Orange County NC Website
Executive Summary <br />This examination of alternative waste processing technologies (N[T) was undertaken <br />at the behest of the Orange County Board of Commissioners to explore and evaluate <br />alternatives to landfill disposal of the County's municipal solid waste. The purpose of <br />this white paper is to initiate that evaluation and brief the County's solid waste staff, <br />elected officials, Solid Waste Advisory Board, and citizens on state-of-the-art solid <br />waste processing technologies, emerging technologies and their applicability to the <br />County's needs, and the potential of these technologies to contribute to the County's <br />overall solid waste management system. <br />Orange County generated approximately 116,000 tons of waste in FY2006-07, or <br />about 318 tons per day (TPD). Of that material, 62,800 tons or 172 TPD were <br />disposed of in |a'-�||�, an^ 29'�OO tons or 24 percent was naoyded' The County is <br />��- ' <br />examining ways to achieve its goal of 61 percen t waste reduction, up from their <br />current rate of4Q percent. The County's landfill is projected to close in 2011. The <br />County has decided to manage its future waste using a transfer station and <br />contracting for disposal in an out-of-County landfill as well as examining the <br />feasibility of alternatives. <br />Traditional waste processing technologies now in operation have the potential of <br />managing most of the County's non-recycled waste. Generally, VVTE plants reduce <br />the processed waste tonnage by 75 percent and the volume by 90 percent. This <br />leaves residue, ash, which needs to be |andfi||ed in a permitted Subtitle D landfill. <br />In some states, ash may be used beneficially as alternative daily cover atlandfills. <br />Even at 75 percent reduction by weight, a \NTEfaci|ity has dramatic effect on the <br />amount ofresidual waste. <br />This report examines both proven and unproven waste processing technologies. <br />Table A-2 in the Appendices provides a ' comparison of these various technologies. <br />Waste-to-energy (VVTEl technologies profiled include: rnass-burn/watenwa|| <br />^ ^ <br />combustion, mass-burn/modular combustion, refuse-derived fuel (RDF)/dedicated <br />boi|ar, and KDF/Ouid bed. Although VVTE plants range in size from 10 to 3,000 TPD <br />in the ~U.S., 71 percent are 500 TPD or larger. Mass-burn/vvabsnwa|| combustion is <br />.the �most prevalent V <br />PT in the U . S .' employed at GS of the 89 facilities. <br />However, <br />no new mass-b-rnVTE facilities have been built in the U.S. for over ten years. Ten <br />VTEfad|ities currently operate in the Mid-Atlantic States region, processing almost <br />12'000 TPD- North Carolina, New Hanover County owns e 500 TPD plant that <br />produces electricity. In contrast to its smaller presence in the U.S., VTE is an <br />accepted and commonly used waste processing technology worldwide, with 400 <br />facilities i <br />Europe, 100 in Japan, and 70 in other nations such as Taiwan, Singapore, <br />and China. <br />In addition to proven technologies, this report examines the emerging technologies <br />of high-temperature gasification, fluidized-bed combustion, plasma-arc processing, <br />non-thermal anaerobic digestion, and biological fuel production. Although technically <br />not an emerging technology, biological fuel production has not been cornrnmroia||y <br />proven using MSVV as feedstock. <br />The historical and current context for development and use of VVTE in the U.S. is <br />explored, with waste processing technologies currently receiving renewed interest <br />due to: the proven VVTEtrock record, increasing fossil fuel costs, growing interest in <br />renewable energy, a higher ranking in the EPA's waste -rnanagamnent hierarchy, <br />GBB/CO8027-01 ES-1 August 15, 2008 <br />