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Agenda - 12-01-2008 - 3d
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Agenda - 12-01-2008 - 3d
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4/23/2013 10:50:27 AM
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BOCC
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12/1/2008
Meeting Type
Regular Meeting
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Agenda
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3d
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Minutes - 20081201
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Appendix B <br />Overview of Waste Processing Technologies (WPlF) <br />1.1 "Proven" Technologies <br />Waste has been converted to beneficial use on a large scale for well over 100 years. <br />Incineration with electric power generation was first applied to MSVV in 1894 in New <br />York City. Since that time, the burning ofMSVV with energy recovery (now known as <br />VVTE) has matured into safe, effective and environmentally acceptable technology. <br />The proven large-scale waste processing methods include incineration and starved- <br />air combustion, as defined below: <br />Incineration: This is the controlled combustion of organic or inorganic <br />waste with more than the ideal air (stoichinnnethu) requirement - excess air - to <br />assure that complete burning occurs. <br />Combustion: Starved Air Starved air incineration utilizes |aas air than conventional <br />incineration, and it produces ash similar in appearance to that from o conventional <br />incineration process. The gases that result are burned in a second chamber. The <br />lower air requirement leads to smaller equipment sizes. This process, however, is an <br />incineration process. <br />Refuse-derived Fuel : An RDF system processes waste by shredding it and <br />removing ferrous metals in preparation for combustion. The removal of non- <br />combustibles can increase the specific heat content by over 10 percent and can allow <br />for revenues from the metals removed. <br />It has been found that recycling, the most preferred waste management option aside <br />from waste reduction, increases when VVTEexiste in the United States aswell as in <br />other countries. As shown in 8ioCvzl*'s "2006 State of Garbage in America," <br />(ht±p://vvvvvv.jgpraas.ozrn/archivag/_jrae/000048,htrn|), most of the states with large <br />energy recovery rates have recycling notes higher than the national recycling <br />average of 28.5 percent.' These recycling rates range from 43 percent in Minnesota <br />(where 21 percent ofthe waste is burned for energy) to 24 percent in Connecticut <br />(where 65 percent of the waste is burned for energy). North Carolina illustrates the <br />inverse with 19 percent recycling and '9 percent combustion for energy. <br />Apparently, where VVTE.axists, there is greater public awareness of waste disposal <br />and the need to deal with waste reduction overall. <br />Other methods of MSVV disposal, such as mixed-waste composting and |andfi||ing, <br />are being used but they are becoming less and less attractive. Mixed-waste <br />composting requires large land areas, creates significant odor, and produces compost <br />that is ||nnitad in its application because of contaminants. Landfi||ing is not a <br />processing technology, it is storage. It also requires large land areas or a large <br />capital investment, generates methane (a greenhouse gas that is more than 20 <br />times as potent ascarbon dioxide, which is generated from VVTE), and creates other <br />1 BioQLcle includes recycling, composting,. yard waste, VVTE and landfill collection in its figures. <br />EPA reports MSVV from a slightly different source. They include collection receipts for domestic <br />waste and for industrial waste, but their recycling quantities are derived from firms that <br />recycle the waste, such as paper mills or steel plants, rather than from collection data. This <br />difference in methodology from that used byBioc is reflected in the difference in recycling <br />rates in the United States in 2006, which is reported as 32.5% by EPA and 28.596 byBdZg�cle. <br />GBB/C08027-01. B-1 August 15, 2008 <br />
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