sediment-bound pyrethroids were used as toxicity thresholds in a toxicity unit (TU) analysis. Samples containing at least 2 pyrethroids with concentrations above the reporting limit were assessed for additive toxicity.14 of 14 sediment samples indicated a calculated TU > 1, suggesting that samples had pyrethroid pesticides at levels expected to exert additive, chronic toxicity. A combination of 2 or more of the pyrethroids, bifenthrin, fenpropathrin, lambda-cyhalothrin, permethrin, cyfluthrin, cypermethrin, esfenvalerate, and deltamethrin were present in the assessed samples.
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: "The narrative toxicity objective states, ""All waters shall be maintained free of toxic substances in concentrations that produce detrimental physiological responses in human, plant, animal, or aquatic life. This objective applies regardless of whether the toxicity is caused by a single substance or the interactive effect of multiple substances."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for the TU analysis is based on the following: "The concentration of each toxic substance is divided by its toxicologic limit. The resulting ratios are added for substances having similar toxicologic effects and, separately, for carcinogens. The additive toxicity criterion has been violated if the sum of the ratios is >1 (CV Basin Plan, 2011)."
Guideline Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Spatial Representation: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
 
DECISION ID
94049
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Cypermethrin
Final Listing Decision: Do Not Delist from 303(d) list (being addressed with USEPA approved TMDL)
Last Listing Cycle's Final Listing Decision: List on 303(d) list (TMDL required list)(2016)
Revision Status Revised
Sources: A Source Unknown
TMDL Name: Phase 2 (Pyrethroids)Sacramento and San Joaquin Pesticides Basin Plan Amendment and TMDLs
TMDL Project Code: 872
Date TMDL Approved by USEPA: 04/22/2019
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: This pollutant is being considered for removal on the CWA section 303(d) List under sections 2.2 and 4.11 of the Listing Policy. Under 4.11 of the Policy, a minimum of one line of evidence is needed to assess listing status.

Two lines of evidence are available in the administrative record to assess this pollutant.

Based on the readily available data and information, the weight of evidence indicates that there is sufficient justification against removing this water segment-pollutant combination from the CWA section 303(d) List. There is sufficient justification to place it in the Being Addressed portion of the CWA 303(d) List because a TMDL has been completed and approved by RWQCB and USEPA, and is expected to result in attainment of the standard.

This conclusion is based on the staff findings that:
1. The data used satisfies the data quality requirements of section 6.1.4 of the Policy.
2. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy.
3. Twelve of the 14 samples exceed the evaluation guideline for COLD and this sample size is sufficient to determine beneficial use support, with the power and confidence of the Listing Policy. There is an associated sediment toxicity data as required by Section 3.6 of the Listing Policy.
4. The Central Valley Pyrethroid Pesticides TMDL and Basin Plan Amendment was approved by USEPA in 2019.
5. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should not be removed from the section 303(d) list because applicable water quality standards for the pollutant are being exceeded.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation:
 
 
Line of Evidence (LOE) for Decision ID 94049, Cypermethrin
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59063
 
Pollutant: Cypermethrin
LOE Subgroup: Pollutant-Sediment
Matrix: Sediment
Fraction: Total
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 14
Number of Exceedances: 12
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: A total of 14 individual sediment samples were collected; 12 of 14 samples exceeded the evaluation guideline (0.03 ug/g OC).
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: The narrative objective for pesticides states, "No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. Discharges shall not result in pesticide concentrations in bottom sediments or aquatic life that adversely affect beneficial uses."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for cypermethrin, 0.03 ug/g OC, is one-tenth of the median lethal concentration for H. azteca (LC50; 0.3 ug/g OC). The LC50 (0.3 ug/g OC) is the geometric mean of OC normalized 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: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
Line of Evidence (LOE) for Decision ID 94049, Cypermethrin
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59090
 
Pollutant: Toxicity
LOE Subgroup: Toxicity
Matrix: Sediment
Fraction: None
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 14
Number of Exceedances: 14
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: One-tenth the organic carbon normalized LC50 values for sediment-bound pyrethroids were used as toxicity thresholds in a toxicity unit (TU) analysis. Samples containing at least 2 pyrethroids with concentrations above the reporting limit were assessed for additive toxicity.14 of 14 sediment samples indicated a calculated TU > 1, suggesting that samples had pyrethroid pesticides at levels expected to exert additive, chronic toxicity. A combination of 2 or more of the pyrethroids, bifenthrin, fenpropathrin, lambda-cyhalothrin, permethrin, cyfluthrin, cypermethrin, esfenvalerate, and deltamethrin were present in the assessed samples.
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: "The narrative toxicity objective states, ""All waters shall be maintained free of toxic substances in concentrations that produce detrimental physiological responses in human, plant, animal, or aquatic life. This objective applies regardless of whether the toxicity is caused by a single substance or the interactive effect of multiple substances."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for the TU analysis is based on the following: "The concentration of each toxic substance is divided by its toxicologic limit. The resulting ratios are added for substances having similar toxicologic effects and, separately, for carcinogens. The additive toxicity criterion has been violated if the sum of the ratios is >1 (CV Basin Plan, 2011)."
Guideline Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Spatial Representation: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
 
DECISION ID
73404
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Pyrethroids
Final Listing Decision: Do Not Delist from 303(d) list (being addressed with USEPA approved TMDL)
Last Listing Cycle's Final Listing Decision: Do Not Delist from 303(d) list (TMDL required list)(2016)
Revision Status Revised
Sources: A Source Unknown
TMDL Name: Phase 2 (Pyrethroids)Sacramento and San Joaquin Pesticides Basin Plan Amendment and TMDLs
TMDL Project Code: 872
Date TMDL Approved by USEPA: 04/22/2019
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: This pollutant is being considered for removal on the CWA section 303(d) List under sections 2.2 and 4.11 of the Listing Policy. Under 4.11 of the Policy, a minimum of one line of evidence is needed to assess listing status.

