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n <br /> SITE BACKGROUND <br /> CANEPA'S CAR WASH, PARK STREET <br /> The Site is located in the downtown business district of Stockton, California One 12,000-gallon unleaded <br /> gasoline underground storage tank (UST), one 5,000-gallon leaded gasoline UST, and one 5,000-gallon <br /> diesel fuel UST were removed from the Site in 1990 According to WHF Environmental Consultants, Inc <br /> (WHF), soil samples collected from the UST excavation from approximately 16 feet below the ground <br /> surface (bgs) contained elevated concentrations of gasoline and gasoline constituents Between September <br /> 1993 and March 1994, WHF installed six soil borings and seven monitor wells at and around the Site <br /> Three of the monitor wells (MW-1, MW-2, and MW-3) were constructed with a screened interval from 45 <br /> to 65 feet bgs Monitor wells MW-4 through MW-7 were constructed with a screened interval from 40 to <br /> 60 feet bgs <br /> Beginning in April 1997, Condor implemented a quarterly groundwater monitoring program at the Site <br /> Following the July 1998 quarterly groundwater monitoring event, Mr Ron Rowe, formerly with San <br /> Joaquin County Environmental Health Department (SJCEHD) requested the installation of additional <br /> monitor wells The tops of the screened intervals of monitor wells MW-1 through MW-7 were submerged <br /> below the groundwater table during the period under study Condor prepared a work plan dated <br /> November 17, 1998, for the installation of four additional monitor wells (MW-8 through MW-11) In a <br /> letter dated September 7, 2001, however, Mr Jeffrey Wong of the SJCEHD requested that an additional <br /> work plan be submitted by October 20, 2001 to define the lateral and vertical extent of groundwater <br /> contamination and the vertical extent of soil contamination at the Site Mr Wong also requested submittal <br /> of a Sensitive Receptor Survey Report for a 2,000-foot radius around the Site by November 10, 2001 In <br /> response to Mr Wong's request, Condor submitted the Work Plan for Additional Soil and Groundwater <br /> Investigation, dated October 17, 2001 The work plan described several proposed direct push borings <br /> intended to investigate the lateral and vertical extent of contamination and assist in the siting of additional <br /> monitor wells in a subsequent phase of work, if necessary Mr Wong subsequently approved the work <br /> plan, with modifications, in a letter dated October 29, 2001 <br /> Site investigation activities pursuant to the above described work plan were performed from March 25 <br /> through March 28, 2002, details of the investigation are presented in Condor's Additional Soil and <br /> Groundwater Investigation Report, dated May 8, 2002 Investigation activities included the installation of <br /> two Cone Penetrometer test (CPT) borings, one soil boring, and twenty-one direct push (hydropunch) <br /> borings Laboratory analytical results of the soil samples indicated that relatively elevated concentrations <br /> of gasoline constituents were present down to the deepest sample collected (approximately 82 feet bgs) <br /> However, the lowest concentrations of gasoline constituents were detected in the sample collected at 82 <br /> feet bgs, indicating the potential for some attenuation of concentrations at that depth Methyl tertiary- <br /> butyl ether (MTBE) was not detected at or above the laboratory reported detection limit in any of the soil <br /> samples In addition, laboratory analytical results from the groundwater sample collected proximal to the <br /> soil samples indicated that the gasoline was partitioning into the groundwater phase with some difficulty, <br /> probably as a result of the relatively fine-grained soil texture <br /> The laboratory analytical results of the hydropunch groundwater samples indicated that relatively elevated <br /> concentrations of gasoline constituents were present at depths below the water table both proximal <br /> (CPT I) to and down-gradient (CPT2) from the location of the former USTs The results associated with <br /> CPT1 indicated an increasing trend of contaminant concentration with depth with benzene concentrations <br /> ranging from 65 µg/L at 79 to 83 feet bgs, to 1,900 ptg/ in the deepest sample collected at 119 to 123 feet <br /> bgs As opposed to CPT I, the results associated with CPT2 indicated a trend of decreasing groundwater <br />