A172-06
Controlling particulate nitrate pollution in China

Tuesday, 15 December 2020: 04:20
Virtual
Shixian Zhai1, Daniel Jacob1, Xuan Wang2, Zirui Liu3, Tianxue Wen3, Viral Shah1, Ke Li1, Jonathan Moch1, Kelvin Hamilton Bates1, Shaojie Song1, Lu Shen1, Yuzhong Zhang4, Gan Luo5, Fangqun Yu6, Sun Yele3, Litao Wang7, Mengyao Qi7, Jun Tao8, Ke Gui9, Honghui Xu10, Qiang Zhang11, Tianliang Zhao12, Hyun Chul Lee13, Hyoungwoo Choi13 and Hong Liao12, (1)Harvard University, Cambridge, MA, United States, (2)City University of Hong Kong, Hong Kong, Hong Kong, (3)IAP, CAS, Beijing, China, (4)Westlake University, Hangzhou, China, (5)SUNY Albany, Albany, NY, United States, (6)SUNY at Albany, Atmospheric Sciences Research Center, Albany, NY, United States, (7)Hebei University of Engineering, Handan, China, (8)Jinan University, Guangzhou, China, (9)Chinese Academy of Meteorological Sciences, Beijing, China, (10)Institute of Meteorological Science of Zhejiang Province, Hangzhou, China, (11)Tsinghua University, Beijing, China, (12)Nanjing University of Information Science and Technology, Nanjing, China, (13)Samsung Advance Institute of Technology, Suwon-si, South Korea
Abstract:
Stringent emission controls to improve air quality have decreased fine particulate matter (PM2.5) concentrations in China by 30-50% over the 2013-2018 period. However, the nitrate component of PM2.5 has not responded effectively to emission controls on nitrogen oxides (NOx), and has actually increased during winter haze pollution events in the North China Plain. Recent studies have suggested that this could be caused by increased nitrate partitioning to the particulate phase as the sulfate component of PM2.5 decreases, or by faster NOx oxidation as oxidants increase. However, we find that these two processes are inadequate to explain the observed nitrate trends, and that nitrate would have increased even more over 2013-2018 were it not for favorable meteorology. We present simulations with the GEOS-Chem model that can successfully reproduce the observed nitrate trends, including the increase under winter haze conditions, and show that slower deposition of total nitrate (gas + particle) as the particulate fraction approaches unity is the dominant explanatory factor. Although ammonia is thermodynamically in excess for formation of PM2.5 nitrate, we find that ammonia emission controls are more effective than NOx for controlling nitrate because they decrease the lifetime of total nitrate against deposition. This calls for better understanding of the sources of wintertime ammonia in China as targets for emission controls.