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1IS <br /> • petroleum hydrocarbon concentration in the influent stream reached an asymptotic condition <br /> The SVE system utilized SVE wells that were screened from 14 to 44 feet bgs Figures 4, 5, <br /> and 6 depict soil conditions beneath the site prior to operation of the SVE system (November <br /> 1990 -November 1992) Cu,-rent site conditions are discussed below <br /> Currently, residual hydrocarbons in soils occur below the northeast corner of the former UST <br /> cluster (installed in 1984) and adjacent product island These hydrocarbon affected soils <br /> occur in what can be described as two localized vertical soil columns Hydrocarbon affected <br /> soils in these two vertical soil columns occur from a depth of approximately 15 feet to 50 feet, <br /> bgs The horizontal extent of hydrocarbon affected soils within these soil columns occur <br /> primarily within a range of 5 to 10 feet, with occasional thin zones that extend horizontally an <br /> additional 10 feet from the soil column These soil columns occur within vadose zone soils, <br /> soils within the capillary fringe and zone of groundwater fluctuation, and currently saturated <br /> soils Figures 7, 8, and 9 depict these conditions and show soil analytical data from soil <br /> borings and wells drilled after the operation of the SVE system A further discussion of the <br /> occurrence of these hydrocarbons are discussed below <br /> The location of the residual hydrocarbons in soils are characterized by soil borings located in <br /> two areas These include soil Borings SB-2 and SB-12 located in the northern portion of the <br /> UST complex and Borings SB-3 and SB-13 located adjacent to the western product island <br /> • Hydrocarbons in these two areas are well defined and appear to be isolated based on data <br /> collected from several borings as shown on the geologic cross-sections(Figures 8 and 9) <br /> The concentration of the residual hydrocarbons in soils are characterized by the presence of <br /> the relatively high molecular weight compounds as discussed above TPH g concentrations <br /> range in concentration from less than 10 ppm to 10,000 ppm Benzene with few exceptions <br /> has not been detected <br /> Residual hydrocarbons as dissolved hydrocarbons are primarily affected by (1)hydrocarbon- <br /> affected vadose-zone soils typical of source areas, (2)residual hydrocarbons left in soil by <br /> groundwater fluctuation, (3) operation of the SVE system, and (4) intrinsic remediation <br /> (mechanisms including biodegradation, chemical oxidation, and adsorption/absorption) <br /> Dissolved hydrocarbon concentrations in groundwater samples collected from Well MW-9, <br /> located in the source area, have generally decreased with the overall increase in groundwater <br /> elevation This trend indicates that SVE was effective in remediating hydrocarbon-affected <br /> soils in the source area Dissolved hydrocarbons were not detected in groundwater samples <br /> collected from Well MW-9 during the second quarter 1995 <br /> Groundwater samples collected from Well MW-13, during the second quarter 1995, contained <br /> TPH-g and benzene at concentrations of 1,500 and 6 5 parts per billion (ppb), respectively <br /> The hydrocarbon concentration in groundwater samples collected from this well may be the <br /> 3201337B/1918REV 4 August 31, 1995 <br />