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Agenda - 10-07-2008 - 7a
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Agenda - 10-07-2008 - 7a
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4/23/2013 10:37:48 AM
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10/7/2008 12:22:34 PM
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BOCC
Date
10/7/2008
Meeting Type
Regular Meeting
Document Type
Agenda
Agenda Item
7a
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Minutes - 20081007
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Appendix B <br />Overview of Waste Processing Technologies (WPT) <br />1~1 ""Proven" Technologies <br />Waste has been converted to beneficial use on o large scale for well over 100 years. <br />vv�h electric was first to M5VV in 1894 in New <br />Incineration ( known as <br />York City. Sinoathattirn�,theburningofi�SVV vv�henergYnecmvery^no� <br />~~ '' - <br />VTE) has matured into a safe, effective and environmentally acceptable technology. <br />The proven large-scale waste processing <br />methods include incineration and starved- <br />air combustion, as defined below: <br />: This is the controlled combustion of organic or inorganic <br />waste with more than the ideal air /stoiohiornethc1 requirement - excess air - to <br />assure that complete burning occurs. <br />Starved air incineration utilizes less air than conventional <br />incineration, " and it produces similar in appearance <br />to that from a conventional <br />incineration process. The -� so� that result are burne d in a second chamber. The <br />lower air requirement leads to <br />smaller equipment sizes. This process, however, is an <br />incineration process. <br />Refuse-derived Fuel (RD : An RDF system processes waste by shredding it and <br />removing " '~''~~~ metals ' in preparation for combustion. The -removal of non- <br />combustibles can increase the specific heat content by over 1O percent and can allow <br />for revenues from the metals removed. <br />It has been found that recycling, the nmost /neferrod waste mnanagenment option aside <br />from waste reduction, increases when VVT� exists in the United States as well as in <br />other countries' As shown in 8�Cmz�'s "2OO6 State of G <br />arbage in America," (http'//wvw' jgpnyss.00n/archives/_ƒree/OOO84 Q . ht |), mo st of the states with large <br />rates have recycling rates higher than the national recycling <br />energy recovery percent.' These recycling rates range from 43 percent in Minnesota <br />av�ragec��m'� p� . <br />�-- ' - l to percent in Connecticut <br />(where 21 percent of the waste is burned for energy) pa <br />^whe°= O5 percent of the waste is burned for energy). North Carolina illustrates the <br />!,ve-~- with 19 percent recycling and '9 percent combustion for energy' <br />inverse with <br />where VVTE exists, there is greater public awareness of waste disposal <br />and the need to deal with waste reduction overall. <br />Other methods of MBVV disposal, such as mixed-waste composting and |andM||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 limited 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 potentasoarbon dioxide, which is generated from VVTE), and creates other <br />---� <br />1 BI Cycle includes recycling, composting, yard waste, VVTEand|andfiUod|ecdoninhsfigures - <br />EPA reports MGV from a slightly different source. They include coUactonrecaiptsfordonest^ <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 byB�Vg6e is reflected in the difference in recycling <br />rates in the United ~States in 2006, which is reported es32.596 by EPA and 28.596 byBioc���. <br />GBB/CO8027-01 B-1 August 15, 2008 <br />
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