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' LPH, and had the highest concentrations of TPHg (220,000 ug/L) and benzene (2,200 ug/L), <br /> and minor concentrations of MtBE in well MW-9, concentrations of petroleum hydrocarbons and <br /> ' MtBE have generally decreased to non-detectable levels in other site wells TPHg and BTEX <br /> concentrations in well MW-1 have significantly declined over time (Figure 7) Residual <br /> concentrations of benzene, toluene, and ethylbenzene that have been detected in well MW-1 <br /> ' over recent quarters are below the Tier 11 SSTLs that were applied during the RBCA <br /> assessment (Appendix D) A groundwater chemical concentration map depicting <br /> concentrations from the most recent quarterly sampling event conducted in October 2004 is <br /> ' included as Figure 8 <br /> Analysis for the presence of MtBE was first performed on groundwater samples from site wells <br /> in October 1997 Historical results through October 2004 indicate that low levels of MtBE have <br /> ' been detected in wells MW-1 through MW-7, MW-9, and MW-10 With the exception of some <br /> detections of MtBE reported in well MW-4 between January 1998 and November 1999 up to a <br /> historical site maximum concentration of 41 2 ug/L, MtBE concentrations in the aforementioned <br /> ' wells have historically been reported at levels below the California Department of Health <br /> Services (DHS) maximum contaminant level (MCL) of 13 ug/L Historical results for fuel <br /> oxygenates other than MtBE (TBA, DIPE, EtBE, TAME) compiled since July 1999 indicate that <br /> t these constituents have not been detected in the site wells Historical groundwater analytical - <br /> results for fuel oxygenates are presented in Table 5 <br /> ' Overall, active remediation and natural attenuation processes at the site have resulted in the <br /> reduction of the dissolved plume beneath the site, which is limited in its ext'bnt to the vicinity of <br /> well MW-1 The lateral extent of the dissolved plume is defined across the site The vertical <br /> extent of dissolved petroleum hydrocarbons is defined outside the source area, with the <br /> exception of in the area of well MW-1, which has not been defined to non-detectable levels of <br /> TPHg and MtBE beyond the completed depth of the well (101 5 feet bgs) Residual <br /> concentrations of benzene, toluene, and ethylbenzene that have been detected in well MW-1 <br /> ' over recent quarters are below the Tier II SSTLs that were applied during the RBCA <br /> assessment (Appendix D) A schematic illustration of the historical pathway of the dissolved <br /> plume beneath the site is presented as Figure 9 <br /> ' 73 Estimated Residual Mass <br /> According to estimated mass calculations, approximately 24,335 pounds (3,479 gallons) of <br /> residual TPHg were present in soil, and approximately 37 84 pounds (5 41) gallons of TPHg <br /> were present in groundwater before the implementation of remedial action at the site (SECOR, <br /> September 8, 1998) <br /> Historical pre-remediation sod analytical results in the area of the former USTs and in the vicinity <br /> ' of well MWA were used to estimate the area of residual petroleum hydrocarbon impacts <br /> remaining in soil beneath the site after remediation Based on the results obtained during the <br /> November 2004 post-remediation soil confirmation sampling event, an estimated 789 7 pounds <br /> of TPHg remain beneath the site in the area of the former USTs, and an estimated 148 0 <br /> pounds of TPHg are present in soil in the vicinity of well MWA <br /> Historical groundwater data collected from well MWA during the operation of the SVEIAS <br /> ' system from February 2000 through October 2004 was used to estimate residual TPHg <br /> Time Ool Asmt&SCM doc 12 March 17,2005 <br /> ' 770T 41658 00 0015 <br />