Modeling study on the roles of the deposition and transport of PM 2.5 in air quality changes over central-eastern China
The role of PM (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...
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Veröffentlicht in: | Journal of environmental sciences (China) 2023-01, Vol.123, p.535 |
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creator | Zhang, Lei He, Jianjun Gong, Sunling Guo, Xiaomei Zhao, Tianliang Che, Huizheng Wang, Hong Zhou, Chunhong Mo, Jingyue Gui, Ke Zheng, Yu Li, Lei Zhong, Junting Zhang, Xiaoye |
description | The role of PM
(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 PM
and anthropogenic emissions over central-eastern China in cold seasons as well as in different life stages of haze events was unraveled. PM
deposition is spatially distributed differently from PM
concentrations and anthropogenic emissions over China. The North China Plain (NCP) is typically characterized by higher anthropogenic emissions compared to southern China, such as the middle-low reaches of Yangtze River (MLYR), which includes parts of the Yangtze River Delta and the Midwest. However, PM
deposition 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 PM
during the removal stages is substantially higher than that in accumulation stages, with most of the PM
being transported southward and deposited to the MLYR and Sichuan Basin region, corresponding to a latitude range of about 24°N-31°N. |
format | Article |
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(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 PM
and anthropogenic emissions over central-eastern China in cold seasons as well as in different life stages of haze events was unraveled. PM
deposition is spatially distributed differently from PM
concentrations and anthropogenic emissions over China. The North China Plain (NCP) is typically characterized by higher anthropogenic emissions compared to southern China, such as the middle-low reaches of Yangtze River (MLYR), which includes parts of the Yangtze River Delta and the Midwest. However, PM
deposition 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 PM
during the removal stages is substantially higher than that in accumulation stages, with most of the PM
being transported southward and deposited to the MLYR and Sichuan Basin region, corresponding to a latitude range of about 24°N-31°N.</description><identifier>ISSN: 1001-0742</identifier><identifier>PMID: 36522012</identifier><language>eng</language><publisher>Netherlands</publisher><subject>Air Pollutants - analysis ; Air Pollution - analysis ; China ; Environmental Monitoring - methods ; Particulate Matter - analysis ; Seasons</subject><ispartof>Journal of environmental sciences (China), 2023-01, Vol.123, p.535</ispartof><rights>Copyright © 2022. Published by Elsevier B.V.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/36522012$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Zhang, Lei</creatorcontrib><creatorcontrib>He, Jianjun</creatorcontrib><creatorcontrib>Gong, Sunling</creatorcontrib><creatorcontrib>Guo, Xiaomei</creatorcontrib><creatorcontrib>Zhao, Tianliang</creatorcontrib><creatorcontrib>Che, Huizheng</creatorcontrib><creatorcontrib>Wang, Hong</creatorcontrib><creatorcontrib>Zhou, Chunhong</creatorcontrib><creatorcontrib>Mo, Jingyue</creatorcontrib><creatorcontrib>Gui, Ke</creatorcontrib><creatorcontrib>Zheng, Yu</creatorcontrib><creatorcontrib>Li, Lei</creatorcontrib><creatorcontrib>Zhong, Junting</creatorcontrib><creatorcontrib>Zhang, Xiaoye</creatorcontrib><title>Modeling study on the roles of the deposition and transport of PM 2.5 in air quality changes over central-eastern China</title><title>Journal of environmental sciences (China)</title><addtitle>J Environ Sci (China)</addtitle><description>The role of PM
(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 PM
and anthropogenic emissions over central-eastern China in cold seasons as well as in different life stages of haze events was unraveled. PM
deposition is spatially distributed differently from PM
concentrations and anthropogenic emissions over China. The North China Plain (NCP) is typically characterized by higher anthropogenic emissions compared to southern China, such as the middle-low reaches of Yangtze River (MLYR), which includes parts of the Yangtze River Delta and the Midwest. However, PM
deposition 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 PM
during the removal stages is substantially higher than that in accumulation stages, with most of the PM
