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Soil and Groundwater Investigation Report <br /> Mountain House Development Site#6 July 2008 <br /> • Total Dissolved Solids(TDS)using EPA Method 160.1; sulfate, chloride,nitrate (as nitrogen), <br /> and nitrite(as nitrogen)using EPA 300.0; specific conductance using EPA 120.1; Kjeldahl <br /> nitrogen using EPA 351.2;total phosphorus using EPA 365.1; ammonia(as nitrogen)using <br /> 350.2; alkalinity(as CaCO3),bicarbonate (as CaCO3), carbonate(as CaCO3), and hardness(as <br /> CaCO3)using SM 20 2320B;boron, sodium, calcium, iron,magnesium, manganese, and <br /> potassium using SW846 6010B. <br /> Refer to Appendix D for more information regarding the field, sampling, and analytical methods <br /> employed during the field investigation. <br /> 3.3 QUALITY ASSURANCE/QUALITY CONTROL AND DATA USABILITY <br /> Field sampling was conducted in accordance with SAIC's Quality Assurance and Quality Control Sample <br /> Collection, Handling, and Analysis procedures (SAIL, 2007a). In accordance with those procedures, <br /> quality assurance samples were also collected and analyzed. SAIC performed a data usability evaluation <br /> after receipt of all final laboratory reports to determine whether the data can be used for the intended <br /> purposes. The evaluation is summarized in the Data Usability Summary found in Appendix E. <br /> 3.4 INVESTIGATION-DERIVED WASTE(IDW) <br /> To properly store, characterize,and dispose of IDW, SAIC conducted the following: <br /> • Placed all IDW(soil cuttings and unused soil sample, disposable sampling equipment,used <br /> personal protective equipment, and decontamination water) in U.S. Department of <br /> Transportation(DOT) approved 55-gallon drums; <br /> • Properly labeled, secured, and stored IDW-containing drums on site pending disposal by <br /> Sturgeon& Son, Inc.; and <br /> • Collected composite IDW samples and submitted them to Lancaster for profiling. IDW was <br /> segregated, sampled, analyzed, and disposed of consistent with Chevron's Operational <br /> Excellence Process document entitled HPP-BTR Waste Management Process(Chevron, <br /> 2006). <br /> 4. FINDINGS <br /> 4.1 DWR FILE REVIEW <br /> SAIC conducted a search of DWR files to identify water supply wells within a 2,000-foot radius of the <br /> site. The search covered portions of Township 2-South,Range 4-East, and Sections 2, 3, 10, and 11. <br /> A total of seven wells were identified: five wells are located northwest of the site; and two wells are <br /> located southeast of the site. Two of the wells located northwest(approximately 1,500 feet cross <br /> gradient)were sampled during the recent investigation at Mountain House Development Site#3. <br /> Analytical results of the groundwater samples collected from the two wells were below laboratory <br /> reporting limits. <br /> A summary of the water well search results is provided in Table 1. Approximate locations of the water <br /> wells are shown on Figure 1. This figure also shows the presence of various aqueducts, surface irrigation <br /> canals, and other waterways within a 1-mile radius from the site. <br /> 4.2 SUBSURFACE CONDITIONS <br /> Soil encountered in the borings consisted predominantly of mixtures of clay, silt, and sand. Boring logs, <br /> which describe USCS soil characteristics,PID readings, and observations of residual crude oil in soil <br /> and/or in groundwater, are provided in Appendix C. Groundwater was encountered at depths ranging <br /> from 4.9 to 12 feet bgs. <br /> 5 <br /> From Science to Solutions <br />