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enhanced vacuum within waste mass in close proximity to impacted groundwater. The third well <br /> will be used to provide an enhanced vacuum within the waste mass below the over lying <br /> impermeable liner. The construction details of typical LFG well is shown in Appendix A. <br /> The existing LFG extraction system has wells installed on approximately a 250-ft spacing within <br /> the centroid of the waste mass of Area"I". This pattern follows the State-of-Engineering <br /> Practice in LFG design. Engineering practice has shown that such a spacing provides sufficient <br /> vacuum within the waste mass to limit the buildup of LFG, but not exert such a vacuum that will <br /> cause the intrusion of oxygen into the waste mass. The proposed wells maintain the approximate <br /> 250-ft spacing between wells, yet keep the wells approximately 250-ft from the edge of the waste <br /> mass to limit the potential for oxygen intrusion. <br /> ' It is proposed that the three additional extraction wells and up-sizing of the LFG piping network <br /> be installed by December 31, 2014. This installation will also require approval from San Joaquin <br /> County Environmental Health Department and perhaps other agencies. However, the County <br /> believes the required permitting by these agencies can be obtained to meet this schedule. <br /> Although the present detection of VOCs in well MW-3 is not consistent between monitoring <br /> events, it appears that low levels of VOCs are present in the groundwater at MW-3, due to the <br /> entrapment of LFG under the HDPE liner placed over a portion of Area"I". The <br /> commencement of enhanced LFG extraction from Area"I" in the vicinity of MW-3 and from <br /> below the HDPE liner commencing in 2015 will have a high probability of eliminating the <br /> detection of VOCs at MW-3 by 2020. <br /> Soil Gas Well Work Plan <br /> Well SG-I is a single probe station that was installed as part of the EMP in 2003. Wells SG-2 <br /> through SG-I I were not originally intended to function as a system for the detection of <br /> groundwater impacts nor for the detection of off-site migration. These single-probe monitoring <br /> wells originally intended to function as shallow LFG monitoring stations and approved by <br /> RWQCB staff for that purpose. They were selected for the collection of vadose gas samples, <br /> because the County could use them to fulfill the monitoring requirements for CalRecycle and the <br /> CVRWQCB in force at that time (2004). <br /> However, the County has since installed a more extensive 3-probe vadose zone monitoring <br /> network consisting of 25 wells (SG-12 and SG-102 through SG-125) for perimeter migration <br /> monitoring (Figure 2). SG-12 was installed in 2004 and SG-102 through SG-125 were installed <br /> in 2009. These vadose monitoring stations are located along the landfill's property boundary at <br /> approximately 1,000-ft centers. Their construction details are contained in Appendix B. <br /> Because the newer vadose zone monitoring network consists of 3-probe wells,the County <br /> proposes to discontinue TO-15 monitoring of most of the existing single-probe well locations. <br /> ' Several of the 3-probe wells that are closest to existing waste disposal areas are proposed for <br /> vadose zone TO-15 monitoring. They include: <br /> • SG-117, located to the east of Area 2 and in the general vicinity of SG-7. <br /> ® SG-118, located to the east of Area 2 and in the general vicinity of LFG flare station. <br /> • SG-119, deep well located along the southern limit of Area 2 and a replacement for SG-8. <br /> Foothill Sanitary Landfill 5 Department of Public Works/Solid Waste <br /> Engineering Feasibility Study County of San Joaquin—August 2014 <br />