Three lines of evidence are available in the administrative record to assess this pollutant.

Based on the readily available data and information, the weight of evidence indicates that there is sufficient justification against removing this water segment-pollutant combination from the CWA section 303(d) List. There is sufficient justification to place it in the Being Addressed portion of the CWA 303(d) List because a TMDL has been completed and approved by RWQCB and USEPA, and is expected to result in attainment of the standard.

This conclusion is based on the staff findings that:
1. The data used satisfies the data quality requirements of section 6.1.4 of the Policy.
2. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy.
3. Nineteen of 20 sediment samples exceed the narrative toxicity objective and this exceeds the allowable frequency listed in Table 4.1 of the Listing Policy. Sediment-bound pyrethroid pesticide concentrations were used to calculate toxic units (TUs) of multiple pyrethroid pesticides observed in sediments. Pyrethroid TU analyses correlated with distribution and magnitude of toxicity.
4. The Central Valley Pyrethroid Pesticides TMDL and Basin Plan Amendment was approved by USEPA in 2019.
5. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should not be removed from the section 303(d) list because applicable water quality standards for the pollutant are being exceeded.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation:
 
 
Line of Evidence (LOE) for Decision ID 73404, Pyrethroids
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 30940
 
Pollutant: Sediment Toxicity
LOE Subgroup: Toxicity
Matrix: Sediment
Fraction: Total
 
Beneficial Use: Warm Freshwater Habitat
Aquatic Life 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: Five of six sediment toxicity testing samples violated the narrative toxicity objective. The five toxic (Mean mortality + standard deviation) sediment samples were collected from: Kaseberg Creek at Caragh Road 9/25/04: 100+0; Kaseberg Creek at Timberose Road 8/31/04: 16+9, 9/24/04: 15+5; Kaseberg Creek at 25 Meters North of McAnally Drive and Thunderbird Court 9/24/04: 38+18; Kaseberg Creek at Country Club Boulevard and McAnally Drive 9/24/04: 93+12. The observed toxicity was associated with pyrethroid pesticides.
Data Reference: Five reports and 1 abstract (all PDFs) for SWAMP studies in the Lower Sacramento River: "R5SWAMP04-05_1.pdf" [Weston, D.P, R.W. Holmes, J. You, and M.J. Lydy. 2005. Aquatic toxicity due to residential use of pyrethroid insecticides. Environmental Science and Technology 39 (Dec. 15): 9778-9784.] "rb5_sedimentchem_rptmain.pdf" [Holmes, R.W. 2004. Monitoring of Sediment-bound Contaminants In the Lower Sacramento River Watershed Surface Water Ambient Monitoring Program (SWAMP) Lower Sacramento River Watershed, Final Report. Regional Water Quality Control Board - Central Valley Region. July 2004.]; "Sac_River_Benthic_Rpt.pdf" [Holmes, R.W., V. de Vlaming, D. Markiewicz, and K. Goding. 2005. Benthic Macroinvertebrate Colonization on Artificial Substrates in Agriculture-dominated Waterways of the Lower Sacramento River Watershed, Surface Water Ambient Monitoring Program (SWAMP) Lower Sacramento River Watershed. Regional Water Quality Control Board-Central Valley Region and U.C. Davis Aquatic Toxicology Laboratory and School of Veterinary Medicine. June 2005.]; "Sac_River_BioReport_Final.pdf" [V. de Vlaming, D. Markiwiecz, K. Goding, T. Kimball, and R. Holmes. Macroinvertebrate Assemblages in Agriculture- and Effluent-dominated Waterways of the Lower Sacramento River Watershed. Regional Water Quality Control Board-Central Valley Region, Moss Landing Laboratories, and U.C. Davis Aquatic Toxicology Laboratory and School of Veterinary Medicine.]; "sedimentchem.pdf" [R. W. Holmes. Monitoring of Sediment-bound Contaminants In the Lower Sacramento River Watershed Surface Water Ambient Monitoring Program (SWAMP) Lower Sacramento River Watershed, Final Report. Regional Water Quality Control Board - Central Valley Region. July 2004.]; "SWAMP03-04zooplankton_1.pdf" [V. de Vlaming, K. Goding, D. Markiwiecz, R. Wallace, and R. Holmes. Survey of Zooplankton Community Structure and Abundance in Agriculture-dominated Waterways in the Lower Sacramento River Watershed. Regional Water Quality Control Board-Central Valley Region and U.C. Davis Aquatic Toxicology Laboratory and School of Veterinary Medicine. May 2006.]
 
SWAMP Data: SWAMP
 
Water Quality Objective/Criterion: All waters shall be maintained free of toxic substances in concentrations that produce detrimental physiological responses in human, plant, animal, or aquatic life. (CVRWQCB, 2007)
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: Statistically significant difference from control sediment using Dunnett's test in 10-day Hyalella azteca sediment toxicity tests. Arcsin squareroot transformation was used when necessary to meet the assumptions of normality and homogeneity of variance. Steel's test was used for comparison to control if these assumptions were not met after transformation.
Guideline Reference: Distribution and Toxicity of Sediment-Associated Pesticides in Agriculture-Dominated Water Bodies of California¿s Central Valley
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: 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: Samples were collected at Kaseberg Creek at Caragh Road, Kaseberg Creek at Timberose Road, Kaseberg Creek at 25 Meters North of McAnally Drive and Thunderbird Court, Kaseberg Creek at Country Club Boulevard and McAnally Drive, Kaseberg Creek at Open Space Area/Aquatic Center.
Temporal Representation: Samples were collected September 2004 - October 2004. Data collected during late summer.
Environmental Conditions:
QAPP Information: Data quality: Excellent.. Monitoring was conducted in accordance with the State Water Resources Control Board's Quality Assurance Program Plan for the State of California's Surface Water Ambient Monitoring Program.
QAPP Information Reference(s):
 