being transported southward and deposited to the MLYR and Sichuan Basin region, corresponding to a latitude range of about 24°N-31°N.</description><subject>Air Pollutants - analysis</subject><subject>Air Pollution - analysis</subject><subject>China</subject><subject>Environmental Monitoring - methods</subject><subject>Particulate Matter - analysis</subject><subject>Seasons</subject><issn>1001-0742</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2023</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqFjk0KwjAUhLNQtP5cQd4FKq-x0QOI4qbgwr1E87SRNKlJqvT2VtG1q2H4ZobpsSRDzFJc5XzIRiHcEDEXKAZsuFgKzjHjCXsWTpHR9gohNqoFZyGWBN4ZCuAuH6OodkFH3TFpFUQvbaidj2--L4DPBegOaQ_3RhodWziX0l7fAw_ycCbbVUxKMkTyFtaltnLC-hdpAk2_Omaz7eaw3qV1c6pIHWuvK-nb4-_p4m_gBW5BSZc</recordid><startdate>202301</startdate><enddate>202301</enddate><creator>Zhang, Lei</creator><creator>He, Jianjun</creator><creator>Gong, Sunling</creator><creator>Guo, Xiaomei</creator><creator>Zhao, Tianliang</creator><creator>Che, Huizheng</creator><creator>Wang, Hong</creator><creator>Zhou, Chunhong</creator><creator>Mo, Jingyue</creator><creator>Gui, Ke</creator><creator>Zheng, Yu</creator><creator>Li, Lei</creator><creator>Zhong, Junting</creator><creator>Zhang, Xiaoye</creator><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope></search><sort><creationdate>202301</creationdate><title>Modeling study on the roles of the deposition and transport of PM 2.5 in air quality changes over central-eastern China</title><author>Zhang, Lei ; He, Jianjun ; Gong, Sunling ; Guo, Xiaomei ; Zhao, Tianliang ; Che, Huizheng ; Wang, Hong ; Zhou, Chunhong ; Mo, Jingyue ; Gui, Ke ; Zheng, Yu ; Li, Lei ; Zhong, Junting ; Zhang, Xiaoye</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-pubmed_primary_365220123</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2023</creationdate><topic>Air Pollutants - analysis</topic><topic>Air Pollution - analysis</topic><topic>China</topic><topic>Environmental Monitoring - methods</topic><topic>Particulate Matter - analysis</topic><topic>Seasons</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Zhang, Lei</creatorcontrib><creatorcontrib>He, Jianjun</creatorcontrib><creatorcontrib>Gong, Sunling</creatorcontrib><creatorcontrib>Guo, Xiaomei</creatorcontrib><creatorcontrib>Zhao, Tianliang</creatorcontrib><creatorcontrib>Che, Huizheng</creatorcontrib><creatorcontrib>Wang, Hong</creatorcontrib><creatorcontrib>Zhou, Chunhong</creatorcontrib><creatorcontrib>Mo, Jingyue</creatorcontrib><creatorcontrib>Gui, Ke</creatorcontrib><creatorcontrib>Zheng, Yu</creatorcontrib><creatorcontrib>Li, Lei</creatorcontrib><creatorcontrib>Zhong, Junting</creatorcontrib><creatorcontrib>Zhang, Xiaoye</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><jtitle>Journal of environmental sciences (China)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Zhang, Lei</au><au>He, Jianjun</au><au>Gong, Sunling</au><au>Guo, Xiaomei</au><au>Zhao, Tianliang</au><au>Che, Huizheng</au><au>Wang, Hong</au><au>Zhou, Chunhong</au><au>Mo, Jingyue</au><au>Gui, Ke</au><au>Zheng, Yu</au><au>Li, Lei</au><au>Zhong, Junting</au><au>Zhang, Xiaoye</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Modeling study on the roles of the deposition and transport of PM 2.5 in air quality changes over central-eastern China</atitle><jtitle>Journal of environmental sciences (China)</jtitle><addtitle>J Environ Sci (China)</addtitle><date>2023-01</date><risdate>2023</risdate><volume>123</volume><spage>535</spage><pages>535-</pages><issn>1001-0742</issn><abstract>The role of PM
(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 PM
and anthropogenic emissions over central-eastern China in cold seasons as well as in different life stages of haze events was unraveled. PM
deposition is spatially distributed differently from PM
concentrations and anthropogenic emissions over China. The North China Plain (NCP) is typically characterized by higher anthropogenic emissions compared to southern China, such as the middle-low reaches of Yangtze River (MLYR), which includes parts of the Yangtze River Delta and the Midwest. However, PM
deposition 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 PM
during the removal stages is substantially higher than that in accumulation stages, with most of the PM
being transported southward and deposited to the MLYR and Sichuan Basin region, corresponding to a latitude range of about 24°N-31°N.</abstract><cop>Netherlands</cop><pmid>36522012</pmid></addata></record> |
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source | MEDLINE; Access via ScienceDirect (Elsevier); Alma/SFX Local Collection |
subjects | Air Pollutants - analysis Air Pollution - analysis China Environmental Monitoring - methods Particulate Matter - analysis Seasons |
title | Modeling study on the roles of the deposition and transport of PM 2.5 in air quality changes over central-eastern China |
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