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Chevron Environmental Management Company Soil and Groundwater Investigation Report <br /> Tracy Byron Road Project <br /> 6.5 WATER SUPPLY WELLS <br /> SAIL and RWQCB collected split grab groundwater samples on October 23 and 30, 2003, from the water <br /> supply wells identified at several rural properties along West Byron Road. SAIC's laboratory results did <br /> not indicate concentrations of petroleum hydrocarbons at or above the laboratory detection limits in any <br /> of the tested samples. <br /> A split sample collected by the RWQCB from a water supply well located at 3190 West Byron Road <br /> contained TPHd at a concentration of 58 µg/L. The laboratory indicated that the sample chromatogram <br /> pattern exhibited atypical weathered hydrocarbon pattern. (The sample collected by SAIC did not contain <br /> TPHd.) The RWQCB also submitted the water supply well samples for analysis of TDS. Each sample <br /> contained concentrations of TDS above the recommended secondary MCL range of 500 mg/L California <br /> Department of Health Services Drinking Water Source Assessment and Protection Program Section 7 <br /> (CA DHS DWSAP Section 7). <br /> SAIC reviewed Water Well Driller Reports from the water supply wells located within the TBRP <br /> investigation area. SAIC identified a total of 37 water supply wells within the 2,000-foot search area. <br /> Based on the DWR file search, 29 of the 37 water supply wells identified were listed as domestic wells, <br /> three were listed as irrigation wells, and two were listed as unknown. <br /> Of the 29 domestic wells listed,three wells were listed as abandoned. Several domestic wells identified <br /> are adjacent to Byron Road and are pumping water from a depth considerably deeper than known <br /> impacted soil. Based on well driller reports reviewed,the domestic wells identified were constructed with <br /> sanitary seals 50 feet or greater, and appear to be separated from known affected-soil intervals. Water <br /> supply well samples collected by SAIC did not contain concentrations of petroleum constituents at or <br /> above the laboratory detection limits. <br /> 6.6 CROSS SECTIONS AND WEST BYRON ROAD BISECTS <br /> SAIC prepared four cross sections and four bisects to better illustrate the soil and groundwater conditions <br /> encountered during recent subsurface investigations. Cross-sections A-B,B-C, C-D, and D-E illustrate <br /> the subsurface conditions along the West Byron Road corridor, from Interstate 205 to the west,to Corral <br /> Hollow Road to the east(Appendix F, Insert 1). Each of these cross sections is approximately 1,600 to <br /> 1,700 feet long and all four present summarized data for approximately 6,600 feet of the West Byron <br /> Road corridor. All cross sections present the combined data collected from dewatering well installation <br /> (Geomatrix and Viking Drillers boring logs), trench excavation observations(Summary Report Tracy <br /> Westside Channel Outfall Project [WSCO], SAIC, 2003) and soil boring log data from SB-1 through <br /> SB-36 (SAIC). <br /> Explored subsurface depths for these wells and borings varied from 20 to 50 feet bgs with the majority <br /> extending from the 20-to 30-feet bgs range. SAIC grouped the soils into two main categories exhibiting <br /> similar characteristics that included fine-grained soils (clays, silts, and their mixtures), and coarse-grained <br /> soils (sands, gravels, and their mixtures). These features included particle or grain size,porosity, and <br /> permeability of the soil. <br /> The four bisects illustrate simplified and generalized subsurface conditions across the sewer line <br /> installation trench(Appendix G; Bisects A through D). Bisect A shows main features and dimensions of <br /> the utility corridor along West Byron Road,bisect B illustrates conditions with contamination present on <br /> the south side of West Byron Road, bisect C illustrates conditions on the north side of West Byron Road, <br /> and bisect D illustrates the combined northern and southern conditions along West Byron Road. <br /> 7. SUMMARY/CONCLUSIONS <br /> The data collected during former and current subsurface investigations indicate that residual petroleum <br /> has affected soil from various depths bgs to approximately 30 feet bgs, and that the majority of the <br /> affected soil is located between 4 and 20 feet bgs. Upper clay and silt layers appear to be the most <br /> 11 <br />