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[臭氧及其他光化学氧化剂的形成与传输]

[Formation and transport of ozone and other photochemical oxidants].

作者信息

Moser W

出版信息

Soz Praventivmed. 1986;31(1):48-52. doi: 10.1007/BF02103750.

DOI:10.1007/BF02103750
PMID:3962505
Abstract

Photochemical oxidants (O3, PAN, HCHO) are the typical pollutants in photochemical Smog. They can be formed as the result of the sunlight induced oxidation of precursor pollutants emitted into the atmosphere (NOx, CxHy). Other important precursor substances and reactive intermediates are compounds of the organic hydroxyl group (-O-H, for instance the methoxy radical CH3O), hydroxyl radical .OH, hydroperoxy radical HO2, and singlet oxygen O. For the production of photochemical oxidants in smog, especially ozone, NOx primarily act as catalysator. But CxHy serve as "combustibles". The quantities of the several formed photooxidants are mainly dependent on intensity and duration of daily sunshine, temperature, oxidant concentrations at the beginning of a build-up period, and on emission rates and concentrations of primary pollutants (NO, CxHy). Maximum mixing ratios of secondary pollutants often occur at certain distances downwind of primary pollutant sources, dependent on meteorological conditions (wind velocity, rel. humidity, etc.) and on rate constants for oxidant formation cycles. During the period of July 5 to 11, 1984, for instance, 6 kilometers SW from Zürich we found maximum ground-level mixing ratios of about 150 ppbv ozone, 4 ppbv PAN and 9 ppbv formaldehyde, that is 5 (ozone) to 10 (PAN) times above the supposed oxidant concentrations of unpolluted continental air. The increase in ozone in the late morning and early afternoon is accompanied by an increase in PAN and HCHO and by a decrease in NOx. This shows that in this case HCHO originates from photochemical reactions rather than being emitted directly to the atmosphere from vehicles.(ABSTRACT TRUNCATED AT 250 WORDS)

摘要

光化学氧化剂(臭氧、过氧乙酰硝酸酯、甲醛)是光化学烟雾中的典型污染物。它们可由排放到大气中的前驱污染物(氮氧化物、碳氢化合物)在阳光诱导下氧化形成。其他重要的前驱物质和反应中间体是有机羟基化合物(-O-H,例如甲氧基自由基CH3O)、羟基自由基·OH、氢过氧自由基HO2和单线态氧O。对于烟雾中光化学氧化剂的产生,尤其是臭氧,氮氧化物主要起催化剂的作用。但碳氢化合物充当“可燃物”。几种形成的光氧化剂的数量主要取决于每日日照的强度和持续时间、温度、积累期开始时的氧化剂浓度,以及一次污染物(NO、碳氢化合物)的排放速率和浓度。二次污染物的最大混合比通常出现在一次污染源下风方向的特定距离处,这取决于气象条件(风速、相对湿度等)和氧化剂形成循环的速率常数。例如,在1984年7月5日至11日期间,在苏黎世西南6公里处,我们发现地面臭氧最大混合比约为150 ppbv,过氧乙酰硝酸酯为4 ppbv,甲醛为9 ppbv,即比未受污染的大陆空气假定的氧化剂浓度高出5(臭氧)至10(过氧乙酰硝酸酯)倍。上午晚些时候和下午早些时候臭氧的增加伴随着过氧乙酰硝酸酯和甲醛的增加以及氮氧化物的减少。这表明在这种情况下,甲醛源自光化学反应,而非直接从车辆排放到大气中。(摘要截取自250词)

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