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flow rate of 240,953 gallons per day. During the monitoring period, it is calculated that <br /> the GTF removed approximately 1.12 pounds of VOCs. <br /> 3.2 CONSTITUENTS OF CONCERN <br /> During the first quarter 2013 monitoring period, groundwater, domestic well, and surface <br /> water samples from the Austin Unit were analyzed for the five-year COCs listed in <br /> RWQCB Order No. R5-2003-0049 and are summarized in Tables 3-1, 3-2, 3-3, and 3-5. <br /> As shown in Tables 3-1, 3-2, 3-3, and 3-5, with the exception of one semi-volatile <br /> organic compound (SVOC)that was measured at a trace concentration(di-n-butyl <br /> phthalate) in the sample from well AMW-4, no organic COCs were detected in the <br /> groundwater and surface water samples. It should be noted that phthalates are used as <br /> plasticizers in polyvinyl chloride (PVC), which is a common monitoring well material. <br /> Therefore, the presence of di-n-butyl phthalate in well AMW-4 is believed to be a field <br /> contaminant. <br /> Several inorganic COCs were detected in both up-gradient and down-gradient wells and <br /> surface water stations. The similarity in the concentrations in both up-gradient and <br /> down-gradient wells and surface water stations suggest that the inorganic COCs are <br /> naturally occurring. A comparison of inorganic COCl to Federal and State maximum <br /> contaminant levels (MCLs) for drinking water, indicate that the MCL for antimony <br /> (0.006 mg/L) was exceeded in all groundwater wells except AMW-4, AMW-5R, <br /> AMW-6, and AMW-10. No other inorganic MCLs were exceeded during the COC <br /> monitoring event. <br /> 3.3 SUMMARY <br /> Groundwater quality conditions beneath the Austin Unit during the first quarter 2013 <br /> monitoring period were generally similar to historical results. During the first quarter <br /> 2013 monitoring period, non-statistical exceedances for VOCs were identified at DMP <br /> wells AMW-6, AMW-13 and AMW-14. Trend analyses indicate that statistically <br /> significant increasing temporal trends were calculated for PCE and TCE in well <br /> AMW-13. These results are similar to previous results and it has been recommended that <br /> wells AMW-6, AMW-13, and AMW-14 be re-designated as CAP wells since they have <br /> historically contained VOCs. For the routine inorganic monitoring parameters, CLs were <br /> exceeded for constituent concentrations in DMP wells MW-2A, MW-13, MW-14, <br /> MW-15, and MW-23R. With the exception of nitrate-N concentrations measured in well <br /> MW-14 and sulfate concentrations measured in well MW-15,there were no statistically <br /> significant increasing trends calculated for the CL exceedances during the current <br /> monitoring period. In the CAP wells,trend analyses are performed instead of <br /> comparison to CLs. During the current monitoring period, statistically significant <br /> increasing trends were noted for three VOCs in CAP well AMW-1, while decreasing <br /> VOC trends were noted for several VOCs in CAP wells AMW-1, AMW-4, AMW-10, <br /> and AMW-11. The increasing trend exhibited for cis-1,2-DCE at well AMW-1 and <br /> generally decreasing (organic and inorganic)trends noted in all of the CAP wells, <br /> C:\2013-002I\FA_1QIIdoc 13 Geo-Logic Associates <br />