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• <br /> Draft Supplemental Environmental Impact Report Page III-30 • <br /> Forward Inc.Landfill 2018 Expansion Project <br /> the pipes. The drainage layer is separated from the operations layer above by a nonwoven • <br /> geotextile to prevent migration of fine-grained material into the LCRS. • <br /> The LCRS design for slopes greater than 15 percent consists of a geocomposite drainage net <br /> (GDN). GDN is used due to construction and stability concerns associated with placement of • <br /> granular materials on steep slopes. No collection pipes are required on the side slopes because any . <br /> leachate occurring on the slope would naturally flow down slope. <br /> Leachate collected in the LCRS would flow through the drainage layer to the pipes and <br /> subsequently into leachate collection sumps. Submersible pumps located in each sump would ' <br /> pump leachate from the LCRS to lined surface ponds, from which the leachate evaporates. • <br /> Three leachate evaporation impoundments are permitted at the site, of which two are constructed <br /> and are currently in use. WMU F North is located in the southwest region of the existing Forward • <br /> Landfill,just north of the South Fork. It was constructed in 1999 and provides containment for . <br /> leachate from the active portions of the southern WMUs. The leachate impoundment was sized <br /> based on actual leachate generation records from 1991 to 1997 and has a design capacity of <br /> approximately 3.5 million gallons. WMU F West is located in the northern portion of the site, <br /> directly west of WMU FU-03. It was constructed in 2003 with a design capacity of 3.4 million • <br /> gallons and receives leachate from the northern waste management units. A third impoundment, <br /> WMU F South,has not yet been constructed as no waste has yet been landfilled south of the South <br /> Fork. WMU F South would replace the existing WMU F North leachate impoundment. <br /> If, during the service life of the landfill,the demand on the leachate impoundment exceeds <br /> capacity,Forward would implement an alternative leachate management plan. Leachate in excess <br /> of the impoundment's capacity would either be pumped to temporary onsite tanks,trucked for off- <br /> site disposal at the City of Stockton Municipal Utility Department wastewater treatment plant <br /> located at 2500 North Navy Drive in Stockton,or trucked to another off-site licensed Treatment • <br /> and Disposal Facility. Leachate stored in the temporary on-site tanks may be released back into the • <br /> impoundment at a later date. <br /> Leachate Monitoring • <br /> To monitor the LCRSs,Forward,Inc.conducts a leachate monitoring and sampling program in <br /> compliance with WDR Order No. R5-2014-0006. Quarterly and annual reports of the monitoring <br /> results are submitted to the DTSC,RWQCB,and the San Joaquin County Environmental Health • <br /> Department, which is the Local Enforcement Agency(LEA). • <br /> A leak detection system is also located under the sumps in the WMUs and the leachate <br /> impoundments. The leak detection system currently consists of suction cup lysimeters and pan <br /> lysimeters installed in all the Subtitle D lined WMUs with permanent sumps(i.e.WMU D-93,D-01, i <br /> D-02,FU-03,FU-04, FU-05, and FU-06). A suction lysimeter is a device that measures the soil pore • <br /> water in the unsaturated zone, while a pan lysimeter measures the water that percolates down <br /> from below the sump. The lysimeters are sampled and tested in accordance with the site's WDRs. <br /> The former Austin Road Landfill unit has no leachate collection system and therefore no <br /> lysimeters. . <br />