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Alternative 3. Exhibit 6 shows the layout for aerated static pile composting using the <br /> extended pile technique. Mixing of materials would occur adjacent to the RRF. Processed <br /> material would be placed prior to dumping semi-solid or liquid feedstock. Mixing would <br /> be accomplished using a front end loader, compost mixer or Windrow machine depending <br /> on the quantity of maternal to be mixed. At the composting area a 1-foot-thick layer of <br /> ground wood waste would be placed over the aeration pipes. The compost mixture would <br /> be placed over the ground wood waste to a depth of 7 feet. The compost mixture would be <br /> covered with a 1-foot-thick layer of insulating material. The extended process is con- <br /> structed without a space between adjacent piles or cells. The piles would be 75 feet long. <br /> Aeration would be provided using one 400-cfm blower per pile and two 4-inch aeration <br /> pipes per pile. The aeration system would be designed to either pull air from the piles <br /> (negative) or blow air into the piles (positive). Initially, the aeration system would be <br /> operated in the negative mode and the exhausted air would be piped to a biofilter for reduc- <br /> tion in odorous compounds and VOC reduction. The basic composting process criteria are <br /> similar to Windrow composting except the piles are not turned. Forward will consider this <br /> option if necessary for odor or VOC control for the feedstocks they desire to compost. <br /> Alternative 4. Exhibit 7 shows the layout for a combination of aerated static pile and <br /> Windrow composting. The criteria are the same as for options 2 and 3 with the exception <br /> that 4 weeks composting time is assumed for the aerated static pile method. The alterna- <br /> tive provides some capacity for the higher cost aerated static pile process with the remain- <br /> der of the space used for Windrow composting. This provides some capacity for more <br /> difficult wastes that might require aerated static pile composting for odor and VOC control, <br /> but provides Windrow composting for aerated curing of the aerated static pile compost and <br /> other less sensitive feedstocks. Forward would consider this option for limited capacity if <br /> odor or VOC control is necessary for some feedstocks, but not all feedstocks. <br /> Alternative 5. Exhibit 8 shows the layout for a combination of enclosed agitated bed and <br /> Windrow composting. The criteria are the same as option 4. The enclosed agitated bed <br /> process replaces the aerated static pile process. Enclosing the composting process provides <br /> a higher level of odor and VOC control and eliminates the effect of precipitation and poten- <br /> tial for leachate generation. This may allow Forward to compost feedstocks not otherwise <br /> permissible. The agitated bed process consists of concrete bins 10 feet wide 230 feet long <br /> and 5.5 feet high. A track mounted mixer mixes the compost daily and at the same time <br /> moves the compost from the inlet to the outlet. Aeration is provided by blowing air up <br /> through the pile. All air is contained in the building and is exhausted through a biofilter <br /> for odor and VOC reduction. <br /> iCuring and Screening. Following composting, the mixture may be screened or placed in <br /> piles 10 feet high and 20 feet wide at the base for curing. In curing a slower rate of <br /> decomposition occurs. Curing of 1 to 6 months will be provided. A longer curing period <br /> is desirable for high quality compost. The curing period will depend on the quality desired <br /> and this in turn will depend on the market or final use of the product. The capacity of the <br /> composting site is significantly less to produce a higher quality compost product. After <br /> curing the material may be screened. Screening produces a higher quality material, but <br /> wa10029B64.wp5/28 <br /> 9/28/94 '28 <br />