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Anthropogenically and meteorologically modulated summertime ozone trends and their health implications since China's clean air actions.
Yan, Dan; Jin, Zhipeng; Zhou, Yiting; Li, Mengmeng; Zhang, Zihan; Wang, Tijian; Zhuang, Bingliang; Li, Shu; Xie, Min.
Affiliation
  • Yan D; School of Atmospheric Sciences, Nanjing University, Nanjing, 210023, China.
  • Jin Z; School of Atmospheric Sciences, Nanjing University, Nanjing, 210023, China.
  • Zhou Y; School of Atmospheric Sciences, Nanjing University, Nanjing, 210023, China.
  • Li M; School of Atmospheric Sciences, Nanjing University, Nanjing, 210023, China; Frontiers Science Center for Critical Earth Material Cycling, Nanjing, 210023, China. Electronic address: mengmengli2015@nju.edu.cn.
  • Zhang Z; School of Atmospheric Sciences, Nanjing University, Nanjing, 210023, China.
  • Wang T; School of Atmospheric Sciences, Nanjing University, Nanjing, 210023, China.
  • Zhuang B; School of Atmospheric Sciences, Nanjing University, Nanjing, 210023, China.
  • Li S; School of Atmospheric Sciences, Nanjing University, Nanjing, 210023, China.
  • Xie M; School of Environment, Nanjing Normal University, Nanjing, 210023, China.
Environ Pollut ; 343: 123234, 2024 Feb 15.
Article in En | MEDLINE | ID: mdl-38154777
ABSTRACT
Elevated ozone (O3) has emerged as the major air quality concern since China's clean air actions, offsetting the health benefits gained from improved air quality. Given the shifted ozone chemical regimes and recently boosted extreme weather in China, it's essential to rethink the O3 trends since 2013 for evaluations of air pollution mitigation policy. Here, we examine the anthropogenically and meteorologically modulated summertime O3 trends across China at different stages of the clean air actions using multi-source observations combined with multi-model calculations. Ozone increases steadily in China between 2013-2022, with a fast increase rate of 4.4 µg m-3 yr-1 in Phase I and a much smaller 0.6 µg m-3 yr-1 in Phase II of Action Plan. Results highlight that the deteriorative O3 pollution in Phase I and early Phase II is dominated by the nonlinear O3-emission response. Persistent decline in O3 precursors has shifted its chemical regime in urban areas and began to show a positive influence on ozone mitigation in recent years. Meteorological influence on O3 variations is minor until 2019 (∼10%), but it greatly accelerates or relieves the O3 pollution after then, showing comparable contribution to emissions. Epidemiological model predicts totally 0.8-3.0 thousand yr-1 more deaths across China with altered anthropogenic emissions since clean air actions, and additional health burdens by -1.5-0.3 thousand yr-1 from perturbated meteorology. This study calls for stringent emission control and climate adaptation strategies to attain the ozone pollution mitigation in China.
Subject(s)

Full text: 1 Collection: 01-internacional Database: MEDLINE Main subject: Ozone / Air Pollutants / Air Pollution Country/Region as subject: Asia Language: En Journal: Environ Pollut Journal subject: SAUDE AMBIENTAL Year: 2024 Document type: Article Affiliation country: China Country of publication: United kingdom

Full text: 1 Collection: 01-internacional Database: MEDLINE Main subject: Ozone / Air Pollutants / Air Pollution Country/Region as subject: Asia Language: En Journal: Environ Pollut Journal subject: SAUDE AMBIENTAL Year: 2024 Document type: Article Affiliation country: China Country of publication: United kingdom