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MWMC FACILITIES PLAN <br /> <br />requirement in the anaerobic digesters alone. Providing additional volume through either <br />construction of a new FSL or using the SIWF lagoon is based on meeting the VSS loading <br />design criteria at the current projected flows and VSS loads to the existing FSLs. If the fourth <br />digester uses an advanced digestion process, the VSS loading to the FSLs will be less than <br />the current projections. <br /> <br />At this time it appears most likely that a fifth FSL will not be needed within the design <br />period. There are several reasons for this assumption. The first is that overall plant VSS <br />reduction requirements are likely to be achieved even if VSS loading to the existing FSLs <br />exceeds design criteria. The second is that digester mixing improvements will increase <br />active digester volume and further improve VSS destruction. The third is that the fourth <br />digester (constructed between 2010 and 2012) may use an advanced digestion process that <br />will improve reduction in VSS loads to the FSLs. Based on the phasing shown in Figure <br />6.5.3-1, there will be 3 to 5 years between construction of the fourth digester and when a <br />fifth FSL is required. <br /> <br />Solids Inventory <br />Currently, the solids in the FSLs are processed through mechanical and passive dewatering <br />processes. Mechanical dewatering is accomplished through three 2-meter BFPs. Passive <br />dewatering is accomplished using thirteen air-drying beds. Mechanical dewatering is the <br />primary processing method. The FSLs are harvested seasonally, typically from March <br />through September. Beginning in February, one FSL is taken offiine to provide a minimum <br />of thirty days residence time before harvest. Beginning in March a dredge is used to pump <br />solids from the FSLs into two 370,000-gallon mix tanks that then feed the BFPs. Dewatered <br />cake is then placed in windrow piles in the air drying beds where it is further dewatered to <br />approximately 40 to 50 percent solids. In mid-summer the windrowed piles are trucked to <br />local cooperative farms for land application. Solids (digested sludge) sent to the FSLs year- <br />round exceed the seasonal capacity of the dewatering processes, based on current operation, <br />thus leading to increased inventory. <br /> <br />As the solids inventory in the FSLs has increased to levels above typical operating <br />conditions, the increase in the FSL solids blanket has decreased the water cap on the FSLs. <br />The water cap helps to control odors in the FSLs by decreasing the potential for turn over of <br />the solids blanket. Turn over occurs when the upper layers of the solids blanket become <br />warmer than the bottom layer and the organic material in the bottom layer flips with the <br />warmer upper layer. This flip (turn over) brings anaerobic organic material from the bottom <br />to the top and results in the release of odorous fumes. Maintaining a water cap depth <br />greater than the solids depth helps to control the temperature of the solids layer beneath <br />and, therefore, odors. On-site staff have recognized the increased solids inventory and they <br />have anticipated that the solids inventory would be reduced once the BF Phase 1 came <br />online in the summer of 2004. Recommendations for future operating strategies to reduce <br />the solids inventory in the FSLs are discussed below. <br /> <br />Recommendations <br />At this time the need to construct a fifth FSL by a specific year is not recommended, nor is it <br />expected that a fifth FSL will be needed within the design period. It is recommended that <br /> <br />6-40 MWMC_6.0_REV11.DOC <br /> <br /> <br />