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• <br /> Significant levels of impact have been detected beneath the former USTs to at least 50 feet bgs, <br /> and this impacted soil has been submerged by rising groundwater levels. <br /> Extent of Petroleum Hydrocarbon Impact in Groundwater <br /> Anecdotal reports indicate that groundwater in the site vicinity was as deep as 110 feet bgs in <br /> 1979. Groundwater beneath the site has risen from approximately 68 to 44 feet bgs since <br /> initiation of the groundwater monitoring program. Gasoline from the USTs appears to have <br /> impacted vadose zone (unsaturated) soil to depths as deep as 66 feet bgs. A subsequent rise in <br /> groundwater elevation then submerged hydrocarbon-impacted soil. <br /> Former Apache Plastics FacilitX <br /> Groundwater Grab Samples: TPHG and BTEX were detected in the HydropunchTM groundwater <br /> samples collected between 62 and 120 feet bgs from borings CPT-1 and B-1/MW-9 at <br /> concentrations that generally decrease with depth. TPHG and BTEX were detected at 152 feet <br /> bgs at boring CPT-8. The vertical extent of petroleum hydrocarbon impact to groundwater was <br /> not completely characterized. The distribution of COCs at various depths based on the <br /> HydropunchTM data are shown on Figures 6 through 10. <br /> TPHG or benzene were not detected in any of the HydropunchTM groundwater samples collected <br /> above 86 feet bgs at any of the CPT borings advanced outside of the former UST complex area. <br /> The highest concentration of benzene (23,000 µg11) in groundwater was detected at 88 feet bgs at <br /> boring CPT-10. TPHG was detected in groundwater at 150 mg/1 at 88 feet bgs in CPT-10 and 87 <br /> feet bgs in CPT-11. As discussed above in reference to COC distribution in soil, this apparent <br /> COC distribution in the groundwater may be a function of the sampling intervals. <br /> TBA and 1,2-DCA were detected in groundwater samples collected at borings CPT-1, CPT-4, <br /> CPT-8, and CPT-13. 1,2-DCA was also detected in samples collected at borings CPT-5, CPT-7, <br /> CPT-10, and CPT-11. MTBE, ETBE, TAME, or DIPE were not detected in any of the <br /> groundwater samples. As shown on Figures 6 through 10, the Hydropunch"M data suggest a co- <br /> mingling of the Sunland and Apache plumes. <br /> Monitoring Well Network: Groundwater monitoring wells at the Apache site are screened in two <br /> zones: an upper zone between 46.5 and 70 feet bgs, and a lower zone between 94 and 115 feet <br /> bgs. Figures 11 and 12 depict the distribution of CDCs in the upper and lower water-bearing <br /> zones, respectively. TPHG, benzene, TBA, and 1,2-DCA concentrations in groundwater are <br /> included on Figures 3 and 4. <br /> During the most recent sampling event (second quarter 2002), TPHG and benzene in the upper <br /> water-bearing zone were detected in wells VEW-1 (19,000 and 1,600 µg/L, respectively), and <br /> VEW-2 (120,000 and 1,500 µg/L, respectively), situated near the former UST. The lateral extent <br /> of TPHG and benzene appear to be adequately delineated. In the lower zone during the second <br /> quarter 2002, TPHG and benzene were reported 160,000 and 20,000 µg/1, respectively, in the <br /> p:\ppache Plastics\Reports\Apache SCM.doc Page 9 Stratus <br />