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VOCs <br /> Two VOCs (Trichloroethene, and 1,1-Dichloroethene) at concentrations below 2 ppb were reported in <br /> samples collected from well MW-3 during the lst and 2nd semester 2011 sampling events. These detections <br /> will continue to be scrutinized in the future. As previously described,the County suspects that this new <br /> detection of VOCs at MW-3 is related to the placement of a gas-tight HDPE membrane over Module"I" <br /> refuse. VOCs were not detected in any other well during 2011. <br /> Collection of LFG was improved in the second quarter 2011 by installing a replacement well GX-2A and <br /> increasing the size of collection pipes that serve wells GX-7 and-9. <br /> The County continues to be concerned that installation of impermeable liner over refuse decreases the <br /> potential venting of LFG in spite of the presence of a LFG collection system. Sealing the refuse from the air <br /> can increase the potential for contamination of groundwater by LFG entering the soil beneath the landfill. <br /> Surface Water <br /> Surface water samples were last taken from the creek flowing along the eastern property boundary during the <br /> first semester 2011. The results of analyses of the upstream and downstream samples were similar, showing <br /> that the surface water contribution to the stream did not degrade the quality of the stream. In fact,the <br /> downstream sample had a lower concentration in both total dissolved solids and electrical conductivity than <br /> the upstream sample,possibly indicating that the surface water from the landfill contributes less to the stream <br /> than upstream surface water. <br /> Surface water was not flowing in the second semester due to lack of rain. <br /> Note that the creek receives contribution from the ground surface and several smaller creeks on the <br /> neighbor's properties east of the creek, and that these surfaces and the creek itself are subject to cattle <br /> grazing(and defecation). Surface water from these adjacent properties also enters the stream, and is <br /> included in the samples taken. <br /> HISTORICAL TIME SERIES PLOTS AND STIFF DIAGRAMS <br /> Constituents not detected are plotted at a value of half their respective detection limits in the Historical Time <br /> Series Plots (Appendix F). Outliers were included in the plots as directed by RWQCB staff. <br /> Stiff diagrams are submitted annually with the second semester and annual report. The stiff diagrams <br /> submitted for the first and second semesters indicate a calcium-bicarbonate water type since these ions have <br /> the highest concentrations in the six wells (Appendix F). The water type is similar in all wells as indicated <br /> by similarity in concentrations of the various constituents and the similarity in diagram shapes. This <br /> similarity indicates that the groundwater is not impacted as it moves under the landfill. The shapes of the <br /> diagrams between the first and second semesters are also very similar indicating that the general groundwater <br /> quality has not changed throughout the year, which is also an indication of no impact from the landfill. <br /> PROGRESS OF EVAPOTRANSPIRATION COVER <br /> The purpose of the evapotranspiration cover is to capture rain water during the wet months, allowing the <br /> vegetation growing on that cover to remove the water from the soil during the dry months,restoring the <br /> ® storage capacity of the soil for the next rainy season. Providing storage for rainwater each year prevents the <br /> percolation of water into the refuse. The intention of this closure method is to minimize water percolating <br /> Foothill Sanitary Landfill 12 Department of Public Works/Solid Waste <br /> 2"d Semester and Annual 2011 Groundwater Monitoring County of San Joaquin—January 31,2012 <br />