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MW2. Benzene (0.020), toluene (0 022 ppm), ethylbenzene (0 0050 ppm) and xylenes (0.027 <br /> ppm) were detected in soils from SBI Benzene (0.010 ppm) was detected in the soils collected <br /> tfrom SB2, and xylenes (0.026 ppm) were detected in soils collected from SB8. Chromium (41 <br /> ppm), lead (8.4 ppm) and zinc (67 ppm) were detected in the soils collected from the soil boring <br /> ' drilled near the waste oil tank pit (SB11). No other petroleum hydrocarbon analytes were <br /> detected above method reporting limits (Table 1) <br /> 5.2 Groundwater <br /> Prior to development, purging and sampling, depth to water data was collected (Table 2). <br /> Subsequently a groundwater gradient map was created (Figure 4). The gradient magnitude is <br /> ' 0.006 ft/ft or 30 ft/mile in a northeasterly direction This gradient direction and magnitude is <br /> consistent with other Tracy area sites. Groundwater monitoring and purging data is presented <br /> ' in Appendix III <br /> lot The wells were purged and developed by pumping, with a bladder pump, a minimum of 3 well <br /> and casing volumes from each well Groundwater samples were collected after EC, pH and <br /> temperature had stabilized. Groundwater samples were analyzed for BTEX, TPHG and TPHD <br /> by EPA methods 8020 and modified 8015, respectively <br /> Moderate to high levels of dissolved petroleum hydrocarbon analytes were detected in wells <br /> ' MW I and MW2 (Table 3) No analytes were present in MW3. Detection limits were increased <br /> during sample analysis in samples collected from MW1 and MW2 due to the high levels of <br /> ' constituents in the samples <br /> 6.0 CONCLUSIONS <br /> ' 6.1 Soil impact <br /> Laboratory analysis of soil samples indicates that the extent of petroleum hydrocarbon <br /> contamination in the soil has been defined The lateral extent is confined to a narrow zone <br /> beneath the former product lines, beneath the former waste oil tank (TP2), and around the <br /> l <br /> R-012792 LF 6 <br />