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1 <br /> ranging from approximately 13 to 41 feet bgs Groundwater has risen approximately 25 feet <br /> over time at the site, from -30 55 feet (40 70 feet bgs) in October 1992 to -5 24 feet (12 72 feet <br />' bgs in June 2001 This general rise in groundwater over time is graphically presented on the <br /> hydrograph for MW 10 (Appendix C), which presents well construction details and groundwater <br /> elevations over time Data for the groundwater elevation during the period from 1970 to 1986 <br />' was inferred from several groundwater monitoring stations in the Stockton area (Figure 7) <br /> During this time period, groundwater elevations varied from 0 feet in the early 1970s to <br /> approximately-20 feet in 1978, and back to 0 feet in the mid-1980s <br /> 1 <br /> The historical onsite groundwater elevation high and low points are also presented on the <br />' geologic cross-sections (Figures 5a-5d), as are the analytical results for soil samples collected <br /> during past hydrogeologic investigations As presented on these cross-sections, petroleum <br /> hydrocarbons occur in soil at the site between approximately 20 and 46 feet bgs Currently the <br /> groundwater is at approximately 19 feet bgs, which means that these petroleum hydrocarbons <br /> entrapped in soil at the site are submerged This issue, coupled with soil types encountered at the <br /> site, will be discussed in greater detail in other sections of this report as it relates to past and <br />' future remedial efforts at the site <br /> 2.4 DISTRIBUTION OF HYDROCARBONS IN SOIL <br />' A majority of the lateral and vertical extent of hydrocarbons detected in soil samples are beneath <br /> and immediately downgradient (northeast) of the former USTs and former pump islands This <br /> lie area is graphically depicted in Figure 8 The location, depth, and analytical results of all soil <br /> samples collected during this investigation are also presented in Figure 8, and appended in <br /> Appendix B This area identified in Figure 8 approximates the area of soils containing <br />' hydrocarbons at residual saturation, or areas in which hydrocarbons are entrapped in pore space <br /> within the soil matrix The relationship between the historically highest and lowest groundwater <br /> elevations and the Iocation and concentration of hydrocarbons detected in soil samples are also <br />' presented on the hydrogeologic cross-sections (Figures 5a-5d) <br /> The highest concentrations of TPH-g were detected in soil samples collected from beneath the <br />' former tank field in well V4, at depths ranging from 20 to 40 feet bgs at concentrations ranging <br /> from 2,100 to 12,000 mg/kg Approximately 200 feet northeast of and downgradient of V4, <br /> TPH-g was detected at a concentration of 130 mg/kg in a soil sample collected at 40 feet bgs in <br />' RW4 Soil samples collected at 30 feet bgs from wells IW 1 and P2, installed upgradient of the <br /> former tank field and in the general vicinity of former dispenser islands, contained 530 and 210 <br /> mg/kg TPH-g, respectively <br />' It is assumed that the hydrocarbon mass remaining in the current vadose zone (0-20 feet bgs), is <br /> negligible relative to hydrocarbon mass below groundwater because of previous excavation <br />' efforts to 20 feet bgs during UST removal (Appendix B), soil vapor extraction (SVE) conducted <br /> at the site between 1994 and 1996, and natural processes <br />' Monitoring well MW8 was installed west of and upgradient of the ExxonMobil site across North <br /> • Pershing Avenue This location is downgradient of the Shell service station, approximately 25 <br />' G 1Projmts%739421MASTERIWPIWP03031WPtx dm 4 <br />