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Water Quality Monitoring Report <br /> Forward Landfill <br /> 2.2 Summary <br /> Environmental monitoring for the Forward Unit during the third quarter 2017 monitoring <br /> period indicates that non-statistical indication of release were identified at wells MW-2A as a <br /> result of three VOCs measured at trace concentrations; at well MW-16 as a result of one VOC <br /> measured at a quantifiable concentration; and at well MW-17 as a result of three VOCs <br /> measured at quantifiable concentrations and four VOCs measured at trace concentrations. Of <br /> note, these quantifiable organic constituents have been previously confirmed and are currently <br /> in "Tracking Mode". For the inorganic monitoring parameters, CLs were exceeded at wells MW- <br /> 10, MW-15, MW-17, MW-18, MW-19, and MW-24. All of the inorganic CL exceedances were <br /> placed in "Tracking Mode" and are being evaluated for temporal trends. For constituent <br /> concentrations in "Tracking Mode", increasing trends were calculated for barium, bicarbonate, <br /> calcium, magnesium, and potassium at well MW-10; carbon tetrachloride and TCFM at well <br /> MW-17; sodium at well MW-18; and sodium at well MW-24. For vadose zone monitoring <br /> stations soil-pore liquid samples were collected from W-2, LY-A, and LY-BG-1 and a quantifiable <br /> concentration of t-butyl alcohol was measured in lysimeter LY-BG-1. <br /> 3.0 AUSTIN UNIT <br /> 3.1 Water Quality Monitoring <br /> 3.1.1 Sampling and Laboratory Analyses <br /> Del-Tech performed routine monitoring of DMP, CAP, EMP wells at the Austin Unit during the <br /> third quarter 2017 monitoring period. Depth-to-water measurements were recorded in the <br /> groundwater monitoring wells on August 1 and 31, 2017. Groundwater sampling was <br /> performed between August 1 and 31, 2017, and surface water stations were sampled on <br /> August 23, 2017. <br /> Samples were collected from each sample point with sufficient liquid and submitted to BC for <br /> analysis of the routine monitoring parameters stipulated in RWQCB Order No. 115-2014-0006. <br /> Table 2-1 presents the monitoring schedule and summarizes the analytical methods utilized <br /> during the current monitoring period. In addition, wells AMW-1, AMW-7, AMW-10, and AMW- <br /> 13 were also sampled for total arsenic, nitrogen, iron, and manganese for the CWLAM program; <br /> and wells AMW-1, AMW-2, AMW-4, AMW-7, and leachate sump FU-04, FU-06, FU-08, FU-13/14 <br /> were also analyzed for dissolved inorganic/metals as required by Water Code Section 13267 <br /> Order for Technical Reports Regarding Acceptance of Hazardous Waste, Forward Landfill, San <br /> Joaquin County dated May 16, 2017. It should be noted that well AMW-2 was not sampled for <br /> the additional dissolved inorganic/metals due to a transcription error in the sample request and <br /> FU-08 was reported dry. All water quality samples were analyzed in the field for ORP, turbidity, <br /> temperature, specific conductance, and pH and recorded on well data sheets. The <br /> groundwater monitoring wells, surface water monitoring locations, and leachate were sampled <br /> in accordance with the sampling and analysis plan detailed in Appendix E. The well data sheets, <br /> raw laboratory data, certificates of analyses, and chain-of-custody records related to the <br /> Project No.S017.1030 I Water Quality Monitoring Report 9 <br /> October 2017 <br />