Line of Evidence (LOE) for Decision ID 73404, Pyrethroids
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59090
 
Pollutant: Toxicity
LOE Subgroup: Toxicity
Matrix: Sediment
Fraction: None
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 14
Number of Exceedances: 14
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: One-tenth the organic carbon normalized LC50 values for sediment-bound pyrethroids were used as toxicity thresholds in a toxicity unit (TU) analysis. Samples containing at least 2 pyrethroids with concentrations above the reporting limit were assessed for additive toxicity.14 of 14 sediment samples indicated a calculated TU > 1, suggesting that samples had pyrethroid pesticides at levels expected to exert additive, chronic toxicity. A combination of 2 or more of the pyrethroids, bifenthrin, fenpropathrin, lambda-cyhalothrin, permethrin, cyfluthrin, cypermethrin, esfenvalerate, and deltamethrin were present in the assessed samples.
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: "The narrative toxicity objective states, ""All waters shall be maintained free of toxic substances in concentrations that produce detrimental physiological responses in human, plant, animal, or aquatic life. This objective applies regardless of whether the toxicity is caused by a single substance or the interactive effect of multiple substances."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for the TU analysis is based on the following: "The concentration of each toxic substance is divided by its toxicologic limit. The resulting ratios are added for substances having similar toxicologic effects and, separately, for carcinogens. The additive toxicity criterion has been violated if the sum of the ratios is >1 (CV Basin Plan, 2011)."
Guideline Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Spatial Representation: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
Line of Evidence (LOE) for Decision ID 73404, Pyrethroids
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 22310
 
Pollutant: Pyrethroids
LOE Subgroup: Pollutant-Sediment
Matrix: Sediment
Fraction: Total
 
Beneficial Use: Warm Freshwater Habitat
Aquatic Life 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: Five of six sediment toxicity testing samples violated the narrative toxicity objective. Toxicity observations were associated with pyrethroid pesticides LC50s for sediment-bound pyrethroids were used in this study as toxicity threshold benchmarks in a Toxic Unit (TU) analysis normalized to organic carbon content. The TU analysis of Kaseberg Creek sediment samples demonstrated that the five toxic samples had pyrethroid pesticide concentrations that would be expected to be acutely toxic. The five toxic sediment samples had between 1 and 10 TUs or greater of pyrethroid pesticides. Bifenthrin appears to play a dominant role in the toxicity observations, but was not the only pyrethroid found in toxic sediment samples. Other pyrethroids observed in the toxic samples from Kaseberg Creek included cyfluthrin, cypermethrin, deltamethrin, esfenvalerate, lambda-cyhalothrin, and permethrin.
Data Reference: Five reports and 1 abstract (all PDFs) for SWAMP studies in the Lower Sacramento River: "R5SWAMP04-05_1.pdf" [Weston, D.P, R.W. Holmes, J. You, and M.J. Lydy. 2005. Aquatic toxicity due to residential use of pyrethroid insecticides. Environmental Science and Technology 39 (Dec. 15): 9778-9784.] "rb5_sedimentchem_rptmain.pdf" [Holmes, R.W. 2004. Monitoring of Sediment-bound Contaminants In the Lower Sacramento River Watershed Surface Water Ambient Monitoring Program (SWAMP) Lower Sacramento River Watershed, Final Report. Regional Water Quality Control Board - Central Valley Region. July 2004.]; "Sac_River_Benthic_Rpt.pdf" [Holmes, R.W., V. de Vlaming, D. Markiewicz, and K. Goding. 2005. Benthic Macroinvertebrate Colonization on Artificial Substrates in Agriculture-dominated Waterways of the Lower Sacramento River Watershed, Surface Water Ambient Monitoring Program (SWAMP) Lower Sacramento River Watershed. Regional Water Quality Control Board-Central Valley Region and U.C. Davis Aquatic Toxicology Laboratory and School of Veterinary Medicine. June 2005.]; "Sac_River_BioReport_Final.pdf" [V. de Vlaming, D. Markiwiecz, K. Goding, T. Kimball, and R. Holmes. Macroinvertebrate Assemblages in Agriculture- and Effluent-dominated Waterways of the Lower Sacramento River Watershed. Regional Water Quality Control Board-Central Valley Region, Moss Landing Laboratories, and U.C. Davis Aquatic Toxicology Laboratory and School of Veterinary Medicine.]; "sedimentchem.pdf" [R. W. Holmes. Monitoring of Sediment-bound Contaminants In the Lower Sacramento River Watershed Surface Water Ambient Monitoring Program (SWAMP) Lower Sacramento River Watershed, Final Report. Regional Water Quality Control Board - Central Valley Region. July 2004.]; "SWAMP03-04zooplankton_1.pdf" [V. de Vlaming, K. Goding, D. Markiwiecz, R. Wallace, and R. Holmes. Survey of Zooplankton Community Structure and Abundance in Agriculture-dominated Waterways in the Lower Sacramento River Watershed. Regional Water Quality Control Board-Central Valley Region and U.C. Davis Aquatic Toxicology Laboratory and School of Veterinary Medicine. May 2006.]
 
