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February 14 1997 <br /> Page 8 <br /> �- 4000 lbs Figures 6 through 8 depict these conditions and show soil analytical data from <br /> soil borings and wells drilled after the operation of the SVE system <br /> The location of the residual hydrocarbons in soils al e characterized by soil borings <br /> located 1n two areas These include Soil Borings SB-2 and SB-12 located in the north- <br /> ern portion of the UST complex and Borings SB-3 and SB-13 located adjacent to the <br /> western product island Hydrocarbons in these two areas are well defined and appear to <br /> be isolated based on data collected from several borings as shown on the geologic cross- <br /> In <br /> sections (Figures 7 and 8) <br /> The composition of the residual hydrocarbons in soils is dominated by the presence of <br /> the relatively high molecular weight compounds TPPH-g concentrations range from <br /> less than 10 to 10,000 ppm Benzene with few exceptions has not been detected, and <br /> based on toxicity characteristic leaching procedure (TCLP) results is not leachable <br /> (Table 3) Benzene is the most water soluble natural hydrocarbon constituent of <br /> petroleum is a known carcinogen, and is the primary constituent of concern for cleanup <br /> of petroleum discharges in California The remaining elevated concentrations of TPPH-g <br /> tend to reside in relatively tight soils consisting of sandy to clayey silt, or silty sandy clay <br /> RESIDUAL PETROLEUM HYDROCARBONS IN GROUNDWATER <br /> 1 - <br /> Quarterly groundwater monitoring was initiated in November 1988 Dissolved hydro- <br /> carbon concentrations in groundwater samples collected from Well MW-4, located in the <br /> source area, have generaIIy decreased with the overall increase in groundwater elevation <br /> This trend indicates that SVE was effective in remediating hydrocarbon-affected soils in <br /> the source area Furthermore, during 1996, groundwater elevations in site monitoring <br /> wells have risen allowing collection of groundwater samples from wells which were <br /> previously dry (Wells MW-1; and MW-3 through MW-8) Fourth quarter groundwater <br /> monitoring (October 24, 1996, Attachment D) indicates the maximum residual <br /> concentration of TPPH-g and benzene in groundwater to be 560 ppb and 4 8 ppb <br /> respectively, (Well MW-13) Wells MW-4 MW-6 and MW-9 are the only other wells to <br /> report detectable concentrations of petroleum hydrocarbons The wells are located <br /> within and to the east of the former UST complex and product island areas Therefore, <br /> minor petroleum hydrocarbons exist in groundwater locally in the vicinity of the north- <br /> eastern corner of the former UST complex and east of the former product island The <br /> lateral extent of petroleum hydrocarbons in groundwater has been delineated to non- <br /> detectable concentrations with the exception of laterally to the east as evidenced by <br /> fluctuating concentrations of petroleum hydrocarbons in Well MW-13 "Stable or <br /> decreasing plumes often display short-term variability in ground-water concentrations <br /> This behavior should not be construed as evidence of an unstable plume, but may be the <br /> natural variations of a stable plume in the environment " (Supplemental Instructions to <br /> 3201337B1CLOSLTRE3 <br />