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Page 105 <br /> system, and a series of secondary collection trenches beneath the liner and directly under the leachate <br /> collection trenches;(d)the operator will remove any hazardous materials spotted during delivery,thus <br /> minimizing the potential for leachate contamination if there is a break in the liner or the leachate <br /> collection system. <br /> Impact K.3: Project activities which increase leachate production from existing landfill materials <br /> during various phases could alternatively facilitate the remediation of local groundwater,or result <br /> in groundwater contamination. <br /> The collection of additional water quality data shows the h-,achate plume to be larger than was thought in <br /> 1994. Also, a regulatory cleanup and abatement order has been issued by the lead responsible regulatory <br /> agency—the Regional Water Quality Control Board (RWQCB�—for the assessment and-subsequent <br /> mitigation of the contaminant plume emanating from the landfill (current RWQCB Order 96-175, <br /> superceded Orders 92-143, 90-122, and 77-288). In April 1999, the City of. Stockton completed a <br /> Groundwater Corrective Action Engineering Feasibility Study Report (GCE) to evaluate the range of <br /> groundwater cleanup alternatives in terms of protection to the environment and consistency with <br /> regulatory requirements. In addition, as described above, leachate from part of the landfill's north face <br /> has been added to overall leachate collection quantities. Landfill leachate has been collected in a 12,000- <br /> gallon storage tank and removed when near full for off-site treatment at a licensed TDS facility. In the <br /> fourth quarter of 1998, the most recent data available, 1127 tons or 3,100 gallons of leachate were <br /> removed from the 12,000-gallon storage tank for off-site treatment. <br /> The GCE was prepared as part of the RWQCB Order, and addresses the requirement of both the RWQCB <br /> and California Code of Regulations,Title 27,which include the Waste Management Board requirements. <br /> The build-out of Phases V and VI may result in additional leachate generation. Changed conditions in <br /> 1999 compared to 1994 show the potential need for amore extensive groundwater extraction system. <br /> Additional groundwater extraction and treatment may be necessary in the future. Depending on the <br /> selection of the final remedy the larger size of the Groundwater Treatment System could impact the <br /> amount of filter media used to complete the cleanup operations. It also could result in.potentially new Air <br /> Resources Control Board (ARCB) permit requirements if an air stripper is proposed. As described in the <br /> 1994 EIR,these impacts would be significant and mitigable with adoption of the following measure. <br /> Miti ation K.3: (a)The extraction wells developed as part of the CAP shall be maintained and <br /> monitored during Phases V and VI,to be employed as needed for the extraction of any residual <br /> contamination by leachate. <br /> e <br /> Impact K.4: Surface and/or groundwater contamination could result if differential settlement <br /> damaged the liner and/or leachate collection system of the vertical expansion portion of the landfill <br /> (Phases V and VI). <br /> Since none of the proposed vertical expansion of the landfill has occurred since the 1994 EIR,and there <br /> are no new relevant regulatory requirements regarding potential impacts from groundwater contamination <br /> due to settlement-related failures,there would be no changes in the impacts or mitigation measures. As <br /> described in the 1994 EIR,these impacts would be significant and mitigable with adoption of the <br /> following measure. <br /> GRASSETTI ENVIRONMENTAL CONSULTING <br />