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Monitoring Well Destruction and Soil and Groundwater Investigation Report <br /> US Can—Welty Road December 28,2010 <br /> west(up gradient)of Areas 1 and 2 has been delineated by borings SB-44 and SB-45, <br /> respectively. The down-gradient(northeastern) extent of affected groundwater can be inferred <br /> based on borings from the current investigation(SB-47) and previous investigations(SB-35 and <br /> SB-42). Maps depicting concentrations of COPCs in soil and groundwater samples collected <br /> from the previous investigation are included as Appendix G. <br /> The area of affected groundwater northeast of SB-46 (CPS property)has been defined to the <br /> extent practicable. Additional delineation to the northeast is not possible due to property-access <br /> issues. A previously existing access agreement was cancelled by CPS in 2009. <br /> The areas of affected groundwater northwest of the US Can property boundary (borings SB-38 <br /> through SB-41 and SB-43)will be investigated separately as part of the Ahern Road—Vernalis <br /> site. SAIC-Benham submitted a work plan for Ahern Road—Vernalis on August 26, 2010 <br /> (SAIC-Benham, 2010), and it was accepted in a September 2010 letter from the Central Valley <br /> RWQCB (Central Valley RWQCB, 2010b). <br /> The extent of crude-oil affected soil and groundwater depicted on Figure 3 was derived from <br /> SAIC-Benham's evaluation of the data collected during this and previous investigations. <br /> 5.1.1 Suitability of the Groundwater for Drinking <br /> SAIC-Benham submitted one grab groundwater sample (SB-44) for TDS and General Minerals <br /> analysis. The TDS concentration was 1,280 milligrams per liter(mg/L),which exceeds the <br /> following current CDPH MCLS and Central Valley RWQCB Water Quality Goals(WQG; <br /> Central Valley RWQCB, 2000) for drinking water: <br /> • CDPH MCL: 500 mg/L,recommended; 1,000 mg/L,upper; 1,500 mg/L, short term. <br /> • Central Valley RWQCB WQG, CDPH, and EPA drinking water standards: 500 mg/L. <br /> • Central Valley RWQCB WQG, Agricultural Water Quality Goal: 450 mg/L. <br /> • Central Valley RWQCB WQG,EPA Ambient Water Quality Criteria for Taste and Odor <br /> or Welfare: 250 mg/L. <br /> The results of the General Minerals analyses indicated boron, chloride,manganese, nitrate as <br /> nitrogen, sodium, and sulfate in concentrations in excess of their respective WQOs; the chloride <br /> and manganese concentrations also exceeded their respective MCLS. The sample exceeded the <br /> WQO levels for adverse taste and odor for boron, chloride, manganese, sodium, and sulfate. The <br /> groundwater is thus considered to contain certain taste-or odor-producing substances in <br /> concentrations that cause nuisance or adversely affect beneficial uses (California Code of <br /> Regulations, Title 22). These exceedances indicate that the uppermost water-bearing zone is not <br /> suitable for drinking-water use. Groundwater analytical results for General Minerals are <br /> provided in Table 5. <br /> 5.2 CALIFORNIA DEPARTMENT OF WATER RESOURCES FILE REVIEW <br /> On November 1, 2010, SAIC-Benham conducted a search of the DWR files to identify water- <br /> supply wells within a 2,000-foot radius of the site. The search covered portions of Township <br /> 3-South, Range 6-East, Sections 26, 27, 34, and 35, and portions of Township 4-South,Range <br /> 6-East, Sections 2 and 3. A total of nine water-supply wells were identified within the search <br /> area. A summary of the water well search results is provided in Table 6. Locations of the water <br /> wells are shown on Figure 1. <br /> 5 Benham Congmk,LLC <br /> �����` AWh.11y Owned S.bsidiary <br />