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Clean Unit “Comparable to BACT” DeterminationLimitations

机译:清洁单位“与BACT相当”的确定限制

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Facility operators in delegated New Source Review (NSR) and State ImplementationPlan (SIP)-approved states who seek Clean Unit status but have not received a majorNSR permit within the last 10 years, or those who wish to requalify for Clean Unit status,can do so by completing a “comparable-to-BACT” analysis. An emissions unit is“comparable-to-BACT” if it achieves an emission limit that is equal to or better than theaverage of the limits achieved by similar sources for which a BACT determination wasmade in the last five years and is listed in the U.S. Environmental Protection Agency’s(EPA’s) RACT/BACT/LAER Clearinghouse (RBLC). This approach seemsstraightforward, but can yield misleading results without additional research of theemission limits listed in the RBLC.A recent permitting project involving a coal-fired boiler illustrates the details that must beevaluated when conducting a “comparable-to-BACT” analysis. The facility operatorcompleted a “comparable-to-BACT” analysis for PM10 emissions using the methodspecified in the rule. However, the preliminary findings of this analysis were incomplete.The RBLC does not include the test methods on which the emission limits are based.Until recently, many construction permits for coal-fired boilers did not require theinclusion of condensible PM in the total PM10 emission limits. The condensible fractionof PM10 can significantly contribute to the total PM10. Further, many projects have beenpermitted but not tested and therefore did not meet the “demonstrated to be achieved”criteria of the rule. Test methods can have a significant effect on the emission limit. Itwas determined that the original “comparable-to-BACT” test methods included severalemission limits that were based on different test methods than that proposed by thefacility; therefore, not all the units qualify as “comparable” units for the purpose of theClean Unit determination test.This paper uses a Clean Unit project as a case study to illustrate the limitations ofcompleting a “comparable-to-BACT” determination using only information from theRBLC.
机译:在授权的新源审查(NSR)和州实施计划(SIP)批准的州中,希望获得清洁单位资格但在过去10年内未获得主要NSR许可的工厂的操作员,或者希望重新获得清洁单位资格的人员可以因此可以完成“可比BACT”分析。如果排放单位达到的排放限值等于或优于过去五年中做出BACT测定并已在美国环境中列出的类似来源所达到的限值的平均值,则该排放单位为“可比BACT”。保护局(EPA)的RACT / BACT / LAER信息交换所(RBLC)。这种方法看似直截了当,但如果不对RBLC中列出的排放限值进行进一步研究,便会产生误导性的结果。最近一项涉及燃煤锅炉的许可项目说明了进行“可比BACT”分析时必须评估的细节。设施操作员使用规则中指定的方法完成了PM10排放的“可比BACT”分析。但是,该分析的初步结果并不完整.RBLC还没有包括排放限值所依据的测试方法。直到最近,许多燃煤锅炉的施工许可证并未要求将可冷凝PM包含在PM10的总排放中限制。 PM10的可冷凝部分可对总PM10做出重大贡献。此外,许多项目已获准但未经测试,因此不符合规则的“证明可实现”标准。测试方法可能会对排放限值产生重大影响。已经确定,原始的“可比性”测试方法包括多个排放限值,这些限值基于与工厂建议的测试方法不同的测试方法;因此,并非所有单位都可以用于“清洁单位确定”测试。本文使用“清洁单位”项目作为案例研究,以说明仅使用来自以下方面的信息来完成“可与BACT”确定的局限性RBLC。

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