Modeling study on the roles of the deposition and transport of PM2.5 in air quality changes over central-eastern China

被引:0
作者
Lei Zhang [1 ]
Jianjun He [1 ]
Sunling Gong [1 ]
Xiaomei Guo [2 ,3 ]
Tianliang Zhao [4 ]
Huizheng Che [1 ]
Hong Wang [1 ]
Chunhong Zhou [1 ]
Jingyue Mo [1 ]
Ke Gui [1 ]
Yu Zheng [1 ]
Lei Li [1 ]
Junting Zhong [1 ]
Xiaoye Zhang [1 ]
机构
[1] State Key Laboratory of Severe Weather & Key Laboratory of Atmospheric Chemistry of CMA, Chinese Academy of Meteorological Sciences
[2] Heavy Rain and Drought-Flood Disasters in Plateau and Basin Key Laboratory of Sichuan Province
[3] Weather Modification Office of Sichuan Province
[4] Climate and Weather Disasters Collaborative Innovation Center, Nanjing University of Information Science&Technology
基金
中国国家自然科学基金;
关键词
D O I
暂无
中图分类号
X513 [粒状污染物];
学科分类号
0706 ; 070602 ;
摘要
The role of PM2.5(particles with aerodynamic diameters ≤ 2.5 μm) deposition in air quality changes over China remains unclear. By using the three-year(2013, 2015, and 2017) simulation results of the WRF/CUACE v1.0 model from a previous work(Zhang et al., 2021), a non-linear relationship between the deposition of PM2.5and anthropogenic emissions over central-eastern China in cold seasons as well as in different life stages of haze events was unraveled. PM2.5deposition is spatially distributed differently from PM2.5concentrations and anthropogenic emissions over China. The North China Plain(NCP) is typically characterized by higher anthropogenic emissions compared to southern China, such as the middlelow reaches of Yangtze River(MLYR), which includes parts of the Yangtze River Delta and the Midwest. However, PM2.5deposition in the NCP is significantly lower than that in the MLYR region, suggesting that in addition to meteorology and emissions, lower deposition is another important factor in the increase in haze levels. Regional transport of pollution in central-eastern China acts as a moderator of pollution levels in different regions, for example by bringing pollution from the NCP to the MLYR region in cold seasons. It was found that in typical haze events the deposition flux of PM2.5during the removal stages is substantially higher than that in accumulation stages, with most of the PM2.5being transported southward and deposited to the MLYR and Sichuan Basin region, corresponding to a latitude range of about 24°N-31°N.
引用
收藏
页码:535 / 544
页数:10
相关论文
共 44 条
  • [1] Temporal and spatial characteristics of PM2.5 transport fluxes of typical inland and coastal cities in China
    Panbo Guan
    Xiaoqi Wang
    Shuiyuan Cheng
    Hanyu Zhang
    [J]. Journal of Environmental Sciences, 2021, 103 (05) : 229 - 245
  • [2] The impact of meteorological changes from 2013 to 2017 on PM_(2.5) mass reduction in key regions in China.[J].Xiaoye ZHANG;Xiangde XU;Yihui DING;Yanju LIU;Hengde ZHANG;Yaqiang WANG;Junting ZHONG;.Science China(Earth Sciences).2019, 12
  • [3] Comparison of dust emissions; transport; and deposition between the Taklimakan Desert and Gobi Desert from 2007 to 2011.[J].CHEN SiYu;HUANG JianPing;LI JingXin;JIA Rui;JIANG NanXuan;KANG LiTai;MA XiaoJun;XIE TingTing;.Science China(Earth Sciences).2017, 07
  • [4] 中国大地形东侧霾空间分布“避风港”效应及其“气候调节”影响下的年代际变异
    徐祥德
    王寅钧
    赵天良
    程兴宏
    孟莹莹
    丁国安
    [J]. 科学通报, 2015, 60 (12) : 1132 - 1145
  • [5] Effect of vegetation seasonal cycle alterations to aerosol dry deposition on PM<sub>2.5</sub> concentrations in China..[J].Zhang Lei;He Jianjun;Gong Sunling;Guo Xiaomei;Zhao Tianliang;Zhou Chunhong;Wang Hong;Mo Jingyue;Gui Ke;Zheng Yu;Shan Yunpeng;Zhong Junting;Li Lei;Lei Yadong;Che Huizheng.The Science of the total environment.2022,
  • [6] Decline in bulk deposition of air pollutants in China lags behind reductions in emissions
    Zhao, Yu
    Xi, Mengxiao
    Zhang, Qiang
    Dong, Zhaoxin
    Ma, Mingrui
    Zhou, Kaiyue
    Xu, Wen
    Xing, Jia
    Zheng, Bo
    Wen, Zhang
    Liu, Xuejun
    Nielsen, Chris P.
    Liu, Yang
    Pan, Yuepeng
    Zhang, Lei
    [J]. NATURE GEOSCIENCE, 2022, 15 (03) : 190 - +
  • [7] Dry Deposition of Atmospheric Aerosols: Approaches; Observations; and Mechanisms.[J].Farmer Delphine K.;Boedicker Erin K.;DeBolt Holly M..Annual Review of Physical Chemistry.2021, 1
  • [8] Development of WRF/CUACE v1.0 model and its preliminary application in simulating air quality in China
    Zhang, Lei
    Gong, Sunling
    Zhao, Tianliang
    Zhou, Chunhong
    Wang, Yuesi
    Li, Jiawei
    Ji, Dongsheng
    He, Jianjun
    Liu, Hongli
    Gui, Ke
    Guo, Xiaomei
    Gao, Jinhui
    Shan, Yunpeng
    Wang, Hong
    Wang, Yaqiang
    Che, Huizheng
    Zhang, Xiaoye
    [J]. GEOSCIENTIFIC MODEL DEVELOPMENT, 2021, 14 (02) : 703 - 718
  • [9] Meteorological influences on PM 2.5 and O 3 trends and associated health burden since China's clean air actions.[J].Lei Chen;Jia Zhu;Hong Liao;Yang Yang;Xu Yue.Science of the Total Environment.2020,
  • [10] Changes of nitrogen deposition in China from 1980 to 2018..[J].Wen Zhang;Xu Wen;Li Qi;Han Mengjuan;Tang Aohan;Zhang Ying;Luo Xiaosheng;Shen Jianlin;Wang Wei;Li Kaihui;Pan Yuepeng;Zhang Lin;Li Wenqing;Collett Jeffery Lee;Zhong Buqing;Wang Xuemei;Goulding Keith;Zhang Fusuo;Liu Xuejun.Environment international.2020,