SWAMP Data: SWAMP
 
Water Quality Objective/Criterion: No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. (CVRWQCB, 2007)All waters shall be maintained free of toxic substances in concentrations that produce detrimental physiological responses in human, plant, animal, or aquatic life. (CVRWQCB, 2007)
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: Statistically significant difference from control sediment using Dunnett's test in 10-day Hyalella azteca sediment toxicity tests. Arcsin squareroot transformation was used when necessary to meet the assumptions of normality and homogeneity of variance. Steel's test was used for comparison to control if these assumptions were not met after transformation. LC50 values, based on 10-day exposure to Hyallela azteca of pyrethroids in sediment samples, were used to determine Toxic Unit (TUs) for pyrethroids in sediments. Urban creek sediment sample pyrethroid concentrations were compared the TUs to determine exceedances.
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: 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: Distribution and Toxicity of Sediment-Associated Pesticides in Agriculture-Dominated Water Bodies of California¿s Central Valley
 
Spatial Representation: Samples were collected at Kaseberg Creek at Caragh Road, Kaseberg Creek at Timberose Road, Kaseberg Creek at 25 Meters North of McAnally Drive and Thunderbird Court, Kaseberg Creek at Country Club Boulevard and McAnally Drive, Kaseberg Creek at Open Space Area/Aquatic Center.
Temporal Representation: Samples were collected September 2004 - October 2004. Data collected during late summer.
Environmental Conditions:
QAPP Information: Data quality: Excellent.. Monitoring was conducted in accordance with the State Water Resources Control Board's Quality Assurance Program Plan for the State of California's Surface Water Ambient Monitoring Program.
QAPP Information Reference(s):
 
 
DECISION ID
72691
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Toxicity
Final Listing Decision: Do Not Delist from 303(d) list (TMDL required list)
Last Listing Cycle's Final Listing Decision: Do Not Delist from 303(d) list (TMDL required list)(2016)
Revision Status Original
Sources: A Source Unknown
Expected TMDL Completion Date: 2021
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: This pollutant is being considered for removal from the CWA section 303(d) List under section 4.1 of the Listing Policy. Under this section a single line of evidence is necessary to assess listing status.

Two lines of evidence are available in the administrative record to assess pollutant. Nineteen of 20 sediment samples exceed the objective.

Based on the readily available data and information, the weight of evidence indicates that there is sufficient justification against removing this water segment-pollutant combination from the CWA section 303(d) List.

This conclusion is based on the staff findings that:
1. The data used satisfies the data quality requirements of section 6.1.4 of the Policy.
2. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy.
3. Nineteen of 20 samples exceed the objective and this exceeds the allowable frequency listed in Table 4.1 of the Listing Policy.
4. Pursuant to section 4.11 of the Listing Policy, no additional data and information are available indicating that standards are met.
 
Regional Board Decision Recommendation: After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should not be removed from the section 303(d) list because applicable water quality standards for the pollutant are being exceeded.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation: After review of this Regional Board decision, SWRCB staff recommend the decision be approved by the State Board.
 
 
Line of Evidence (LOE) for Decision ID 72691, Toxicity
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59090
 
Pollutant: Toxicity
LOE Subgroup: Toxicity
Matrix: Sediment
Fraction: None
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 14
Number of Exceedances: 14
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: One-tenth the organic carbon normalized LC50 values for sediment-bound pyrethroids were used as toxicity thresholds in a toxicity unit (TU) analysis. Samples containing at least 2 pyrethroids with concentrations above the reporting limit were assessed for additive toxicity.14 of 14 sediment samples indicated a calculated TU > 1, suggesting that samples had pyrethroid pesticides at levels expected to exert additive, chronic toxicity. A combination of 2 or more of the pyrethroids, bifenthrin, fenpropathrin, lambda-cyhalothrin, permethrin, cyfluthrin, cypermethrin, esfenvalerate, and deltamethrin were present in the assessed samples.
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: "The narrative toxicity objective states, ""All waters shall be maintained free of toxic substances in concentrations that produce detrimental physiological responses in human, plant, animal, or aquatic life. This objective applies regardless of whether the toxicity is caused by a single substance or the interactive effect of multiple substances."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for the TU analysis is based on the following: "The concentration of each toxic substance is divided by its toxicologic limit. The resulting ratios are added for substances having similar toxicologic effects and, separately, for carcinogens. The additive toxicity criterion has been violated if the sum of the ratios is >1 (CV Basin Plan, 2011)."
Guideline Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Spatial Representation: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
Line of Evidence (LOE) for Decision ID 72691, Toxicity
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 30940
 
Pollutant: Sediment Toxicity
LOE Subgroup: Toxicity
Matrix: Sediment
Fraction: Total
 
