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Site-Wide Comprehensive ROD -5- 1 May 1997 <br /> DDRW Tracy <br /> of construction, based on DLA funding available during the period the excavations are being <br /> conducted. The record shows that we have emphasized the need for a one-time removal action to <br /> meet final cleanup levels at these sites to be cost-effective and eliminate the probable need for future <br /> actions to complete site characterization and remobilization to be excavate further to meet final <br /> cleanup levels (see all previous RWQCB comment letters on the EE/CA documents and state letter <br /> dated 31.March 1997). <br /> As we have discussed, the ground water table is relatively shallow, approximately 18 feet bgs, and a <br /> number of the CoCs are present in soils at depth at these sites; therefore, the additional excavation <br /> necessary to meet final cleanup levels is critical to protecting water quality and may be limited. In <br /> order to meet cleanup levels in the ROD and be cost-effective, the excavation of contaminated <br /> soils should be implemented as a final remedial action. Final cleanup is achieved when <br /> concentrations of CoCs present in soils remaining above the water table are shown to be at or <br /> below final cleanup levels, as set forth in the ROD. The ROD should clarify that confirmation <br /> sampling will be conducted as part of the remedial action in accordance with an approved <br /> sampling and analysis plan (also see specific comments SWMUs 2, 3, & 33). <br /> Furthermore, these SWMUs have been identified as main source areas of ground water contamination <br /> at DDRW Tracy and remedial action is necessary to protect water quality. Soil cleanup levels must <br /> be achieved in order to meet groundwater cleanup levels. The assumption that the CoC soil (soil <br /> source area) concentrations were equal to final cleanup levels at SWMUs 2, 3 and 33 (e.g., see RI/FS <br /> Report Sections 12.3.4.1.0.3 & 12.3.4.2.0.4) was used as part of the basis for determining the need <br /> for groundwater remedial action and the cleanup levels. In addition, DDRW Tracy proposes to <br /> continue using the lagoons for percolating wastewater discharged from the wastewater treatment <br /> plant. Regional Board Order No. 96-122 regulates this discharge. Therefore, the ROD should state <br /> that if final soil cleanup levels are not met at these sites, DDRW Tracy will re-evaluate the remaining <br /> threat to groundwater and the ability to meet groundwater cleanup levels. <br /> 10. Correlate Soil Source Areas With Ground Water Plumes: The ROD does not clearly correlate <br /> soil source areas and ground water contamination identified at DDRW Tracy. The ROD should <br /> identify the soil source area(s) related to the areas where concentrations have been detected above <br /> ground water cleanup levels. Maps of contaminant plumes which show soil source areas for VOCs <br /> and pesticides should be included. <br /> 11. No Substance In Declaration For The ROD: This part of the ROD should present a concise <br /> summary of the selected remedies, basis for selecting these remedies, and statutory determinations. <br /> The site location should be modified to include the description presented in Section 1.2 of the OU-1 <br /> ROD. The declaration should state that the ROD presents the selected remedial actions for all soil <br /> sites (identified as a SWMU or soil source area) and for the OU-1 ground water plume and refer to <br /> map(s) which shows their location at DDRW Tracy. Plume maps which illustrate associated source <br /> area sites should be used (see General comment #10 ). <br /> The text should also clarify how the underground storage tanks (USTs) were addressed outside <br /> CERCLA. All references to LUFT Guidelines should be replaced by Tri-Regional Guidelines. The <br /> USTs which were addressed as part of SWMUs should be so specified. Major components of each <br /> selected remedy should be presented in bullet fashion. Additional language should summarize the <br />