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in accordance with CCR Title 27, Section 20937, Forward continues to install additional <br /> landfill gas extraction wells, as needed. <br /> Concentration Limit Thresholds <br /> As specified in the RPCMP and RWQCB Order No. R5-2003-0049 for the Forward <br /> Landfill,the routine inorganic monitoring data obtained during the first quarter 2013 <br /> monitoring period were compared to established intrawell concentration limits (CLs) <br /> calculated for the Forward Unit. The CLs are summarized in Table 2-4 and compared to <br /> the analytical results collected during the first quarter 2013. As summarized in this table, <br /> CLs were exceeded for chloride at wells MW-2A and MW-13; nitrate as nitrogen (N) at <br /> well MW-14; pH at well MW-23R; and for sulfate at wells MW-14 and MW-15. With <br /> the exception of nitrate-N concentrations in well MW-14 and sulfate concentrations in <br /> well MW-15,trend analyses indicate that there were no statistically significant increasing <br /> trends calculated for the CL exceedances during the current monitoring period. Trend <br /> analyses are included in Appendix D. Previously submitted No Release Demonstrations <br /> (NRDs) for these common inorganic constituents at the Forward Unit have concluded <br /> that the CL exceedances are not the result of a release from the Forward Unit and as a <br /> result retesting is not necessary for these common inorganic constituents. <br /> Vadose Zone Monitoring <br /> The current vadose-zone monitoring network at the Forward Unit consists of 17 <br /> lysimeters. The lysimeter locations are shown on Figure 2-1. Each accessible lysimeter <br /> was inspected and vacuums were reset to approximately—25 inches of mercury on <br /> March 7, 2013 at each suction lysimeter. On March 19, 2013, the lysimeters were again <br /> checked and positive pressure was applied to evacuate the accumulated sample. As <br /> recorded in the field notes for lysimeters (Appendix C) and summarized on Table 2-5, <br /> lysimeters were reported dry to moist, and as a result, no soil-pore liquid samples were <br /> collected during the current monitoring period. Of note,there was no access port to <br /> inspect pan lysimeters WMW-DO 1N, WMW-DO1 S, and WMW-D02. GLA and Del- <br /> Tech will be working with Forward to access these pan lysimeters for future monitoring. <br /> Leachate Monitoring <br /> Leachate sumps are inspected for the presence of leachate and observations are recorded <br /> at least weekly by Forward Landfill personnel. If leachate is detected in a sump, it is <br /> pumped into the surface impoundment(WMU F)for evaporation. During the first <br /> quarter 2013, leachate was observed at all of the holding areas except WMU D-87 and <br /> WMU D-88 A/B. Freeboard at WMU-F ranged from approximately 3.75 to 6.33 feet <br /> during the first quarter 2013 monitoring period. Appendix A presents copies of the <br /> leachate logs and the freeboard observation logs. <br /> Leachate samples were collected on a monthly basis and analyzed in the field for pH, <br /> specific conductance, and temperature. Results of monthly field monitoring <br /> measurements for the first quarter 2013 are presented in Table 2-6. <br /> C:\2013-0021\FA_1Q13.doc 6 Geo-Logic Associates <br />