Beneficial Use: Warm Freshwater Habitat
Aquatic Life 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: Five of six sediment toxicity testing samples violated the narrative toxicity objective. The five toxic (Mean mortality + standard deviation) sediment samples were collected from: Kaseberg Creek at Caragh Road 9/25/04: 100+0; Kaseberg Creek at Timberose Road 8/31/04: 16+9, 9/24/04: 15+5; Kaseberg Creek at 25 Meters North of McAnally Drive and Thunderbird Court 9/24/04: 38+18; Kaseberg Creek at Country Club Boulevard and McAnally Drive 9/24/04: 93+12. The observed toxicity was associated with pyrethroid pesticides.
Data Reference: Five reports and 1 abstract (all PDFs) for SWAMP studies in the Lower Sacramento River: "R5SWAMP04-05_1.pdf" [Weston, D.P, R.W. Holmes, J. You, and M.J. Lydy. 2005. Aquatic toxicity due to residential use of pyrethroid insecticides. Environmental Science and Technology 39 (Dec. 15): 9778-9784.] "rb5_sedimentchem_rptmain.pdf" [Holmes, R.W. 2004. Monitoring of Sediment-bound Contaminants In the Lower Sacramento River Watershed Surface Water Ambient Monitoring Program (SWAMP) Lower Sacramento River Watershed, Final Report. Regional Water Quality Control Board - Central Valley Region. July 2004.]; "Sac_River_Benthic_Rpt.pdf" [Holmes, R.W., V. de Vlaming, D. Markiewicz, and K. Goding. 2005. Benthic Macroinvertebrate Colonization on Artificial Substrates in Agriculture-dominated Waterways of the Lower Sacramento River Watershed, Surface Water Ambient Monitoring Program (SWAMP) Lower Sacramento River Watershed. Regional Water Quality Control Board-Central Valley Region and U.C. Davis Aquatic Toxicology Laboratory and School of Veterinary Medicine. June 2005.]; "Sac_River_BioReport_Final.pdf" [V. de Vlaming, D. Markiwiecz, K. Goding, T. Kimball, and R. Holmes. Macroinvertebrate Assemblages in Agriculture- and Effluent-dominated Waterways of the Lower Sacramento River Watershed. Regional Water Quality Control Board-Central Valley Region, Moss Landing Laboratories, and U.C. Davis Aquatic Toxicology Laboratory and School of Veterinary Medicine.]; "sedimentchem.pdf" [R. W. Holmes. Monitoring of Sediment-bound Contaminants In the Lower Sacramento River Watershed Surface Water Ambient Monitoring Program (SWAMP) Lower Sacramento River Watershed, Final Report. Regional Water Quality Control Board - Central Valley Region. July 2004.]; "SWAMP03-04zooplankton_1.pdf" [V. de Vlaming, K. Goding, D. Markiwiecz, R. Wallace, and R. Holmes. Survey of Zooplankton Community Structure and Abundance in Agriculture-dominated Waterways in the Lower Sacramento River Watershed. Regional Water Quality Control Board-Central Valley Region and U.C. Davis Aquatic Toxicology Laboratory and School of Veterinary Medicine. May 2006.]
 
SWAMP Data: SWAMP
 
Water Quality Objective/Criterion: All waters shall be maintained free of toxic substances in concentrations that produce detrimental physiological responses in human, plant, animal, or aquatic life. (CVRWQCB, 2007)
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: Statistically significant difference from control sediment using Dunnett's test in 10-day Hyalella azteca sediment toxicity tests. Arcsin squareroot transformation was used when necessary to meet the assumptions of normality and homogeneity of variance. Steel's test was used for comparison to control if these assumptions were not met after transformation.
Guideline Reference: Distribution and Toxicity of Sediment-Associated Pesticides in Agriculture-Dominated Water Bodies of California¿s Central Valley
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: 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: Samples were collected at Kaseberg Creek at Caragh Road, Kaseberg Creek at Timberose Road, Kaseberg Creek at 25 Meters North of McAnally Drive and Thunderbird Court, Kaseberg Creek at Country Club Boulevard and McAnally Drive, Kaseberg Creek at Open Space Area/Aquatic Center.
Temporal Representation: Samples were collected September 2004 - October 2004. Data collected during late summer.
Environmental Conditions:
QAPP Information: Data quality: Excellent.. Monitoring was conducted in accordance with the State Water Resources Control Board's Quality Assurance Program Plan for the State of California's Surface Water Ambient Monitoring Program.
QAPP Information Reference(s):
 
 
DECISION ID
93067
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Benthic Community Effects
Final Listing Decision: Do Not List on 303(d) list (TMDL required list)
Last Listing Cycle's Final Listing Decision: Do Not List on 303(d) list (TMDL required list)(2016)
Revision Status Original
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: Benthic Community Effects is being considered for placement on the CWA section 303(d) List under sections 3.9 of the Listing Policy. Under section 3.9, an additional line of evidence associating the Benthic Community Effects with a water or sediment concentration of pollutants is necessary to assess listing status. One line of evidence is available in the administrative record to assess this indicator. Zero of the zero samples exceed the Evaluation Guideline.

Based on the readily available data and information, the weight of evidence indicates that there is sufficient justification against placing Benthic Community Effects in this water segment on the CWA section 303(d) List.

This conclusion is based on the staff findings that:
1. The data used satisfies the data quality requirements of section 6.1.4 of the Policy.
2. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy.
3. Zero of zero samples exceeded the Index of Biological Integrity (IBI) value of poor water quality for this area and this sample size is insufficient to determine with the power and confidence of the Listing Policy if standards are not met. A minimum of 2 samples is needed to determine impairment using Table 3.1.
4. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should not be placed on the section 303(d) list. The readily available data and information is insufficient to determine, with the power and confidence of the Listing Policy, the applicable beneficial use support rating.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation: After review of this Regional Board decision, SWRCB staff recommend the decision be approved by the State Board.
 
 
Line of Evidence (LOE) for Decision ID 93067, Benthic Community Effects
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59099
 
Pollutant: Benthic-Macroinvertebrate Bioassessments
LOE Subgroup: Population/Community Degradation
Matrix: Water
Fraction: None
 
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: Four sites were sampled in 2006, 2007, and 2008; 1 additional site was sampled in 2008 for a total of 13 individual IBI scores. Out of a possible IBI score of 100, sample scores ranged from 4 to 21.
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: The narrative toxicity objective states, "All waters shall be maintained free of toxic substances in concentrations that produce detrimental physiological responses in human, plant, animal, or aquatic life."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: Based on the lack of reference sites for the Central Valley floor, the Central Valley IBI is not adequate to determine impairment thresholds at this time.
Guideline Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Spatial Representation: BMI samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 BMI samples were collected from 05/16/2006 to 05/19/2006; the 2007 BMI samples were collected on 05/09/2007 and 05/10/2007; the 2008 BMI samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
 
DECISION ID
70322
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Esfenvalerate/Fenvalerate
Final Listing Decision: Do Not List on 303(d) list (TMDL required list)
Last Listing Cycle's Final Listing Decision: Do Not List on 303(d) list (TMDL required list)(2016)
Revision Status Original
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: This pollutant is being considered for placement on the CWA section 303(d) List under section 3.1 of the Listing Policy. Under section 3.1 a single line(s) of evidence are necessary to assess listing status.

