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Drivers of Increasing Ozone during the Two Phases of Clean Air Actions in China 2013–2020

[Image: see text] In response to the severe air pollution issue, the Chinese government implemented two phases (Phase I, 2013–2017; Phase II, 2018–2020) of clean air actions since 2013, resulting in a significant decline in fine particles (PM(2.5)) during 2013–2020, while the warm-season (April–Sept...

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Autores principales: Liu, Yuxi, Geng, Guannan, Cheng, Jing, Liu, Yang, Xiao, Qingyang, Liu, Liangke, Shi, Qinren, Tong, Dan, He, Kebin, Zhang, Qiang
Formato: Online Artículo Texto
Lenguaje:English
Publicado: American Chemical Society 2023
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC10286302/
https://www.ncbi.nlm.nih.gov/pubmed/37276527
http://dx.doi.org/10.1021/acs.est.3c00054
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author Liu, Yuxi
Geng, Guannan
Cheng, Jing
Liu, Yang
Xiao, Qingyang
Liu, Liangke
Shi, Qinren
Tong, Dan
He, Kebin
Zhang, Qiang
author_facet Liu, Yuxi
Geng, Guannan
Cheng, Jing
Liu, Yang
Xiao, Qingyang
Liu, Liangke
Shi, Qinren
Tong, Dan
He, Kebin
Zhang, Qiang
author_sort Liu, Yuxi
collection PubMed
description [Image: see text] In response to the severe air pollution issue, the Chinese government implemented two phases (Phase I, 2013–2017; Phase II, 2018–2020) of clean air actions since 2013, resulting in a significant decline in fine particles (PM(2.5)) during 2013–2020, while the warm-season (April–September) mean maximum daily 8 h average ozone (MDA8 O(3)) increased by 2.6 μg m(–3) yr(–1) in China during the same period. Here, we derived the drivers behind the rising O(3) concentrations during the two phases of clean air actions by using a bottom-up emission inventory, a regional chemical transport model, and a multiple linear regression model. We found that both meteorological variations (3.6 μg m(–3)) and anthropogenic emissions (6.7 μg m(–3)) contributed to the growth of MDA8 O(3) from 2013 to 2020, with the changes in anthropogenic emissions playing a more important role. The anthropogenic contributions to the O(3) rise during 2017–2020 (1.2 μg m(–3)) were much lower than that in 2013–2017 (5.2 μg m(–3)). The lack of volatile organic compound (VOC) control and the decline in nitrogen oxides (NO(x)) emissions were responsible for the O(3) increase in 2013–2017 due to VOC-limited regimes in most urban areas, while the synergistic control of VOC and NO(x) in Phase II initially worked to mitigate O(3) pollution during 2018–2020, although its effectiveness was offset by the penalty of PM(2.5) decline. Future mitigation efforts should pay more attention to the simultaneous control of VOC and NO(x) to improve O(3) air quality.
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spelling pubmed-102863022023-06-23 Drivers of Increasing Ozone during the Two Phases of Clean Air Actions in China 2013–2020 Liu, Yuxi Geng, Guannan Cheng, Jing Liu, Yang Xiao, Qingyang Liu, Liangke Shi, Qinren Tong, Dan He, Kebin Zhang, Qiang Environ Sci Technol [Image: see text] In response to the severe air pollution issue, the Chinese government implemented two phases (Phase I, 2013–2017; Phase II, 2018–2020) of clean air actions since 2013, resulting in a significant decline in fine particles (PM(2.5)) during 2013–2020, while the warm-season (April–September) mean maximum daily 8 h average ozone (MDA8 O(3)) increased by 2.6 μg m(–3) yr(–1) in China during the same period. Here, we derived the drivers behind the rising O(3) concentrations during the two phases of clean air actions by using a bottom-up emission inventory, a regional chemical transport model, and a multiple linear regression model. We found that both meteorological variations (3.6 μg m(–3)) and anthropogenic emissions (6.7 μg m(–3)) contributed to the growth of MDA8 O(3) from 2013 to 2020, with the changes in anthropogenic emissions playing a more important role. The anthropogenic contributions to the O(3) rise during 2017–2020 (1.2 μg m(–3)) were much lower than that in 2013–2017 (5.2 μg m(–3)). The lack of volatile organic compound (VOC) control and the decline in nitrogen oxides (NO(x)) emissions were responsible for the O(3) increase in 2013–2017 due to VOC-limited regimes in most urban areas, while the synergistic control of VOC and NO(x) in Phase II initially worked to mitigate O(3) pollution during 2018–2020, although its effectiveness was offset by the penalty of PM(2.5) decline. Future mitigation efforts should pay more attention to the simultaneous control of VOC and NO(x) to improve O(3) air quality. American Chemical Society 2023-06-05 /pmc/articles/PMC10286302/ /pubmed/37276527 http://dx.doi.org/10.1021/acs.est.3c00054 Text en © 2023 The Authors. Published by American Chemical Society https://creativecommons.org/licenses/by-nc-nd/4.0/Permits non-commercial access and re-use, provided that author attribution and integrity are maintained; but does not permit creation of adaptations or other derivative works (https://creativecommons.org/licenses/by-nc-nd/4.0/).
spellingShingle Liu, Yuxi
Geng, Guannan
Cheng, Jing
Liu, Yang
Xiao, Qingyang
Liu, Liangke
Shi, Qinren
Tong, Dan
He, Kebin
Zhang, Qiang
Drivers of Increasing Ozone during the Two Phases of Clean Air Actions in China 2013–2020
title Drivers of Increasing Ozone during the Two Phases of Clean Air Actions in China 2013–2020
title_full Drivers of Increasing Ozone during the Two Phases of Clean Air Actions in China 2013–2020
title_fullStr Drivers of Increasing Ozone during the Two Phases of Clean Air Actions in China 2013–2020
title_full_unstemmed Drivers of Increasing Ozone during the Two Phases of Clean Air Actions in China 2013–2020
title_short Drivers of Increasing Ozone during the Two Phases of Clean Air Actions in China 2013–2020
title_sort drivers of increasing ozone during the two phases of clean air actions in china 2013–2020
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC10286302/
https://www.ncbi.nlm.nih.gov/pubmed/37276527
http://dx.doi.org/10.1021/acs.est.3c00054
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