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A New Modelling Strategy for Secondary Organic Aerosols

机译:二次有机气溶胶的新建模策略

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摘要

In recent years, air quality issues related to airborne particulate matter (PM), or aerosols, have received increasing attention of regulatory agencies, scientific community, and industry due to the adverse health and environmental effects caused by aerosols. In general, atmospheric aerosols are liquid and/or solid mixtures of nitrate, sulphate, ammonia, elemental carbon, organics, and mineral materials. While some of the aerosol components are directly emitted by various sources (primary aerosols), the components that are secondarily formed in the atmosphere (secondary aerosols) are also important contributors to the total atmospheric aerosol loading and to the adverse effects caused by aerosols. The formation of secondary aerosols, especially secondary organic aerosols (SOA), involves extremely complicated chemical and physical processes in the atmosphere. The composition of SOAs is complex and varies widely. Typical SOAs contain hundreds of organic species. The organic species are formed through gas phase reactions of emitted volatile organic compounds (VOC) with various oxidants and are transferred to existing particles through condensation, and possible nucleation, processes. Major components of SOAs include mostly high molecular weight, low vapour pressure organic species. The species normally contain oxygen — or nitrogen - containing functional groups. Because of their low vapour pressure, bi — or multi — functional compounds are some key species found in SOAs (Seinfeld and Pandis 1998; National Research Council 1977; Knoighs et al., 1975; Schuetzle et al., 1975; 1973; Schuetzle, 1972). VOCs that are most probable SOA precursors incldue olefins, especially cyclic olefins and diolefins (Hoffmann et al., 1997; Hatakeyama et al., 1987; Hatakeyama et al., 1985; Kamens et al., 1982. ), and high molecular weight olefins (Forstner et al., 1997a); aromatics, especially substituted aromatics (Forstner et al., 1997b; Odum et al., 1997; Izumi and Fukuyama, 1990); long chain alkanes; and other long chain and high molecular weight VOCs, such as high molecular weight carbonyls or carboxylic acids.
机译:近年来,由于气溶胶造成的不利健康和环境影响,与空气传播颗粒物质(PM)或气溶胶相关的空气质量问题受到监管机构,科学界和工业的影响。通常,大气气溶胶是硝酸液和/或固体混合物,硫酸盐,氨,元素碳,有机物和矿物质。虽然一些气溶胶组分由各种来源(原发性气溶胶)直接发射,但在大气中(二次气溶胶)二次形成的组分也是总大气气溶胶加载的重要贡献者和气溶胶引起的不利影响。二次气溶胶的形成,特别是二次有机气溶胶(SOA),涉及大气中非常复杂的化学和物理过程。 SOA的组成是复杂的,并且广泛变化。典型的SOA包含数百种有机物种。通过具有各种氧化剂的发射挥发性有机化合物(VOC)的气相反应形成有机物质,并通过缩合转移到现有颗粒中,以及可能的核心,方法。 SOA的主要成分包括大多数高分子量,低​​蒸气压有机物质。该物种通常含有含氧或含氮的官能团。由于它们的蒸气压低,Bi - 或多功能化合物是SOAS(Seinfeld和Pandis 1998中的某些关键物种; 1977年国家研究理事会; Knoighs等,1975; Schuetzle等,1975; Schuetzle, 1972)。 VOCS是最可能的SOA前体INCLVUE烯烃,特别是环烯烃和Diolefins(Hoffmann等,1997; Hatakeyama等,1987; Hatakeyama等,1985; Kamens等,1982.)和高分子量烯烃(Forstner等,1997a);芳烃,特别是取代的芳烃(Forstner等,1997b; Odum等,1997; Izumi和Fukuyama,1990);长链烷烃;和其他长链和高分子量VOC,如高分子量羰基或羧酸。

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