One line of evidence is available in the administrative record to assess this pollutant. Zero of 14 samples exceed the guideline.

Based on the readily available data and information, the weight of evidence indicates that there is sufficient justification against placing this water segment-pollutant combination on the CWA section 303(d) List.

This conclusion is based on the staff findings that:
1. The data used satisfies the data quality requirements of section 6.1.4 of the Policy.
2. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy.
3. Zero of 14 samples exceed the guideline and this sample size is insufficient to determine, with the power and confidence of the Listing Policy, the applicable beneficial use support rating. A minimum of 16 samples is needed to determine if a beneficial use is fully supported using table 3.1.
4. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should not be placed on the section 303(d) list. The readily available data and information is insufficient to determine, with the power and confidence of the Listing Policy, the applicable beneficial use support rating.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation: After review of this Regional Board decision, SWRCB staff recommend the decision be approved by the State Board.
 
 
Line of Evidence (LOE) for Decision ID 70322, Esfenvalerate/Fenvalerate
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59072
 
Pollutant: Esfenvalerate/Fenvalerate
LOE Subgroup: Pollutant-Sediment
Matrix: Sediment
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: A total of 14 individual sediment samples were collected; 0 of 14 exceeded the evaluation guideline (0.15 ug/g OC).
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: The narrative objective for pesticides states, "No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. Discharges shall not result in pesticide concentrations in bottom sediments or aquatic life that adversely affect beneficial uses."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for esfenvalerate/fenvalerate, 0.15 ug/g OC, is one-tenth of the median lethal concentration for H. azteca (LC50; 1.5 ug/g OC). The LC50 (1.5 ug/g OC) is the geometric mean of OC normalized 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: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
 
DECISION ID
85852
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Fenpropathrin
Final Listing Decision: Do Not List on 303(d) list (TMDL required list)
Last Listing Cycle's Final Listing Decision: Do Not List on 303(d) list (TMDL required list)(2016)
Revision Status Original
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: This pollutant is being considered for placement on the CWA section 303(d) List under section 3.1 of the Listing Policy. Under section 3.1 a single line(s) of evidence are necessary to assess listing status.

One line of evidence is available in the administrative record to assess this pollutant. Zero of 14 samples exceed the guideline.

Based on the readily available data and information, the weight of evidence indicates that there is sufficient justification against placing this water segment-pollutant combination on the CWA section 303(d) List.

This conclusion is based on the staff findings that:
1. The data used satisfies the data quality requirements of section 6.1.4 of the Policy.
2. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy.
3. Zero of 14 samples exceed the guideline and this sample size is insufficient to determine, with the power and confidence of the Listing Policy, the applicable beneficial use support rating. A minimum of 16 samples is needed to determine if a beneficial use is fully supported using table 3.1.
4. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should not be placed on the section 303(d) list. The readily available data and information is insufficient to determine, with the power and confidence of the Listing Policy, the applicable beneficial use support rating.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation: After review of this Regional Board decision, SWRCB staff recommend the decision be approved by the State Board.
 
 
Line of Evidence (LOE) for Decision ID 85852, Fenpropathrin
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59027
 
Pollutant: Fenpropathrin
LOE Subgroup: Pollutant-Sediment
Matrix: Sediment
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: A total of 14 individual sediment samples were collected; 0 of 14 exceeded the evaluation guideline (0.1 ug/g OC).
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: The narrative objective for pesticides states, "No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. Discharges shall not result in pesticide concentrations in bottom sediments or aquatic life that adversely affect beneficial uses."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for fenpropathrin, 0.1 ug/g OC, is one-tenth of the median lethal concentration for H. azteca (LC50; 1 ug/g OC). The LC50 (1 ug/g OC) is the geometric mean of OC normalized 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: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
 
DECISION ID
85854
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Permethrin, total
Final Listing Decision: Do Not List on 303(d) list (TMDL required list)
Last Listing Cycle's Final Listing Decision: Do Not List on 303(d) list (TMDL required list)(2016)
Revision Status Original
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: This pollutant is being considered for placement on the CWA section 303(d) List under section 3.1 of the Listing Policy. Under section 3.1 a single line(s) of evidence are necessary to assess listing status.

One line of evidence is available in the administrative record to assess this pollutant. One of 12 samples exceed the guideline.

Based on the readily available data and information, the weight of evidence indicates that there is sufficient justification against placing this water segment-pollutant combination on the CWA section 303(d) List.

This conclusion is based on the staff findings that:
1. The data used satisfies the data quality requirements of section 6.1.4 of the Policy.
2. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy.
3. One of 12 samples exceed the guideline and this sample size is insufficient to determine, with the power and confidence of the Listing Policy, the applicable beneficial use support rating. A minimum of 16 samples is needed to determine if a beneficial use is fully supported using table 3.1.
4. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should not be placed on the section 303(d) list. The readily available data and information is insufficient to determine, with the power and confidence of the Listing Policy, the applicable beneficial use support rating.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation: After review of this Regional Board decision, SWRCB staff recommend the decision be approved by the State Board.
 
