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PM2.5 From Gas Combustion: Emissions Characterization Issues and Speciation Results

机译:气体燃烧产生的PM2.5:排放特征问题和形成结果

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Reliable PM2.5 source apportionment will require accurate inventories of speciated emissionsrnfrom stationary sources. Although gas combustion is typically thought of as a "clean" process, thernenormous quantities of gas burned in boilers, process heaters, and engines potentially makes evenrnsmall pollutant concentrations significant. Tests were performed on a gas-fired industrial boilerrnand a gas-fired process heater at different oil refineries to characterize air emissions contributingrnto fine particulate matter in the ambient air.rnTotal particulate, PM10 and PM2.5 were measured using in-stack cyclones followed by an instackrnquartz filter at stack temperature (EPA Method 201A). Downstream of the filter, thernsample was passed through a series of impingers in an ice bath (EPA Method 202) to collect bothrnfine particles which pass through the filter and aerosols which condense at the temperature of therngas leaving the impingers (typically 60-70°F). PM2.5 mass and chemical speciation also wererndetermined using a dilution tunnel and ambient air sampling/analytical methods. The dilutionrntunnel included an aging chamber which provided a total system bulk residence time ofrnapproximately 80 seconds to ensure representative sampling of organic aerosols.rnThe amount of filterable particulate collected using the in-stack methods was essentially near orrnbelow the overall method detection limit. However, condensable particulate matter (CPM) asrndefined by EPA Method 202 was measured at much higher levels. Analysis of the impingerrncontents from the boiler test suggests a large fraction of the measured CPM can be accounted forrnin sulfates and chlorides; however, the mass of sulfates in the impingers was much greater than inrnthe dilution tunnel samples. Laboratory results indicate most of this can be accounted for byrnoxidation of gaseous SO2 in the impingers leading to a positive bias in the results. These resultsrnindicate the potential for a large positive bias in the existing emission inventory for PM2.5rn(which is based on EPA methods) from gas fired stationary sources.
机译:可靠的PM2.5排放源分配需要准确的固定源特定排放清单。尽管通常将气体燃烧视为“清洁”过程,但锅炉,过程加热器和发动机中燃烧的大量气体有可能使很小的污染物浓度变得明显。在不同的炼油厂对燃气工业锅炉和燃气过程加热器进行了测试,以表征造成环境空气中细颗粒物排放的空气.rn使用烟囱内旋风除尘器测量总颗粒物,PM10和PM2.5烟囱温度下的烟囱石英过滤器(EPA方法201A)。在过滤器的下游,使样品通过冰浴中的一系列撞击器(EPA方法202),以收集通过过滤器的细颗粒和在离开撞击器的温度(通常为60-70°F)下冷凝的气溶胶。 )。还使用稀释隧道和环境空气采样/分析方法确定了PM2.5的质量和化学形态。稀释隧道包括一个老化室,该老化室提供了大约80秒的总系统总体停留时间,以确保对有机气溶胶进行有代表性的采样。使用堆叠式方法收集的可过滤颗粒物的量基本上接近或低于总体方法检测极限。但是,EPA方法202定义的可冷凝颗粒物(CPM)的含量要高得多。对锅炉测试中含浸量的分析表明,测得的每千次展示费用中有很大一部分是硫酸盐和氯化物。但是,撞击器中的硫酸盐质量比稀释隧道样品中的硫酸盐质量大得多。实验室结果表明,其中大部分可归因于撞击器中气态SO2的过氧化,导致结果呈正偏。这些结果表明,来自燃气固定源的PM2.5rn(基于EPA方法)的现有排放清单可能存在较大的正偏差。

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