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首页> 外文期刊>Atmospheric Chemistry and Physics Discussions >Formation kinetics and mechanisms of ozone and secondary organic aerosols from photochemical oxidation of different aromatic hydrocarbons: dependence on NO x and organic substituents
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Formation kinetics and mechanisms of ozone and secondary organic aerosols from photochemical oxidation of different aromatic hydrocarbons: dependence on NO x and organic substituents

机译:不同芳烃光化学氧化的臭氧和二次有机气溶胶的形成动力学及机制:依赖NO X和有机取代基

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摘要

Aromatic hydrocarbons (AHs) contribute significantly to ozone and secondary organic aerosol (SOA) formation in the atmosphere, but their formation mechanisms are still unclear. Herein, the photochemical oxidation of nine AHs was investigated in a chamber. Only a small amount of ozone was produced from the direct photochemical oxidation of AHs, while a lower number of AH substituents resulted in higher concentrated ozone. Addition of NO x increased ozone and SOA production. The synergetic effect of accelerated NO 2 conversion and NO reaction with AHs boosted ozone and volatile intermediate formation. Promoting AH concentration in the VOC? / ?NO x ratio further increased formation rates and concentrations of both ozone and SOA. Additionally, ozone formation was enhanced with increasing AH substituent number but negligibly affected by their substituent position. Differently, SOA yield decreased with an increased substituent number of AHs but increased with ortho-methyl-group-substituted AHs. Model fitting and intermediates consistently confirmed that increasing the substituent number on the phenyl ring inhibited generation of dicarbonyl intermediates, which however were preferentially produced from oxidation of ortho-methyl-group-substituted AHs, resulting in different changing trends of the SOA yield. The restrained oligomerization by increased substituent number was another main cause for decreased SOA yield. These results are helpful to understand the photochemical transformation of AHs to secondary pollutants in the real atmosphere.
机译:芳烃(AHS)显着促成大气中的臭氧和二次有机气溶胶(SOA)形成,但它们的形成机制尚不清楚。在此,在腔室中研究了九个AHS的光化学氧化。仅从AHS的直接光化学氧化产生少量臭氧,而均多的均取代基均产生较高的浓度臭氧。添加NO X增加臭氧和SOA生产。加速NO 2转化的协同作用,对AHS的反应增强臭氧和挥发性中间体形成。促进VOC中的浓度? /?NO X比进一步增加的形成速率和臭氧和SOA的浓度。另外,通过增加αh取代基数而是通过其取代基位置疏忽影响的臭氧形成。不同,SOA产率随着取代基的增加而降低,但随着甲基 - 基团取代的AHS增加而增加。模型拟合和中间体一致地证实,增加苯环上的取代基抑制二羰基中间体的产生,然而优先由邻甲基 - 基 - 取代的AHS的氧化产生,导致SOA产量的不同变化趋势。通过增加的取代基数量的抑制的低聚是另一种主要原因,用于降低SOA产量。这些结果有助于了解真实气氛中AHS对次级污染物的光化学转化。

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