 
Line of Evidence (LOE) for Decision ID 85854, Permethrin, total
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59045
 
Pollutant: Permethrin, total
LOE Subgroup: Pollutant-Sediment
Matrix: Sediment
Fraction: Total
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 12
Number of Exceedances: 1
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: A total of 14 individual sediment samples were collected; 2 samples were below both the reporting limit (1.0 ug/kg dry weight) and the organic carbon normalized evaluation guideline (0.89 ug/g OC) and could not be quantified with the level of certainty required by the listing policy. 1 of 12 samples exceeded the evaluation guideline.
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: The narrative objective for pesticides states, "No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. Discharges shall not result in pesticide concentrations in bottom sediments or aquatic life that adversely affect beneficial uses."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for permethrin, 0.89 ug/g OC, is one-tenth of the median lethal concentration for H. azteca (LC50; 8.9 ug/g OC). The LC50 (8.9 ug/g OC) is the geometric mean of OC normalized LC50 values for permethrin 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: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
 
DECISION ID
75135
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Specific Conductivity
Final Listing Decision: Do Not List on 303(d) list (TMDL required list)
Last Listing Cycle's Final Listing Decision: Do Not List on 303(d) list (TMDL required list)(2016)
Revision Status Original
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: The decision has not changed. Region 5 data was not included in the 2012 Integrated Report so all decisions are carried over from the 2010 listing cycle.

This pollutant is being considered for listing under sections 3.2 of the Listing Policy. Under section 3.2 a single line of evidence is necessary to assess listing status. Data is available from 1 line of evidence for this pollutant. Based on the readily available data and information, the weight of evidence indicates that there is not sufficient justification for placing this water segment-pollution combination on the section 303(d) list. The recommendation is based on staff findings that 0 of 7 available concentrations exceeded the water quality objective and this does not exceed the allowable frequency using Table 3.2 of the Listing Policy. Table 3.2 of the listing policy recommends listing if a sample size of 7 has 5 or more samples that exceed the evaluation criteria.

The data used satisfies the data quality requirements of section 6.1.4 of the Policy. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: The decision has not changed. Region 5 data was not included in the 2012 Integrated Report so all decisions are carried over from the 2010 listing cycle.

After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should not be placed on the section 303(d) list because applicable water quality standards are not being exceeded.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation: After review of this Regional Board decision, SWRCB staff recommend the decision be approved by the State Board.
 
 
Line of Evidence (LOE) for Decision ID 75135, Specific Conductivity
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 21096
 
Pollutant: Specific Conductivity
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: None of the 7 samples collected by the Surface Water Ambient Monitoring Program exceeded the "recommended" Secondary MCL of 900 uS/cm for electrical conductivity
Data Reference: SWAMP data entered by SWRCB into BDAT database
 
SWAMP Data: SWAMP
 
Water Quality Objective/Criterion: The secondary MCLs for electrical conductivity provide a range of values including a recommended level (900 uS/cm), upper level (1600 uS/cm) and a short-term level (2200 uS/cm). The ¿recommended¿ level of 900 uS/cm was used as it is intended to be protective of all drinking water uses
Objective/Criterion Reference: California Code of Regulations, Title 22, Division 4, Chapter 15. Domestic Water Quality and Monitoring
 
Evaluation Guideline:
Guideline Reference:
 
Spatial Representation: Samples were collected from Kaseberg Creek at McAnally/Thunderbird Court, at Caragh Road, at Country Club Boulevard/McAnally, at confluence w/ SOT, at Green Grove Road, at Pleasant Grove Boulevard, and at Timberose Road
Temporal Representation: The samples were collected between September 24, 2004 and September 25, 2004
Environmental Conditions:
QAPP Information: Monitoring was conducted in accordance with the State Water Resources Control Board's Quality Assurance Program Plan for the State of California's Surface Water Ambient Monitoring Program.
QAPP Information Reference(s):
 
 
DECISION ID
68721
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: pH
Final Listing Decision: Do Not List on 303(d) list (TMDL required list)
Last Listing Cycle's Final Listing Decision: Do Not List on 303(d) list (TMDL required list)(2016)
Revision Status Original
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: This pollutant is being considered for listing under sections 3.2 of the Listing Policy. Under section 3.2 a single line of evidence is necessary to assess listing status. Data is available from 1 line of evidence for this pollutant. Based on the readily available data and information, the weight of evidence indicates that there is not sufficient justification for placing this water segment-pollution combination on the section 303(d) list. The recommendation is based on staff findings that 0 of 7 available concentrations exceeded the water quality objective and this does not exceed the allowable frequency using Table 3.2 of the Listing Policy. Table 3.2 of the listing policy recommends listing if a sample size of 7 has 5 or more samples that exceed the evaluation criteria.

The data used satisfies the data quality requirements of section 6.1.4 of the Policy. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: This is a decision previously approved by the State Water Resources Control Board and the USEPA. No new data were assessed by the Regional Board for the current cycle. The decision has not changed.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation: After review of this Regional Board decision, SWRCB staff recommend the decision be approved by the State Board.
 
 
Line of Evidence (LOE) for Decision ID 68721, pH
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 8815
 
Pollutant: pH
LOE Subgroup: Pollutant-Water
Matrix: Water
Fraction: None
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 7
Number of Exceedances: 0
 
Data and Information Type: Not Specified
Data Used to Assess Water Quality: Zero of the 7 samples collected by the Surface Water Ambient Monitoring Program exceeded the evaluation objective for pH.
Data Reference: SWAMP data entered by SWRCB into BDAT database
 
SWAMP Data: SWAMP
 
Water Quality Objective/Criterion: pH levels should not be lower than 6.5 or higher than 8.5 (Basin Plan Objective)
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline:
Guideline Reference:
 
Spatial Representation: Samples were collected at Kaseberg Ck (McAnally/Thunderbird Ct). Samples were collected at Kaseberg Ck @ Caragh Rd. Samples were collected at Kaseberg CK @ Cntry Club Blvd/McAnally. Samples were collected at Kaseberg CK @ confluence w/ SOT. Samples were collected at Kaseberg Ck @ Green Grove Rd. Samples were collected at Kaseberg Ck @ Pleasant Grove Blvd.. Samples were collected at Kaseberg Ck @ Timberose Rd.
Temporal Representation: The samples were collected from Sep 24 2004 to Sep 25 2004
Environmental Conditions:
QAPP Information: Monitoring was conducted in accordance with the State Water Resources Control Board's Quality Assurance Program Plan for the State of California's Surface Water Ambient Monitoring Program.
QAPP Information Reference(s):
 
