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GEOMATFI1X <br /> field water quality parameters were monitored and the clarity of the water was observed. Groundwater <br /> samples were collected in laboratory-prepared containers, sealed, labeled, and placed immediately in an <br /> ' ice-cooled chest for subsequent delivery to the laboratory using chain-of-custody procedures. <br /> ' 5.0 LABORATORY ANALYSIS <br /> Soil samples collected from the confirmation soil boring (SB6) were analyzed for BTEX using EPA <br /> ' Method 8020, TPH-G using a modified version of EPA Method 8015, and TPH-D also using a modified <br /> version of Method 8015, in accordance with the work plan. The TPH-D analysis was performed using <br /> standard procedures and also with a silica gel cleanup performed prior to analysis. The laboratory <br /> quantified the results of the Method 8015 analyses against a diesel standard as requested and reported <br /> the presence of hydrocarbons in the TPH-D range in this sample; however, the laboratory indicated that <br /> ' the chromatographic signature of the material present in the soil samples showed a non-typical diesel <br /> pattern. Laboratory services were provided by American Environmental Network (AEN) of Pleasant <br /> Hill, California. AEN is certified by the State of California to perform hazardous waste analyses. <br /> Analytical data sheets provided by the laboratory are included in Appendix C. <br /> ' In order to evaluate the type of petroleum hydrocarbons present in soil beneath the site, a soil sample <br /> collected during the additional characterization from boring SBS at a depth of 25 feet was submitted to a <br /> laboratory for fingerprint characterization by capillary gas chromatography. This sample had the <br /> greatest indication (based on field evidence, such as odor, discoloration, and OVM results) of the <br /> presence of petroleum hydrocarbons of the samples collected from that boring. Fingerprint characteri- <br /> zation was performed by Friedman & Bruya, Inc. (FBI) of Seattle, Washington. FBI is certified by the <br /> State of California to perform these analyses. Results of the fingerprint characterization indicate that the <br /> ' petroleum hydrocarbons in soil beneath the site are gasoline and not diesel. The sample was then <br /> analyzed for BTEX using EPA Method 8020 and for TPH-G using a modified version of EPA Method <br /> ' 8015. Analytical data sheets provided by the laboratory are included in Appendix C. <br /> Based on the results of fingerprint characterization, the remaining soil samples collected at the site <br /> ' submitted for laboratory analysis were also analyzed for BTEX using EPA Method 8020 and TPH-G <br /> using a modified version of EPA Method 8015. Laboratory services were provided by AEN. Analytical <br /> data sheets provided by the laboratory are included in Appendix C. <br /> In order to be consistent with, and confirm, the results of the groundwater monitoring performed by <br /> Geomatrix- in-May-,1995;=which=indicated-that diesel-was-not- present-in-groundwater, groundwater— --=--- <br /> samples collected on 17 November 1995 were analyzed for BTEX using EPA Method 8020 and TPH-G <br /> and TPH-D using modified versions of EPA Method 8015. To reduce the likelihood of false positives <br /> for TPH-D, groundwater samples were analyzed for TPH-D as follows: a standard sample with no <br /> preparation, a sample filtered using a 0.45 micron filter, and a sample filtered and treated with a silica <br /> 5 <br />