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1 <br /> CONFIRMATION SOIL SAMPLING REPORT <br /> VINTAGE CAR WASH, INC <br /> PACIFIC AVENUE CAR WASH <br /> STOCKTON, CALIFORNIA <br />' 1.0 INTRODUCTION <br /> On October 10, October 29 and November 4, 1991, TreaTek Inc (TreaTek) conducted confirmation <br /> soil sampling of the fuel distribution network area soils at the Pacific Avenue Car Wash site located <br />' at the intersection of Pacific Avenue and Bianchi Road in Stockton, California (Figure 1) The <br /> purpose of this sampling was to determine whether petroleum hydrocarbon compounds associated <br /> with the fuel distribution network were present within the vadose zone sods The following sections <br />' provide a discussion of the field sampling activities conducted at the site as well as a description <br /> of the soil conditions encountered during sampling and a discussion of the sample analytical <br /> results The final section of this report provides conclusions and recommendations for the site <br /> based on the observed site conditions and the analytical and field data <br /> 2.0 FIELD SAMPLING ACTIVITIES <br />' On October 10, 1991, TreaTek initiated subsurface sampling activities at the Pacific Avenue Car <br /> Wash site The initial activities involved the coring through both the concrete and asphalt covering <br /> the area above the fuel distribution network Nine holes were cored The location of these nine <br />' holes and the subsequent TreaTek location identification numbers are shown on Figure 2 <br /> The first location sampled was location RGN1 This location is situated approximately four feet north <br /> of the west end of the regular leaded gasoline storage tank A four inch diameter stainless steel <br /> hand auger was used to advance the borehole to a depth of five feet beneath the ground surface <br /> (bgs) At the five foot depth, a sample collection tube driver lined with a clean two inch diameter, <br /> 1 six inch long, stainless steel tube, was used to collect a soil sample for field screening The field <br /> screening method utilized an organic vapor analyzer (OVA) Once field screened, the sample was <br /> sealed with aluminum foil and plastic end caps and secured with elastic tape The sample was then <br /> labeled and stored on ice The borehole was then advanced to ten feet bgs, at which another <br /> sample was collected, screened and stored The borehole was finally advanced to the maximum <br /> depth of 15 feet bgs At the 15 foot depth, another soil sample was collected and screened Since <br /> no sample from the borehole exhibited detectable OVA readings, the 15 foot sample from location <br /> RGN1 was sealed, labeled and stored on ice for laboratory analysis The other soil samples from <br /> this borehole were discarded The OVA field screening results for the samples from this and the <br /> other boreholes are presented on Table 1 <br />' Following the collection of sample RGN1, the auger and tube driver were thoroughly decontaminated <br /> utilizing a potable water/laboratory reagent soap mixture wash followed by a potable water rinse and <br /> a deionized water final rinse This process was repeated between each borehole location sampled <br /> T ne next location sampled was location RGN2 This location is north of the east end of the regular <br /> gasoline storage tank Field screening samples were collected at depths of five feet and 9 feet bgs <br /> At the nine foot depth, the hand auger could not be advanced further due to a below grade <br /> obstruction None of the samples collected from this location were analyzed <br /> The final location sampled on October 10, 1991 was location RGS1 Only a five foot depth field <br /> screening sample was collected before field activities were halted <br />