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' and groundwater analytical data is contained in Interim Status Report, Phase 11 Investigation,by WW <br /> . Based on the initial data, the vertical and lateral limits of contamination were not sufficiently defined <br />' <br /> WW- proposed the installation of four (4) additional monitor wells (MW-5 through MW-8) to fully <br /> characterize the groundwater plume The PHS/EHD granted approval of the additional investigation on <br /> January 19, 1994 Between March 9 and 11, 1994, WJ-W� installed MW-5 through MW-8 Moderate <br />' concentrations of gasoline were detected in the soil from MW-6 at 50 and 55 feet bgs and from MW-7 at 50 <br /> feet bgs Low to elevated concentrations of TPH-G and BTEX were detected in groundwater samples <br /> collected from MW-6, MW-7, and MW-8 A summary of the soil and groundwater analytical data is <br />' contained in Phase II Site Characterization, by WHF The wells were surveyed and gradient calculations <br /> indicated that a groundwater mound existed beneath the site indicating that recharge or leakage into the <br /> groundwater in the vicinity of MW-1 and MW-2 was occurring Three potential souicas of lucharge were <br />' identified 1) the car wash water recycling pit system under the building, 2) a leaking or broken Sewer line <br /> that crosses the area, and 3) a leaking water supply line An MBAS (Methyl Blue Active Surfactants) test <br /> was conducted on groundwater samples collected at the site in July, 1994, to investigate the presence of <br /> detergents MBAS was not detected in the samples <br /> Aquifer testing (24-hour pump test) was conducted at the site by WHF on December 22 and 23, 1994 <br /> MW-1 was used as a pumping well, and MW-4,MW-6,MW-7, and MW-8 were used as observation wells <br /> The results indicated an optimum pumping rate of 5 gpm with an effective radius of 140 feet Aquifer <br /> permeability was estimated at 126 gpd/ft2 <br /> Quarterly groundwater monitoring was conducted at the site by WHF from March 1994 through June, 1995 <br /> Historical groundwater analytical data indicated elevated concentrations of TPH-G and BTEX in MW-1, <br /> MW-2, MW-6, and MW-7 Low to trace concentrations of TPI-1-6 and BTEX were detected in MW-3, <br /> MW-4, MW-5 and MW-8 Condor has been conducting quarterly groundwater monitoring at the site since <br /> August 1996 Analysis of groundwater samples collected from selected SVE wells (SVE-1, 2, 3, 5, 7, 8, <br /> and 9) indicate that high concentrations of TPH-G, BTEX, and MTBE are present in the former location of <br />' the fuel dispenser islands The groundwater table has risen approximately 15 feet since quarterly <br /> monitoring of all eight site monitor wells began in March I994 <br /> A site investigation was conducted by Condor Earth Technologies, Inc (Condor) on July 31, 1996, at the <br /> Canepa's Car Wash facility The investigation included a review of existing investigative reports and an <br /> evaluation of the existing SVE system located at the site The fieldwork was conducted in accordance with <br /> Condor's proposal for SVE evaluation,dated Api 11 8, 1996, and the addendum to the proposal, dated May 2, <br /> 1996 The report was titled Soil Vapor Extraction (SVE)System Evaluation,and dated September 23, 1996 <br /> Condor calculated that, based on the soil analytical data available for the site, the volume of hydrocarbons <br /> present in the soil beneath the site is estimated at approximately 13,000 pounds or 2,050-gallons (6 34 <br /> lbs/gal) Due to unknown variations in the lithology and contaminant concentrations, the actual volume of <br /> hydrocarbon beneath the site may vary by an order of magnitude or more from the estimate <br />■ Based on the results of the SVE system evaluation and site background, Condor recommended that <br /> operation of the ICU be suspended since the system did not appear to meet APCD permit conditions (i e, <br /> I 95%destruction efficiency) Condor further recommended that a 150 SCFM catalytic oxidation unit(CAT- <br /> OX) be installed at the site to extract and treat the gasoline contamination in the vadose zone It was <br /> determined that the configuration of the existing SVE wells appeared to be sufficient to remove a majority <br /> of the remaining gasoline contaminants in the vadose zone <br /> 2 <br /> I <br />