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首页> 外文期刊>Atmospheric chemistry and physics >Submicron aerosol source apportionment of wintertime pollution in Paris, France by double positive matrix factorization (PMFsup2/sup) using an aerosol chemical speciation monitor (ACSM) and a multi-wavelength Aethalometer
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Submicron aerosol source apportionment of wintertime pollution in Paris, France by double positive matrix factorization (PMFsup2/sup) using an aerosol chemical speciation monitor (ACSM) and a multi-wavelength Aethalometer

机译:使用气溶胶化学形态监测器(ACSM)和多波长测空仪通过双重正矩阵分解(PMF 2 )对法国巴黎的冬季污染进行亚微米气溶胶源分配

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Online non-refractory submicron aerosol mass spectrometer (AMS) measurementsin urban areas have successfully allowed the apportionment of specificsources and/or physical and chemical properties of the organic fraction.However, in order to be fully representative of PM pollution, acomprehensive source apportionment analysis is needed by taking into accountall major components of submicron aerosols, creating strengthened bondsbetween the organic components and pollution sources. We present here anovel two-step methodology to perform such an analysis, by taking advantageof high time resolution of monitoring instruments: the aerosol chemicalspeciation monitor (ACSM) and the multi-wavelength absorption measurements(Aethalometer AE31) in Paris, France. As a first step, organic aerosols (OA)were deconvolved to hydrocarbon-like OA (HOA), biomass burning OA (BBOA)and oxygenated OA (OOA) with positive matrix factorization (PMF), and black carbonwas deconvolved into its wood burning and fossil fuel combustion fractions.A second PMF analysis was then carried out with organic factors, BCfractions and inorganic species (nitrate, sulfate, ammonium, chloride),leading to a four-factor solution allowing highly time-resolvedcharacterization of the major sources of PM1. Outputs of thisPMF2 include two dominant combustion sources (wood burningand traffic) as well as semi-volatile and low-volatile secondary aerosols.While HOA is found to be emitted by both wood burning and traffic, thelatter sources occurred to significantly contribute also to OOA.
机译:在线非耐火材料亚微米气溶胶质谱仪(AMS)在城市地区的测量已成功地允许对特定来源和/或有机馏分的物理和化学性质进行分摊,但是,为了完全代表PM污染,需要进行全面的源分摊分析通过考虑亚微米气溶胶的所有主要成分,在有机成分和污染源之间建立加强的结合来满足需要。我们在这里展示利用两步法进行分析的方法,它利用了监测仪器的高时间分辨率:法国巴黎的气溶胶化学形态监测仪(ACSM)和多波长吸收测量(Aethalometer AE31)。第一步,将有机气溶胶(OA)分解为类似烃的OA(HOA),将生物质燃烧OA(BBOA)和含氧的OA(OOA)分解为正矩阵分解(PMF),将黑色碳分解为木材燃烧和分解。然后使用有机因子,BC馏分和无机物(硝酸盐,硫酸盐,铵,氯化物)进行第二次PMF分析,从而得到四因子溶液,可对主要PM < sub> 1 。 PMF 2 的输出包括两个主要燃烧源(木材燃烧和交通)以及半挥发性和低挥发性二次气溶胶。虽然发现HOA既由木材燃烧又由交通排放​​,但其他来源发生也显着地促进了OOA。

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