Impact of Marine Shipping Emissions on Ozone Pollution During the Warm Seasons in China

被引:2
作者
Zheng, Songci [1 ]
Jiang, Fei [1 ,2 ,3 ]
Feng, Shuzhuang [1 ]
Liu, Huan [4 ]
Wang, Xiaoyuan [5 ]
Tian, Xudong [5 ]
Ying, Chuanyou [6 ]
Jia, Mengwei [1 ]
Shen, Yang [1 ]
Lyu, Xiaopu [7 ]
Guo, Hai [8 ]
Cai, Zhe [9 ]
机构
[1] Nanjing Univ, Int Inst Earth Syst Sci, Jiangsu Prov Key Lab Geog Informat Sci & Technol, Nanjing, Peoples R China
[2] Jiangsu Ctr Collaborat Innovat Geog Informat Resou, Nanjing, Peoples R China
[3] Nanjing Univ, Frontiers Sci Ctr Crit Earth Mat Cycling, Nanjing, Peoples R China
[4] Tsinghua Univ, Sch Environm, Beijing, Peoples R China
[5] Zhejiang Ecol & Environm Monitoring Ctr, Hangzhou, Peoples R China
[6] Fuzhou Res Acad Environm Sci, Fuzhou, Peoples R China
[7] Hong Kong Baptist Univ, Dept Geog, Hong Kong, Peoples R China
[8] Hong Kong Polytech Univ, Dept Civil & Environm Engn, Hong Kong, Peoples R China
[9] Nanjing Climblue Technol Co Ltd, Nanjing, Peoples R China
关键词
OCEAN-GOING VESSELS; AIR-QUALITY; RIVER DELTA; ANTHROPOGENIC EMISSIONS; PARTICULATE MATTER; ISOPRENE EMISSIONS; ACID DEPOSITION; LEVEL OZONE; EAST-ASIA; MICS-ASIA;
D O I
10.1029/2024JD040864
中图分类号
P4 [大气科学(气象学)];
学科分类号
0706 ; 070601 ;
摘要
As China's land-based anthropogenic emissions are decreasing, the impact of marine shipping emissions (MSEs) on the atmosphere, especially in coastal areas, deserves further attention. This study investigates the impact of MSEs on MDA8 ozone (O3) levels during the warm seasons of 2017 in China, considering different seasons and synoptic patterns. The results indicate that the average impact of MSEs on O3 decreases from offshore to inland, peaking at over 29.0 ppb at sea and 13.8 ppb along the coast of mainland China. Influenced by precursor emissions, meteorology and other factors, MSEs contribute differently to O3 in Beijing-Tianjin-Hebei (BTH), Yangtze River Delta (YRD) and Pearl River Delta (PRD), with contributions of 3.0, 5.2, and 4.9 ppb, respectively, and ranging from 2.7 to 7.3 ppb in 13 coastal port cities. The O3 impacts of MSEs are higher on polluted days than on clean days, especially during onshore winds. In the BTH, MSEs increase O3 by 5.5 ppb on polluted days and 3.0 ppb on clean days with northeast winds from the Bohai Sea. In the YRD, MSEs increase O3 by 9.4 ppb on polluted days and 7.3 ppb on clean days with southeast winds. MSEs significantly increase O3 levels in the PRD by 11.0 ppb on polluted days and 5.0 ppb on clean days with southeast winds. Although the emission inventories, initial and boundary conditions, etc. may introduce uncertainties, our results still provide useful information for O3 pollution management in coastal cities as a reasonable way to track mass contributions. This study looks at how marine shipping emissions (MSEs) affect ozone levels in coastal China during the warm seasons in 2017. The impact of MSEs on ozone levels varies by season and region. They are significant during onshore winds and higher on polluted days than on clean days. They decrease from offshore to inland, peaking at over 29.0 ppb at sea and 13.8 ppb (21.5%) in coastal areas of mainland China. In several port cities, MSEs increase ozone levels by 2.7-7.3 ppb. In the Beijing-Tianjin-Hebei, Yangtze River Delta, and Pearl River Delta, they increase ozone levels by 3.0, 5.2, and 4.9 ppb, respectively. In these three regions, MSEs can increase ozone levels on polluted days (clean days) by 5.5 ppb (3.0 ppb), 9.4 ppb (7.3 ppb), and 11.0 ppb (5.0 ppb) under synoptic patterns with onshore winds. These results show the importance of considering MSEs in managing ozone pollution in coastal cities. Ozone impact of marine shipping emissions (MSEs) decreases from sea to inland, peaking at 29.0 ppb at sea and 13.8 ppb in coastal mainland China In 2017, MSEs increase ozone levels by 2.7-7.3 ppb in coastal port cities and 3.0-5.2 ppb in three major regions MSEs have a higher impact on polluted days and are significant during onshore winds
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页数:21
相关论文
共 113 条
[21]   Impacts of emissions and meteorological changes on China's ozone pollution in the warm seasons of 2013 and 2017 [J].
