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• Mr. Ron Rowe <br /> February 24, 1999 <br /> Page 4 of 6 <br /> grained soil with silt and clay from approximately 66 to 75 feet bgs, the_maximum depth <br /> explored Groundwater was encountered at a depth of approximately 5 et_bgj Soil boring <br /> locations are shown on Figure 3 Soil boring logs are included in Attachment B <br /> Confirmation Sampling <br /> Interpretations of soil type were confirmed through traditional soil logging techniques using <br /> ASTM protocol Soil samples were collected from three borings (SBI, SB2, and SB3) at <br /> significant changes in lithology, based upon the CPT data collected from the pilot borings <br /> Borings SBI and SB2 were advanced in the vicinity of the former USTs and boring SB3 was <br /> advanced in the vicinity of the former dispenser island Samples were collected in SBI at 20 feet <br /> bgs, from SB2 at 25, 30 5, 39, 54, 65, and 72 2 feet bgs, and from SB3 at 16, 26, and 40 feet bgs <br /> No samples were collected deeper than 40 feet bgs from SB3 due to the absence of field <br /> evidence of contamination in shallow samples Samples were collected into brass tubes and each <br /> sample was screened for the presence of petroleum hydrocarbons using a flame ionization <br /> detector (FID) FID readings were recorded on soil boring logs Samples were immediately <br /> placed in a cooled ice chest <br /> Ag roundwater sample was collected from bona SB ` t 2 an approximate depth of 65 feet using a <br /> • Hydropunch sampling tool The sample was collected into pre-cooled 40 mL vials with <br /> hydrochloric acid preservative and placed in a cooled ice chest A laboratory representative <br /> transported soil and water samples under chain of custody to BSK Laboratory in Fresno, CA <br /> (FLAP #1180) <br /> All downhole drilling and sampling equipment was decontaminated by steam cleaning and/or <br /> washing with laboratory-grade detergent Decontamination water was placed into properly <br /> labeled 55 gallon drums and stored on site pending disposal No soil cuttings were generated <br /> during the sampling process <br /> LABORATORY ANALYSIS <br /> Soil samples collected from borings SBI, SB2, and S133 were analyzed for TPHg, BTEX, and <br /> gasoline oxygenate fuel additives utilizing EPA methods 8015, 8020 modified, and 8260 modified, <br /> respectively No TPHg or BTEX were detected in the sample collected from SBI at 20 feet bgs, <br /> from the sample collected from SB2 at 30 5 feet bgs, or from any sample collected from boring <br /> SB3 Petroleum hydrocarbon constituents were detected at relatively low levels in samples <br /> collected from SB2 between 30 5 and 72 2 feet bgs Benzene ranged from 0 0060 parts per <br /> million (ppm) (SB2-30 5' and SB2-65') to 0 33 ppm (SB2-72 2'), and TPHG ranged from <1 0 <br /> ppm (SB2-30 5') to 33 ppm (SB2-72 2') Methyl tert-butyl ether (MTBE) was detected in each <br /> soil sample (ranging from 0 22 ppm to 2 5 ppm) with the exception of the sample collected at <br /> 72 2 feet bgs from S132 Tert-butyl alcohol (TBA) was detected in each soil sample (ranging <br /> from 0 28 ppm to 1 8 ppm) with the exception of the samples collected from S133 at 16 feet bgs <br /> groundzeltuleburonitrpt doc <br />