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Draft Environmental Impac R t a IV.F-25 <br /> Rep ort Page <br /> Forward Inc. Landfill Expansion <br /> differential settlement. The landfill design attempts to mitigate this by placing daily soil cover <br /> over the refuse. The potential for differential settlement affecting the landfill leachate collection <br /> system is limited to the Austin Road portion of the combined landfill where the new leachate <br /> collection system is to be placed on top of the existing landfill. Differential settlement could <br /> damage the liner and/or leachate collection system and affect water quality. <br /> The following measures are proposed as part of the project, as described in the Project <br /> Description: <br /> • A settlement analyses was performed to evaluate how landfill grades could change in <br /> the future as refuse materials biodegrade and consolidate. <br /> • Maximum pre-loaded settlement of the combined landfill is projected to provide the <br /> maximum period for settlement, and take advantage of anticipated improvements in <br /> geosynthetic technology. <br /> • Future design for the vertical expansion will, if necessary, include additional <br /> components in the liner system, depending on future differential settlement on the liner <br /> system. <br /> • The appropriate responsible agencies,the CIWMB and RWQCB, shall conduct a review <br /> of the liner and leachate collection system for the vertical expansion over the existing <br /> landfill(s) proposed in the upcoming JTD update. <br /> This has for the most part been constructed. The design for the last part of it was approved this <br /> may and will be constructed this summer. <br /> Implementation of these procedures would reduce the impact to a less-than-significant level. <br /> Mitigation Measure F.5: None required. <br /> Impact F.6: A VOC-contaminated plume extending northeast from the northern edge of the <br /> landfill border could affect water quality in offsite private water supply wells. <br /> The extent of the groundwater plume associated with the landfill was underestimated in <br /> previous studies. This was documented in the 1994 Austin Road EIR, as updated in 2002 Austin <br /> Road Expansion EIR and the review of more current data and corrective action assessments. <br /> The water quality data show the contaminant plume associated with the area north of Austin <br /> Road Landfill unit to extend north to the NCYCC wells as already described. The recent <br /> RWQCB Order 2008-0714 addresses the need for further articulation of remedial action to <br /> remedy the offsite plume. The VOC-contaminated plume extends from the northern edge of the <br /> landfill border,to approximately 5,500 feet north/northeast(downgradient)of the Austin Road <br /> unit. The plume is thought to take more of a northerly direction near its leading edge. <br /> Concentrations in some key downgradient monitoring wells, such as MW-11, has demonstrated <br /> the existing system is very effective in reducing the VOC in the border area where the extraction <br /> wells are most effective (see Table IV-F1). Further northward of the infiltration basin the <br /> capture of the plume is more problematic. <br /> The April 1999 CDM report estimates the probable need to extract up to 1,570,000 gpd based on <br /> the extended pumping capture zone model. This compares with actual extraction volumes of <br /> the current system estimated at about 400,000 gpd. The volume of groundwater extracted could <br /> be more that the CDM projections based on the AEE model, depending upon which <br /> combination of remedies are selected. The planned artificial recharge would also have the <br />