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Mercury emissions from burning of biomass from temperate North American forests: laboratory and airborne measurements

机译:北美温带森林生物质燃烧产生的汞排放:实验室和空中测量

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The emission of mercury from biomass burning was investigated in laboratory experiments and the results confirmed in airborne measurements on a wildfire near Hearst, Ont. Mercury contained in vegetation (live, dead, coniferous, deciduous) was essentially completely released in laboratory burns in the form of gaseous elemental mercury and mercury contained in particles. Replicate burns of dry Ponderosa needles indicated a linear relationship between emitted mercury and fuel mass loss. Regionally collected fuels showed the same behavior as the replicate burns, i.e. essentially total removal of mercury. Mercury released from fuel could be accounted for as gaseous and particulate mercury in the smoke. The mercury content of regionally collected fuels varied between 14 and 70 ng/g on a dry mass (dm) basis. The smoke plume from a small wildfire was investigated with a research aircraft yielding a mean output of 0.15 +/- 0.02 ng/m(3) of elemental mercury for each ppm of CO2 emitted. The particulate mercury determined by sampling at specific points in the plume was <0.083 ng/m(3) compared to elemental mercury of 0.56 ng/m(3) for the same air, supporting the conclusion that most of the mercury was emitted in the gaseous elemental form. Emission factors for the high/low mercury content samples of the laboratory burns were 14-71 x 10(-6) and 112 x 10(-6) g Hg/kg (dm) fuel for the wildfire. The difference is believed to be the contribution of mercury released from fire-heated soil. Mercury budgets extrapolated from this single wildfire gave upper emission limits of 66 t/yr for temperate/boreal forests. This large source estimate must be refined and included in future regional and global models. Forests are sinks for mercury already in the atmosphere, thus the wildfire "source" is part of the overall cycling of mercury originating from other sources. (C) 2002 Elsevier Science Ltd. All rights reserved. [References: 38]
机译:在实验室实验中研究了生物质燃烧过程中汞的排放,并在安大略省赫斯特附近的一场野火的机载测量中证实了该结果。植被(活的,死的,针叶的,落叶的)中所含的汞在实验室燃烧时基本上以气态元素汞和颗粒中所含的汞的形式完全释放。重复干燥的美国黄松针烧伤表明排放的汞与燃料质量损失之间存在线性关系。区域收集的燃料表现出与重复燃烧相同的行为,即基本上完全去除了汞。从燃料中释放出来的汞可以解释为烟雾中的气态和颗粒状汞。按干重(dm)计,区域收集的燃料的汞含量在14至70 ng / g之间。用一架研究飞机对一小场野火产生的烟羽进行了研究,结果表明,每排放一ppm的二氧化碳,平均汞含量为0.15 +/- 0.02 ng / m(3)。在相同的空气中,通过在羽状流中特定点采样确定的颗粒状汞含量为<0.083 ng / m(3),而在相同的空气中,其元素汞含量为0.56 ng / m(3),这支持了以下结论:气态元素形式。实验室燃烧时高/低汞含量样品的排放因子为野火燃料的14-71 x 10(-6)和112 x 10(-6)g Hg / kg(dm)。认为差异是由火加热的土壤释放的汞造成的。从这种单一的野火推断出的汞预算为温带/北方森林的排放上限设定为66吨/年。必须对大量的来源估算进行完善,并将其包括在未来的区域和全球模型中。森林是大气中已经存在的汞汇,因此,野火“源”是源自其他来源的汞总体循环的一部分。 (C)2002 Elsevier Science Ltd.保留所有权利。 [参考:38]

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