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[中国中部地区空气污染的一年模拟、18个城市的特征、分布、区域内交叉传输及路径研究]

[One-year Simulation of Air Pollution in Central China, Characteristics, Distribution, Inner Region Cross-transmission, and Pathway Research in 18 Cities].

作者信息

Liu Guang-Jin, Su Fang-Cheng, Xu Qi-Xiang, Zhang Rui-Qin, Wang Ke

机构信息

College of Chemistry, Zhengzhou University, Zhengzhou 450001, China.

Research Institute of Environmental Science, Zhengzhou University, Zhengzhou 450001, China.

出版信息

Huan Jing Ke Xue. 2022 Aug 8;43(8):3953-3965. doi: 10.13227/j.hjkx.202111126.

DOI:10.13227/j.hjkx.202111126
PMID:35971694
Abstract

Air pollution in Henan province is serious and is significantly impacted by pollution transmission and interactions with surrounding areas. The emission sources in 18 cities in Henan province were labeled and applied to the WRF-CMAQ traceability model for simulation in January, April, July, and October of 2017. The pollutant distribution results showed that due to the combined influence of emissions and meteorology, the concentrations of PM, NO, and SO in Henan province were the highest in winter and the lowest in summer. The seasonal variation in O-8h concentration was the highest in summer, followed by spring, and the lowest in winter. There was a large difference in pollutant concentrations between different seasons. The average concentrations of PM, NO, and SO in winter in Henan province were 4.17, 4.12, and 6.24 times those in summer, respectively, whereas the concentration of O-8h in summer was 2.24 times that in winter. Since PM, NO, and SO are closely related to primary emissions and have a certain homology, the distributions of high values of these three pollutants were higher in the north and lower in the south, and the seasonal trends were more consistent. The seasonal distribution of O-8h varied widely, with high O-8h values mainly distributed in the northeastern region of Henan province in summer, when meteorological conditions contributed to O production; in winter, spring, and autumn, high O-8h values were mainly distributed in the southern part of Henan province due to the suppression of meteorological conditions and NO consumption. The results of the study on the transport of pollutants showed that extra-provincial transport and natural sources contributed the most to the concentrations of PM, O-8h, NO, and SO in winter, with 36.20%-72.32%, 77.96%-96.08%, 49.45%-78.80%, and 59.05%-88.85%, respectively. When considering only local emissions and intra-provincial transmission, the contributions of emissions to local concentrations of the four pollutants in summer were the highest in all cities of Henan province. The contributions of intra-provincial transmission to PM and O-8h in spring were the largest, with 25.63%-74.69% and 30.21%-80.01%, respectively, and the contributions of intra-provincial transmission to NO and SO in winter were larger, with 26.02%-76.96% and 20.30%-82.34%. The transmission paths of PM, NO, and SO were more similar in Henan province, with more transmission from north to south in winter, from west to east and southwest to northeast in spring, from southwest to northeast in summer, and from north to south in autumn; however, the transmission of PM was more complicated. The O-8h transport path was more different from the others, especially in autumn when pollutants were mostly transported from north to south, but the O-8h transport path from southwest to northeast was obvious.

摘要

河南省空气污染严重,受污染传输及与周边地区相互作用的影响显著。对河南省18个城市的排放源进行了标记,并应用于WRF-CMAQ溯源模型,于2017年1月、4月、7月和10月进行模拟。污染物分布结果表明,受排放和气象条件共同影响,河南省PM、NO和SO浓度冬季最高,夏季最低。O-8h浓度的季节变化夏季最高,其次是春季,冬季最低。不同季节污染物浓度差异较大。河南省冬季PM、NO和SO的平均浓度分别是夏季的4.17倍、4.12倍和6.24倍,而夏季O-8h浓度是冬季的2.24倍。由于PM、NO和SO与一次排放密切相关且具有一定同源性,这三种污染物高值分布北高南低,季节趋势较为一致。O-8h的季节分布差异较大,夏季O-8h高值主要分布在河南省东北部地区,此时气象条件利于O生成;冬季、春季和秋季,由于气象条件抑制和NO消耗,O-8h高值主要分布在河南省南部。污染物传输研究结果表明,冬季省外传输和自然源对PM、O-8h、NO和SO浓度的贡献最大,分别为36.20%-72.32%、77.96%-96.08%、49.45%-78.80%和59.05%-88.85%。仅考虑本地排放和省内传输时,夏季河南省所有城市排放对本地四种污染物浓度的贡献最高。春季省内传输对PM和O-8h的贡献最大,分别为25.63%-74.69%和30.21%-80.01%,冬季省内传输对NO和SO的贡献较大,分别为26.02%-76.96%和20.30%-82.34%。河南省PM、NO和SO的传输路径较为相似,冬季多由北向南传输,春季由西向东、西南向东北传输,夏季由西南向东北传输,秋季由北向南传输;不过,PM的传输更为复杂。O-8h的传输路径与其他污染物差异较大,尤其是秋季污染物大多由北向南传输,但O-8h由西南向东北的传输路径较为明显。

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