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Soil and Groundwater Investigation Report and <br /> Second Quarter 2005 Monitoring and Sampling,US Can-Welty Road October 2005 <br /> 10.4 QUALITY ASSURANCE/QUALITY CONTROL <br /> All field procedures were conducted in accordance with SAIC's Quality Assurance and Quality Control <br /> Sample Collection, Handling, and Analysis procedures. No sample was received by the laboratory <br /> outside of acceptable temperature or pH limits. In addition to routine laboratory quality control(QC) <br /> analyses, a trip blank(QA-T)and equipment rinsate(QA-RB)were submitted to the laboratory with <br /> samples WFSMW-1 and MW-5. In accordance with SAIC's standard procedures,the trip blank was <br /> analyzed. No BTEX were detected in the trip blank. <br /> The laboratory control sample(LCS) and laboratory control sample duplicate(LCSD) appear to be within <br /> the LCS/LCSD limits. The matrix spike(MS) and matrix spike duplicate(MSD) also are within the <br /> MS/MSD limits and the relative percent difference criteria was within the acceptable range for either the <br /> LCS/LCSD or MS/MSD samples except for PAH compound(benzo[a]pyrene). The laboratory analytical <br /> report noted this PAH compound as "outside of specification." While not all of the laboratory QC <br /> parameters were within specification range,the information provided by these analytical results is <br /> considered useable. Laboratory QA/QC data from this sampling event are considered acceptable and the <br /> sample analytical data are considered valid. <br /> 11. DISCUSSION <br /> Based on the analytical results,the lateral extent of petroleum-affected soil at US Can—Welty Road <br /> appears to be delineated northwest to northeast of borings GMX-10 through GMX 12 by soil borings <br /> SB-13, SB-14, SB-15 and former borings GMX-6 and GMX-7. However,petroleum-affected soil does <br /> not appear to be delineated southeast of GMX-11, adjacent to the former OVP pipeline ROW. Affected <br /> soil in this area was encountered in boring SB-17,but not unexpected since it is adjacent to the former <br /> pipeline ROW and borders the former Vernalis Pump Station. <br /> Affected groundwater has been delineated by groundwater samples collected from wells WFSMW-1 and <br /> MW-5. Well MW-5 did not contain detectable concentrations of petroleum hydrocarbons and the <br /> groundwater sample from well WFSMW-1 did not contain detectable TPHg,BTEX, or MTBE. <br /> However,the groundwater sample collected from well WFSMW-1 contained TPHd at a concentration of <br /> 71 µg/L,below the water quality objective(WQO) of 100 gg/L. Although grab groundwater samples <br /> collected from soil borings SB-13 and SB-14 contained detectable TPHd at concentrations of 450 and 200 <br /> gg/L,respectively,these samples should be considered lesser quality and expected to be an order of <br /> magnitude higher in concentration than detected in the groundwater monitoring wells. Detectable <br /> concentrations of TPHg,BTEX, or MTBE were not detected in these grab groundwater samples. <br /> The grab groundwater sample collected from SB-17 contained 480 pg/L of TPHg, 150,000 gg/L of TPHd <br /> and 0.6 gg/L of benzene. The detection of dissolved-phase TPHg is likely an overlap of the diesel range <br /> organics based on the elevated concentration of dissolved TPHd detected. However,the presence of <br /> benzene in the grab groundwater sample from SB-17 could indicate a refined fuel plume is emanating <br /> from the former Union Oil Service Station, located north(cross gradient)of boring location SB-17. <br /> 12. SUMMARY/CONCLUSIONS <br /> The data collected during this and former subsurface investigations indicate that residual petroleum has <br /> mainly affected soil between 5 and 42 feet bgs in the vicinity of SB-17,MW-1, SB-1, SB-2, SB-3,B-1, <br /> B-4 through B-7(MW-2), GMX-3, GMX-8, GMX-1B,and GMX-12. In SB-17 lean clay and sandy <br /> layers below 37 feet bgs appear to be the most affected soil areas. In general,the depth of affected areas <br /> varies through the site. The lateral extent of petroleum-affected soil appears to be delineated towards the <br /> south,west,north,northeast, and east. However,the lateral extent of petroleum-affected soil southeast of <br /> the subject site has not been fully characterized adjacent to the former OVP ROW,which borders the <br /> 9 From Science to Solutions- <br />