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two additional soil gas points (A1-SG2 and Al-SG3) were installed and sampled in an effort to <br /> delineate the PCE impacts. Al-SG3 was placed approximately 10 feet upgradient of Al-SGI <br /> (relative to groundwater flow direction), and Al-SG2 was placed approximately 10 feet <br /> downgradient of Al-SGI. Results from these additional soil gas points showed PCE <br /> concentrations of 250 ug/m3 (Al-SG2) and 93.0 ug/m3 (A1-SG3), and that PCE concentrations <br /> rapidly decrease in a relatively short distance away from Al-SGI. The source of PCE is not <br /> known, but PCE is not associated with MGP residuals or gasoline. <br /> Groundwater AOI <br /> Groundwater impacts at the Site are limited to AOI 4, located in the northwestern portion of the <br /> Site (Grid A3 in Figure 14) where a former gasoline UST was located. This gasoline UST has <br /> been removed and residual TPH impacts in groundwater associated with this area were above the <br /> Suggested No Adverse Response Level/Taste and Odor Threshold of 100 ug/L during the RI. <br /> However, follow-up samples collected during the SSI, showed only two detections (MTBE at 1.1 <br /> and 1.2 ug/L) in the samples collected from well TW-5 (TW-5 and Dup-1). Based on these <br /> results impacts in groundwater have been delineated. <br /> Additionally, based on results of the long term groundwater monitoring conducted at the Site <br /> after the gasoline UST was removed, the impacts in groundwater have not migrated off-site. As <br /> such, the gasoline UST case was closed per Regional Water Quality Control Board concurrence <br /> letter dated January 2, 1997 and by the SJCDEH in a letter dated January 15, 1997. <br /> Groundwater in this area has been identified as an AOI but it is anticipated that no remedial <br /> efforts will be required to manage impacted groundwater. If future groundwater remedial efforts <br /> are required, it is anticipated that they will be limited to monitored natural attenuation. <br /> Health Risk Assessment <br /> A health risk assessment (HRA) for the Site will be submitted in conjunction with the Removal <br /> Action Workplan (RAW). The details of the HRA will be discussed in an HRA scoping meeting <br /> between DTSC's Human and Ecological Risk Department (HERD), PG&E, Parsons and Iris <br /> Environmental, the health risk assessor for the Site. A technical memorandum that documents <br /> the requirements identified for the HRA in the scoping meeting will be submitted to HERD for <br /> review and approval. Thereafter, the HRA will be initiated and incorporated into a streamlined <br /> HRA/FS/RAW document, to be submitted to DTSC for their review and approval. <br /> The results of the HRA will be used to identify those areas of the Site to be targeted for <br /> remediation, and to define the ultimate level of remediation that would be required to restore the <br /> Site to conditions that would be protective of all potential future land uses to the extent <br /> practicable and feasible, given the potential limitations associated with structures and the <br /> operating facility. As the overall remedial action objective is to remediate to a point that the Site <br /> would have no land-use restrictions and could be used for residential purposes, the focus of this <br /> HRA will be to characterize risks to future hypothetical residents and develop appropriate health- <br /> based target cleanup goals that would be protective of future on-site residential populations. <br /> In the unlikely event that the remediation is not effective in restoring the Site to a condition that <br /> is suitable for future on-site activities, a range of commercial cleanup goals can be used to <br /> evaluate the types of institutional controls, if any, that may appropriate for the long-term <br /> management of the Site. <br /> PARSONS 6 FINAL RI REPORT-FORMER TRACY MGP <br /> APRIL 2010 <br />