Secondary organic aerosol formation and transport — II. Predicting the ambient secondary organic aerosol size distribution

Spyros N. Pandis , Anthony S. Wexler , John H. Seinfeld
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引用次数: 144

Abstract

The size distribution of atmospheric secondary organic aerosol is simulated by a Lagrangian trajectory model that includes descriptions of gas-phase chemistry, inorganic and organic aerosol thermodynamics, condensation/evaporation of aerosol species, dry deposition and emission of primary gaseous and particulate pollutants. The model is applied to simulate the dynamics of aerosol size and composition along trajectories on 27–28 August 1987 during the Southern California Air Quality Study (SCAQS). The secondary organic aerosol material is predicted to condense almost exclusively on the submicron aerosol in agreement with the available measurements, and its size distribution for Claremont, CA, is predicted to be unimodal with a mass mean diameter of roughly 0.2 μm. The distributions of the various secondary organic aerosol species are predicted to be essentially the same. The secondary organic aerosol (SOA) size distribution is found to depend crucially on the mass and size distribution of primary aerosol on which the secondary species condense and on the surface accomodation coefficient of the condensable species. The SOA size distribution is predicted not to be significantly affected by diffusional dry deposition, sources and sinks of ammonia, emissions of VOC, and secondary aerosol yields from precursor hydrocarbons. A bimodal secondary organic aerosol size distribution is predicted only if the submicron primary dust particles reside mainly in the 0.5–1.0 μm diameter size range, or if the condensable species have a strong preference (an accomodation coefficient difference of two orders of magnitude) for the 0.5–1.0 μm diameter particles. The secondary organic aerosol distribution in Claremont is predicted to shift slightly towards the larger aerosol particles during the nighttime hours with it mass mean diameter peaking around midnight at 0.21 μm and having its minimum in early afternoon at 0.18 μm. In coastal locations of the Los Angeles basin, secondary organic material exists in relatively smaller particles (mass mean diameter 0.16 μm) but in far inland locations it condenses on the available larger particles (mass mean diameter 0.23 μm).

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二次有机气溶胶的形成和输送- 2。环境二次有机气溶胶粒径分布预测
采用拉格朗日轨迹模型模拟了大气中二次有机气溶胶的大小分布,该模型包括气相化学、无机和有机气溶胶热力学、气溶胶种类的冷凝/蒸发、主要气体和颗粒污染物的干沉积和排放。该模式用于模拟1987年8月27日至28日南加州空气质量研究(SCAQS)期间沿轨迹的气溶胶大小和成分的动力学。预测二次有机气溶胶物质几乎完全凝结在亚微米气溶胶上,这与现有的测量结果一致,并且其尺寸分布在Claremont, CA,预测为单峰分布,质量平均直径约为0.2 μm。预测各种次生有机气溶胶种类的分布基本相同。发现二级有机气溶胶(SOA)的大小分布主要取决于二级物质凝结在其上的初级气溶胶的质量和大小分布以及可凝结物质的表面调节系数。预计SOA大小分布不会受到扩散干沉降、氨源和汇、挥发性有机化合物排放和前体碳氢化合物产生的二次气溶胶的显著影响。只有当亚微米一级粉尘颗粒主要分布在0.5 ~ 1.0 μm直径范围内,或者可冷凝物质对0.5 ~ 1.0 μm直径颗粒有强烈的偏好(调节系数相差两个数量级)时,才能预测二次有机气溶胶的双峰分布。Claremont地区的二次有机气溶胶分布在夜间略有向较大的气溶胶颗粒偏移,其质量平均直径在午夜左右达到峰值,为0.21 μm,在下午早些时候达到最小值,为0.18 μm。在洛杉矶盆地的沿海地区,二次有机物以相对较小的颗粒(质量平均直径0.16 μm)存在,但在较远的内陆地区,它凝结在可用的较大颗粒(质量平均直径0.23 μm)上。
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