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1 <br /> GEOMATP;X <br /> . µg/1 in the aliquot that was filtered prior to extraction and analysis. These collective results indicate <br /> ' that much of the original TPHd quantification(620µg/1)is due to polar biogenic byproducts resulting <br /> from intrinsic bioremediation and non-dissolved constituents adhered to particulates in these samples. <br /> ' Grab groundwater analytical results are summarized in Table 2 and are presented on Figure 2. The <br /> analytical laboratory report for the soil and grab groundwater samples is presented in Appendix C. <br /> 6.0 CONCLUSIONS <br /> ' Based on the results of this and previous investigations, Geomatrix has developed the following <br /> conclusions about site conditions. <br /> ' One area of petroleum hydrocarbon affected soil has been identified at the site. Based on <br /> review of chromatograms and the results of a forensic evaluation(Geomatrix,2000),the <br /> petroleum hydrocarbons are likely degraded crude oil. The affected soil has been <br /> encountered at depths ranging between 5.5 and 14 feet bgs. The lateral extent of affected <br /> soil has been delineated. <br /> • Groundwater quality downgradient of the affected soil is characterized by grab <br /> groundwater samples from borings GMX-23 and GMX-24. TPHg,BTEX, and PAHs <br /> were not detected in these samples. Constituents quantified as TPHd(without a silica gel <br /> preparation procedure)were not detected in the sample from GMX-23 and were detected <br /> at 86 µg/1 in the sample from GMX-24;this concentration is below the diesel taste and <br /> odor criteria that is used as a water quality objective(WQO)by the Regional Water <br /> Quality Control Board—Central Valley Region(RWQCB). It should be noted that <br /> TPHd detections following a silica gel preparation procedure were due to laboratory <br /> contamination. <br /> ' Groundwater within the area of affected soil is characterized by grab groundwater <br /> samples from borings GMX-12 and GMX-28. TPHg,benzene,ethylbenzene and MTBE <br /> ' were not detected in these samples. Toluene and xylenes were detected at concentrations <br /> well below their respective WQOs(e.g.,the drinking water maximum contaminant levels <br /> are 150 and 1750µg/1,respectively). Very low concentrations(less than 1 µg/1)of three <br /> PAHs(fluorene,phenanthrene and acenaphthene)were detected. Constituents quantified <br /> as TPHd(without a silica gel preparation procedure)were detected at a concentration of <br /> 620µg/1,which is above the diesel taste and odor criteria that is used as a WQO by <br /> RWQCB (100µg/1). Results from sample aliquots that were filtered prior to extraction <br /> and analysis(3 80µg/1)and treated with a silica gel preparation procedure(100µg/1) <br /> indicate that much of the original"TPHd"quantification is due to non-dissolved <br /> constituents adhered to particulates in the sample and soluble polar biogenic byproducts <br /> resulting from intrinsic bioremediation of residual petroleum hydrocarbons in soil. <br /> ' A human health screening evaluation was previously performed by Geomatrix <br /> • (Geomatrix,2000)based on the methodology presented in the PEA. In the evaluation, <br /> the maximum detected concentration for each constituent detected in soil and <br /> \\SF3\DEPTDATA\DOC_SAFE\6000S\6115.007\DEC2000REPORT\BURNS SO[LGW RPTN0V00_1.D0C 6 <br />