Ding, Dian ;
Xing, Jia ;
Wang, Shuxiao ;
Chang, Xing ;
Hao, Jiming .
FRONTIERS OF ENVIRONMENTAL SCIENCE & ENGINEERING, 2019, 13 (05)
[22]   The impact of synoptic patterns on summertime ozone pollution in the North China Plain [J].
Dong, Yueming ;
Li, Jing ;
Guo, Jianping ;
Jiang, Zhongjing ;
Chu, Yiqi ;
Chang, Liang ;
Yang, Yang ;
Liao, Hong .
SCIENCE OF THE TOTAL ENVIRONMENT, 2020, 735
[23]   Emission from international sea transportation and environmental impact -: art. no. 4560 [J].
Endresen, O ;
Sorgård, E ;
Sundet, JK ;
Dalsoren, SB ;
Isaksen, ISA ;
Berglen, TF ;
Gravir, G .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2003, 108 (D17)
[24]   Multi-model simulations of the impact of international shipping on Atmospheric Chemistry and Climate in 2000 and 2030 [J].
Eyring, V. ;
Stevenson, D. S. ;
Lauer, A. ;
Dentener, F. J. ;
Butler, T. ;
Collins, W. J. ;
Ellingsen, K. ;
Gauss, M. ;
Hauglustaine, D. A. ;
Isaksen, I. S. A. ;
Lawrence, M. G. ;
Richter, A. ;
Rodriguez, J. M. ;
Sanderson, M. ;
Strahan, S. E. ;
Sudo, K. ;
Szopa, S. ;
van Noije, T. P. C. ;
Wild, O. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2007, 7 :757-780
[25]   Transport impacts on atmosphere and climate: Shipping [J].
Eyring, Veronika ;
Isaksen, Ivar S. A. ;
Berntsen, Terje ;
Collins, William J. ;
Corbett, James J. ;
Endresen, Oyvind ;
Grainger, Roy G. ;
Moldanova, Jana ;
Schlager, Hans ;
Stevenson, David S. .
ATMOSPHERIC ENVIRONMENT, 2010, 44 (37) :4735-4771
[26]   Spatial and Seasonal Dynamics of Ship Emissions over the Yangtze River Delta and East China Sea and Their Potential Environmental Influence [J].
Fan, Qianzhu ;
Zhang, Yan ;
Ma, Weichun ;
Ma, Huixin ;
Feng, Junlan ;
Yu, Qi ;
Yang, Xin ;
Ng, Simon K. W. ;
Fu, Qingyan ;
Chen, Limin .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2016, 50 (03) :1322-1329
[27]   Impact of Anthropogenic Heat Release on Regional Climate in Three Vast Urban Agglomerations in China [J].
Feng Jinming ;
Wang Jun ;
Yan Zhongwei .
ADVANCES IN ATMOSPHERIC SCIENCES, 2014, 31 (02) :363-373
[28]   The influence of spatiality on shipping emissions, air quality and potential human exposure in the Yangtze River Delta/Shanghai, China [J].
Feng, Junlan ;
Zhang, Yan ;
Li, Shanshan ;
Mao, Jingbo ;
Patton, Allison P. ;
Zhou, Yuyan ;
Ma, Weichun ;
Liu, Cong ;
Kan, Haidong ;
Huang, Cheng ;
An, Jingyu ;
Li, Li ;
Shen, Yin ;
Fu, Qingyan ;
Wang, Xinning ;
Liu, Juan ;
Wang, Shuxiao ;
Ding, Dian ;
Cheng, Jie ;
Ge, Wangqi ;
Zhu, Hong ;
Walker, Katherine .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2019, 19 (09) :6167-6183
[29]   Constraining non-methane VOC emissions with TROPOMI HCHO observations: impact on summertime ozone simulation in August 2022 in China [J].
Feng, Shuzhuang ;
Jiang, Fei ;
Qian, Tianlu ;
Wang, Nan ;
Jia, Mengwei ;
Zheng, Songci ;
Chen, Jiansong ;
Ying, Fang ;
Ju, Weimin .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2024, 24 (13) :7481-7498
[30]   China's Fossil Fuel CO2 Emissions Estimated Using Surface Observations of Coemitted NO2 [J].
Feng, Shuzhuang ;
Jiang, Fei ;
Wang, Hengmao ;
Liu, Yifan ;
He, Wei ;
Wang, Haikun ;
Shen, Yang ;
Zhang, Lingyu ;
Jia, Mengwei ;
Ju, Weimin ;
Chen, Jing M. .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2024, 58 (19) :8299-8312