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• <br /> REsPERUvBL'C <br /> ICES <br /> Mr. Brendan Kenny <br /> Engineering Geologist <br /> Central Valley Regional Water Quality Control Board <br /> 11020 Sun Center Drive, Suite 200 <br /> Rancho Cordova, CA 95670 <br /> October 24, 2017 <br /> RE: Forward Landfill—Third Quarter 2017 <br /> Dear Mr. Kenny: <br /> In accordance with WDR Order No. R5-2014-0006, Forward Incorporated (Forward) is pleased to submit <br /> this Third Quarter 2017 Monitoring Report for the Forward Landfill. Included in this report are the results <br /> of groundwater, surface water, and vadose zone monitoring. In addition this report presents a summary <br /> of monitoring of facility operations including cannery waste monitoring, leachate extraction, LFG <br /> extraction, and additional monitoring in accordance with Water Code Section 13267 Order for Technical <br /> Reports Regarding Acceptance of Hazardous Waste. <br /> • According to the Forward Landfill Operations Manager, standard observations have been conducted <br /> weekly during the reporting quarter. The Forward Landfill Operations Manager also reported that no <br /> surface water was discharged from the facility during the monitoring period. During the third quarter 2017 <br /> monitoring period, no notices of violation (NOVs) were issued by the San Joaquin County Environmental <br /> Health Department. <br /> For the Forward Unit, water quality monitoring for the third quarter 2017 indicated a non-statistical <br /> indication of release at well MW-2A as a result of three volatile organic compounds (VOCs) measured at <br /> trace concentrations; at well MW-16 as a result of one VOC measured at a quantifiable concentration; <br /> and at well MW-17 as a result of three VOCs measured at quantifiable concentrations and four VOCs <br /> measured at trace concentrations. Of note, these organic constituents have been previously confirmed <br /> and are currently in "Tracking Mode". For the inorganic monitoring parameters, concentration limits(CLs) <br /> were exceeded at wells MWA 0, MWA 5, MWA 7, MWA 8, MW-19, and MW-24. All of the inorganic CL <br /> exceedances were placed in "Tracking Mode" and are being evaluated for temporal trends. For <br /> constituent concentrations in "Tracking Mode", increasing trends were calculated for barium, bicarbonate, <br /> calcium, magnesium, and potassium at well MW-10; carbon tetrachloride and trichlorofluoromethane at <br /> well MW-17; sodium at well MW-18; and sodium at well MW-24. The surface water monitoring stations <br /> were inspected multiple times, but were dry each time and therefore could not be sampled. For vadose <br /> zone monitoring stations soil-pore liquid samples were collected from W-2, LY-A, and LY-BG-1 and a <br /> quantifiable concentration of t-butyl alcohol was measured in lysimeter LY-BG-1. <br /> For the Austin Unit, water quality monitoring for the third quarter 2017 indicated a CL exceedance and/or <br /> non-statistical indication of release at Detection Monitoring Program (DMP) wells AMW-6 and AMW-12 <br /> during the monitoring period, of which the tetrachloroethene concentration measured at DMP well AMW- <br /> 12 exhibited an increasing trend. In a letter dated October 17, 2017, the RWQCB was notified of the CL <br /> exceedances in wells AMW-6 and AMW-12. For the Corrective Action Program (CAP)/evaluation wells, <br /> 16 of 28 wells reported one or more VOCs exceeding a practical quantitation limit, with CAP well AMW- <br /> 22S having the highest total concentration of VOCs. Surface water samples collected from the upstream <br /> • <br />