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Widespread and persistent ozone pollution in eastern China during the non-winter season of 2015: observations and source attributions

机译:2015年非冬季中国东部地区臭氧的广泛且持续的污染:观测资料和污染源

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Rapid growth of industrialization, transportation, and urbanization has caused increasing emissions of ozone (Osub3/sub) precursors recently, enhancing the Osub3/sub formation in eastern China. We show here that eastern China has experienced widespread and persistent Osub3/sub pollution from April to September 2015 based on the Osub3/sub observations in 223 cities. The observed maximum 1?h Osub3/sub concentrations exceed 200?μg?msup?3/sup in almost all the cities, 400?μg?msup?3/sup in more than 25?% of the cities, and even 800?μg?msup?3/sup in six cities in eastern China. The average daily maximum 1?h Osub3/sub concentrations are more than 160?μg?msup?3/sup in 45?% of the cities, and the 1?h Osub3/sub concentrations of 200?μg?msup?3/sup have been exceeded on over 10?% of days from April to September in 129 cities. Analyses of pollutant observations from 2013 to 2015 have shown that the concentrations of CO, SOsub2/sub, NOsub2/sub, and PMsub2.5/sub from April to September in eastern China have considerably decreased, but the Osub3/sub concentrations have increased by 9.9?%. A widespread and severe Osub3/sub pollution episode from 22 to 28 May 2015 in eastern China has been simulated using the Weather Research and Forecasting model coupled to chemistry (WRF-CHEM) to evaluate the Osub3/sub contribution of biogenic and various anthropogenic sources. The model generally performs reasonably well in simulating the temporal variations and spatial distributions of near-surface Osub3/sub concentrations. Using the factor separation approach, sensitivity studies have indicated that the industry source plays the most important role in the Osub3/sub formation and constitutes the culprit of the severe Osub3/sub pollution in eastern China. The transportation source contributes considerably to the Osub3/sub formation, and the Osub3/sub contribution of the residential source is not significant generally. The biogenic source provides a background Osub3/sub source, and also plays an important role in the south of eastern China. Further model studies are needed to comprehensively investigate Osub3/sub formation for supporting the design and implementation of Osub3/sub control strategies, considering rapid changes of emission inventories and photolysis caused by the Atmospheric Pollution Prevention and Control Action Plan released by the Chinese State Council in 2013.
机译:工业化,交通运输和城市化的快速发展导致最近臭氧(O 3 )前体的排放增加,从而加剧了中国东部O 3 的形成。根据223个城市的O 3 观测值,我们在此表明​​,从2015年4月至9月,中国东部地区经历了广泛而持续的O 3 污染。在几乎所有城市中,观察到的最大1?h O 3 浓度都超过200?μg?m ?3 ,400?μg?m ?3 在超过25%的城市中,甚至在中国东部的六个城市中达到800?μg?m ?3 。在45%的城市中,平均每日最大1?h O 3 浓度超过160?μg?m ?3 ,而1?h O 3 浓度超过200?μg?m ?3 。 2013年至2015年的污染物观测分析表明,4月至9月的CO,SO 2 ,NO 2 和PM 2.5 的浓度中国东部的O 3 浓度已大大降低,但增加了9.9?%。使用天气研究与天气预报模型结合化学(WRF-CHEM)对O 3进行评估,模拟了2015年5月22日至28日在中国东部发生的一次广泛而严重的O 3 污染事件对生物和各种人为来源的贡献。该模型在模拟近地表O 3 浓度的时间变化和空间分布方面通常表现良好。使用因子分离方法,敏感性研究表明,工业来源在O 3 的形成中起着最重要的作用,并且是东部O 3 严重污染的罪魁祸首。中国。运输来源对O 3 的贡献很大,而住宅来源的O 3 的贡献一般不大。该生物源提供了背景O 3 源,并且在中国东部南部也起着重要作用。需要进一步的模型研究来全面研究O 3 的形成,以支持O 3 控制策略的设计和实施,同时考虑到大气污染引起的排放清单的快速变化和光解。国务院于2013年发布的《防治行动计划》。

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