 
DECISION ID
94107
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
Pollutant: Deltamethrin
Final Listing Decision: List on 303(d) list (TMDL required list)
Last Listing Cycle's Final Listing Decision: List on 303(d) list (TMDL required list)(2016)
Revision Status Original
Sources: A Source Unknown
Expected TMDL Completion Date: 2027
Impairment from Pollutant or Pollution: Pollutant
 
Regional Board Conclusion: This pollutant is being considered for placement on the CWA section 303(d) List under section 3.6 of the Listing Policy. Under section 3.6 at least two lines of evidence are necessary to assess listing status for pollutants sediment, and pollutant concentrations in sediment must be associated with sediment toxicity to justify adding that pollutant to the CWA section 303(d) List.

Two lines of evidence are available in the administrative record to assess this pollutant. Seven of the 14 samples exceed the evaluation guideline for COLD, and 14 of 14 samples exhibited sediment toxicity. Based on the readily available data and information, the weight of evidence indicates that there is sufficient justification for placing this water segment-pollutant combination on the CWA section 303(d) List.
This conclusion is based on the staff findings that:
1. The data used satisfies the data quality requirements of section 6.1.4 of the Policy.
2. The data used satisfies the data quantity requirements of section 6.1.5 of the Policy.
3. Seven of the 14 samples exceed the evaluation guideline for COLD and this sample size is sufficient to determine beneficial use support, with the power and confidence of the Listing Policy. There is an associated sediment toxicity data as required by Section 3.6 of the Listing Policy.
4. Pursuant to section 3.11 of the Listing Policy, no additional data and information are available indicating that standards are not met.
 
Regional Board Decision Recommendation: After review of the available data and information, RWQCB staff concludes that the water body-pollutant combination should be placed on the section 303(d) list because applicable water quality standards are exceeded and a pollutant contributes to or causes the problem.
 
State Board Review of Regional Board Conclusion and Recommendation:
 
State Board Decision Recommendation:
 
 
Line of Evidence (LOE) for Decision ID 94107, Deltamethrin
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59090
 
Pollutant: Toxicity
LOE Subgroup: Toxicity
Matrix: Sediment
Fraction: None
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 14
Number of Exceedances: 14
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: One-tenth the organic carbon normalized LC50 values for sediment-bound pyrethroids were used as toxicity thresholds in a toxicity unit (TU) analysis. Samples containing at least 2 pyrethroids with concentrations above the reporting limit were assessed for additive toxicity.14 of 14 sediment samples indicated a calculated TU > 1, suggesting that samples had pyrethroid pesticides at levels expected to exert additive, chronic toxicity. A combination of 2 or more of the pyrethroids, bifenthrin, fenpropathrin, lambda-cyhalothrin, permethrin, cyfluthrin, cypermethrin, esfenvalerate, and deltamethrin were present in the assessed samples.
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: "The narrative toxicity objective states, ""All waters shall be maintained free of toxic substances in concentrations that produce detrimental physiological responses in human, plant, animal, or aquatic life. This objective applies regardless of whether the toxicity is caused by a single substance or the interactive effect of multiple substances."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for the TU analysis is based on the following: "The concentration of each toxic substance is divided by its toxicologic limit. The resulting ratios are added for substances having similar toxicologic effects and, separately, for carcinogens. The additive toxicity criterion has been violated if the sum of the ratios is >1 (CV Basin Plan, 2011)."
Guideline Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Spatial Representation: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.
 
Line of Evidence (LOE) for Decision ID 94107, Deltamethrin
Region 5     
Kaseberg Creek (tributary to Pleasant Grove Creek, Placer County)
 
LOE ID: 59081
 
Pollutant: Deltamethrin
LOE Subgroup: Pollutant-Sediment
Matrix: Sediment
Fraction: Total
 
Beneficial Use: Cold Freshwater Habitat
 
Number of Samples: 14
Number of Exceedances: 7
 
Data and Information Type: PHYSICAL/CHEMICAL MONITORING
Data Used to Assess Water Quality: A total of 14 individual sediment samples were collected; 7 of 14 samples exceeded the evaluation guideline (0.079 ug/g OC).
Data Reference: Various Data for Pleasant Grove Creek, Del Puerto Creek and Roseville Area, 2006-2010.
 
SWAMP Data:
 
Water Quality Objective/Criterion: The narrative objective for pesticides states, "No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. Discharges shall not result in pesticide concentrations in bottom sediments or aquatic life that adversely affect beneficial uses."
Objective/Criterion Reference: Water Quality Control Plan for the California Regional Water Quality Control Board Central Valley Region, Sacramento and San Joaquin River Basins. 4th ed
 
Evaluation Guideline: The evaluation guideline for deltamethrin, 0.079 ug/g OC, is one-tenth of the median lethal concentration for H. azteca (LC50; 0.79 ug/g OC). The LC50 (0.79 ug/g OC) is the geometric mean of OC normalized 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: Sediment samples were collected along Kaseberg Creek at the following station locations in 2006, 2007 and 2008: PGC 10, PGC 12, PGC 14, and PGC 15. Two additional sites (PGC 11a and PGC 16a) were also sampled in 2008.
Temporal Representation: The 2006 sediment samples were collected from 05/16/2006 to 05/19/2006; the 2007 sediment samples were collected on 05/09/2007 and 05/10/2007; the 2008 sediment samples were collected from 05/02/2008 to 05/06/2008.
Environmental Conditions:
QAPP Information: Submitted QA data are acceptable.
QAPP Information Reference(s): Quality Assurance Project Plan for Pyrethroid Working Group.