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首页> 外文会议>11th Annual North American Waste to Energy Conference Apr 28-30, 2003 Tampa, Florida >HOW IMPLEMENTATION OF RETROFITS REQUIRED BY THE CLEAN AIR ACT AMENDMENTS OF 1990 AFFECTS WASTE-TO-ENERGY FACILITY OPERATIONS, PLANT EFFICIENCY AND FINANCES
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HOW IMPLEMENTATION OF RETROFITS REQUIRED BY THE CLEAN AIR ACT AMENDMENTS OF 1990 AFFECTS WASTE-TO-ENERGY FACILITY OPERATIONS, PLANT EFFICIENCY AND FINANCES

机译：如何实施1990年的《清洁空气法》修正案所规定的改造措施，以影响废物转为能源的设施运营，工厂效率和财务状况

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摘要

This paper considers the direct and indirect impacts on facility operations and financial performance resulting from the retrofits required to comply with the tighter emissions standards and more stringent operating requirements imposed by the Clean Air Act Amendments of 1990 (CAAA). While all large municipal waste combustors (>250 tons per day) and many smaller units (<250 TPD) have already made the initial financial and operational adjustments required by CAAA-induced changes, many small combustors preparing to comply with the Subpart BBBB requirements, have yet to experience these changes. Since most large WTE facilities only began operating under the new CAAA scenario during or shortly before December 2000, the long-term cost impacts of these changes are only now becoming clear. The Subpart BBBB standards are nearly identical to the standards imposed on large combustors. Each existing WTE facility operator affected by Subpart BBBB must determine whether the standards can be met with existing air pollution control devices and existing emission monitoring equipment, or if a facility retrofit is required. If a facility retrofit is required, the economics of continued operation as compared to alternative disposal options must be considered.
机译：本文考虑了为满足更严格的排放标准和1990年《清洁空气法修正案》（CAAA）规定的更严格的运行要求而进行的改造对设施运营和财务绩效的直接和间接影响。尽管所有大型市政垃圾燃烧器（每天超过250吨）和许多较小的焚化炉（<250 TPD）已经进行了CAAA诱导的变更所需的初始财务和运营调整，但许多小型燃烧器准备遵守BBBB子部分的要求，尚未经历这些变化。由于大多数大型WTE设施仅在2000年12月或之前在新的CAAA方案下开始运行，因此这些变化的长期成本影响现在才变得清晰起来。 Subpart BBBB标准几乎与强加于大型燃烧器的标准相同。受BBBB分部影响的每个现有的WTE设施运营商必须确定是否可以通过现有的空气污染控制设备和现有的排放监测设备满足标准，或者是否需要对设施进行改造。如果需要对设施进行改造，则必须考虑与替代处置方案相比，持续运行的经济性。

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