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In this semester, leachate from all three Lined Areas was returned directly to the refuse of at <br /> approximately 160 ft NGVD, over approximately 120 feet of refuse compacted in multiple lifts. Data <br /> indicates that the leachate is being absorbed by the dryer refuse, and is not recirculating. <br /> Overwhelming of the LCRS system due to excessive recirculation is not indicated. Such indication <br /> would include the inability of a leachate sump pump to empty the sump. This condition was observed <br /> once, in 2003,when Area 4 was first installed. At that time, significant areas of that Area was lacking <br /> refuse, allowing rain water to quickly reach the LCRS without the opportunity to be absorbed by refuse. <br /> This situation was corrected by relocating the infusion of leachate to an area that contained more dry <br /> refuse. <br /> Overwhelming the capacity of the refuse to absorb leachate would be indicated by leachate seeps on the <br /> side of the fill in the vicinity of the infusion areas. This condition has not been observed. <br /> Leachate System Testing <br /> Testing the leachate system consists of monitoring the pumping rate of each sump pump monthly. <br /> Leachate pumps that are operating at the rate consistent with past performance are considered to be <br /> operating normally. The in-line filters at the pump intakes are replaced every one to two years when a <br /> diminished flow rate or increased headloss across the filter(pumping stations for Areas 1 and 3) is <br /> observed. Flow rate is calculated by the operator while observing the flow meter. Exposed leachate <br /> pipes are inspected for damage or disturbance once a month. <br /> ANNUAL FACILITY INSPECTION <br /> The facility was inspected to assess damage to the drainage control system, groundwater monitoring <br /> equipment in September 26, 2011. Standard Observations are attached. <br /> Generally,the site was found to be in excellent condition due to the ongoing drainage system <br /> maintenance by the site superintendent. Groundwater monitoring equipment remains in good working <br /> order. <br /> HISTORICAL TIME SERIES PLOTS AND STIFF DIAGRAMS <br /> Historical Time Series Plots are included with this report on CD. Constituents not detected are plotted at <br /> a value of half their respective detection limits in the Historical Time Series Plots. Note that Outliers <br /> were included in the plots as directed by RWQCB staff. <br /> Stiff diagrams are submitted semi annually and are included with this report on CD. The stiff diagrams <br /> submitted for the first semester indicate that well G-1 is a sodium-bicarbonate water type, whereas,the <br /> wells do not show a prominent cation with a prominent anion of bicarbonate. The dissimilarity in <br /> diagram shapes may be an indication of natural regional changes in groundwater quality conditions. <br /> North County RC&SL Public Works/Solid Waste <br /> 2nd Semester and Annual 2013 Groundwater Monitoring 15 County of San Joaquin—January 25,2014 <br />