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通过连续监测设备测量的废物燃烧大气汞排放。

Atmospheric mercury emissions from waste combustions measured by continuous monitoring devices.

机构信息

Faculty of Urban and Environmental Engineering, Graduate School of Engineering, Kyushu University, 744 Motooka, Nishi-ku, Fukuoka 819-0395, Japan.

出版信息

J Air Waste Manag Assoc. 2012 Jun;62(6):686-95. doi: 10.1080/10962247.2012.659329.

Abstract

Atmospheric mercury emissions have attracted great attention owing to adverse impact of mercury on human health and the ecosystem. Although waste combustion is one of major anthropogenic sources, estimated emission might have large uncertainty due to great heterogeneity of wastes. This study investigated atmospheric emissions of speciated mercury from the combustions of municipal solid wastes (MSW), sewage treatment sludge (STS), STS with waste plastics, industrial waste mixtures (IWM), waste plastics from construction demolition, and woody wastes using continuous monitoring devices. Reactive gaseous mercury was the major form at the inlet side of air pollution control devices in all combustion cases. Its concentration was 2.0-70.6 times larger than elemental mercury concentration. In particular, MSW, STS, and IWM combustions emitted higher concentration of reactive gaseous mercury. Concentrations of both gaseous mercury species varied greatly for all waste combustions excluding woody waste. Variation coefficients of measured data were nearly equal to or more than 1.0. Emission factors of gaseous elemental mercury, reactive gaseous mercury, and total mercury were calculated using continuous monitoring data. Total mercury emission factors are 0.30 g-Hg/Mg for MSW combustion, 0.21 g-Hg/Mg for STS combustion, 0.077 g-Hg/Mg for STS with waste plastics, 0.724 g-Hg/Mg for industrial waste mixtures, 0.028 g-Hg/Mg for waste plastic combustion, and 0.0026 g-Hg/Mg for woody waste combustion. All emission factors evaluated in this study were comparable or lower than other reported data. Emission inventory using old emission factors likely causes an overestimation.

摘要

大气汞排放因其对人类健康和生态系统的不利影响而受到极大关注。尽管废物燃烧是人为汞排放的主要来源之一,但由于废物的高度异质性,估计的排放量可能存在很大的不确定性。本研究使用连续监测设备,调查了城市固体废物(MSW)、污水处理污泥(STS)、含废塑料的 STS、工业废物混合物(IWM)、建筑拆除废物塑料和木质废物燃烧过程中 Hg 的形态排放。在所有燃烧情况下,空气污染物控制设备的入口侧均以气态活性汞为主要形态。其浓度是元素汞浓度的 2.0-70.6 倍。特别是 MSW、STS 和 IWM 燃烧排放出更高浓度的气态活性汞。除木质废物外,所有废物燃烧的两种气态汞形态浓度变化均较大。测量数据的变异系数几乎等于或大于 1.0。使用连续监测数据计算了气态元素汞、气态活性汞和总汞的排放因子。MSW 燃烧的总汞排放因子为 0.30 g-Hg/Mg,STS 燃烧的总汞排放因子为 0.21 g-Hg/Mg,含废塑料的 STS 燃烧的总汞排放因子为 0.077 g-Hg/Mg,工业废物混合物燃烧的总汞排放因子为 0.724 g-Hg/Mg,废塑料燃烧的总汞排放因子为 0.028 g-Hg/Mg,木质废物燃烧的总汞排放因子为 0.0026 g-Hg/Mg。本研究评估的所有排放因子均与其他报告的数据相当或更低。使用旧的排放因子进行排放清单编制可能会导致高估。

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