The significant contribution of HONO to secondary pollutants during a severe winter pollution event in southern China

被引:148
作者
Fu, Xiao [1 ]
Wang, Tao [1 ]
Zhang, Li [1 ,2 ]
Li, Qinyi [1 ,6 ]
Wang, Zhe [1 ]
Xia, Men [1 ]
Yun, Hui [1 ]
Wang, Weihao [1 ]
Yu, Chuan [1 ]
Yue, Dingli [3 ]
Zhou, Yan [3 ]
Zheng, Junyun [4 ]
Han, Rui [5 ]
机构
[1] Hong Kong Polytech Univ, Dept Civil & Environm Engn, Hong Kong 99907, Peoples R China
[2] Princeton Univ, Atmospher & Ocean Sci, Princeton, NJ 08540 USA
[3] Guangdong Prov Environm Monitoring Ctr, Guangzhou, Guangdong, Peoples R China
[4] Jinan Univ, Inst Environm & Climate Res, Guangzhou, Guangdong, Peoples R China
[5] China Meteorol Adm, Natl Meteorol Informat Ctr, Beijing 100081, Peoples R China
[6] CSIC, Dept Atmospher Chem & Climate, Inst Phys Chem Rocasolano, E-28006 Madrid, Spain
关键词
NITROUS-ACID HONO; PEARL RIVER DELTA; AIR-QUALITY; NITRIC-ACID; CHEMICAL CHARACTERISTICS; REACTIVE NITROGEN; NITRATE FORMATION; URBAN ATMOSPHERE; OZONE POLLUTION; MODELING SYSTEM;
D O I
10.5194/acp-19-1-2019
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Nitrous acid (HONO) can strongly affect atmospheric photochemistry in polluted regions through the production of hydroxyl radicals (OHs). In January 2017, a severe pollution episode occurred in the Pearl River Delta (PRD) of China, with maximum hourly PM2.5, ozone, and HONO levels reaching 400 mu m(-3), 150 ppb, and 8 ppb, respectively, at a suburban site. The present study investigated the sources and processes generating such high HONO concentrations and the role of HONO chemistry in this severe winter episode. Four recently reported HONO sources were added to the Community Multiscale Air Quality (CMAQ) model, including RH-dependent (relative humidity) and light-enhancing effects on heterogeneous reactions, photolysis of particulate nitrate in the atmosphere, and photolysis of HNO3 and nitrate on surfaces. The revised model reproduced the observed HONO and significantly improved its performance for O-3 and PM2.5. The model simulations showed that the heterogeneous generation on surfaces (with RH and light effects) was the largest contributor (72 %) to the predicted HONO concentrations, with the RH-enhancing effects more significant at nighttime and the light-enhancing effects more important in the daytime. The photolysis of total nitrate in the atmosphere and deposited on surfaces was the dominant HONO source during noon and afternoon, contributing above 50 % of the simulated HONO. The HONO photolysis was the dominant contributor to HOx production in this episode. With all HONO sources, the daytime average O-3 at the Heshan site was increased by 24 ppb (or 70 %), compared to the simulation results without any HONO sources. Moreover, the simulated mean concentrations of TNO3 (HNO3+ fine particle NO3-) at the Heshan site, which was the key species for this haze formation, increased by about 17 mu m(-3) (67 %) due to the HONO chemistry, and the peak enhancement reached 55 mu m(-3). This study highlights the key role of HONO chemistry in the formation of winter haze in a subtropical environment.
引用
收藏
页码:1 / 14
页数:14
相关论文
共 86 条
[1]   Strong daytime production of OH from HNO2 at a rural mountain site -: art. no. L02809 [J].
Acker, K ;
Möller, D ;
Wieprecht, W ;
Meixner, FX ;
Bohn, B ;
Gilge, S ;
Plass-Dülmer, C ;
Berresheim, H .
GEOPHYSICAL RESEARCH LETTERS, 2006, 33 (02)
[2]   OH formation by HONO photolysis during the BERLIOZ experiment -: art. no. 8247 [J].
Alicke, B ;
Geyer, A ;
Hofzumahaus, A ;
Holland, F ;
Konrad, S ;
Pätz, HW ;
Schäfer, J ;
Stutz, J ;
Volz-Thomas, A ;
Platt, U .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2003, 108 (D4)
[3]   Description and evaluation of the Community Multiscale Air Quality (CMAQ) modeling system version 5.1 [J].
Appel, K. Wyat ;
Napelenok, Sergey L. ;
Foley, Kristen M. ;
Pye, Havala O. T. ;
Hogrefe, Christian ;
Luecken, Deborah J. ;
Bash, Jesse O. ;
Roselle, Shawn J. ;
Pleim, Jonathan E. ;
Foroutan, Hosein ;
Hutzell, William T. ;
Pouliot, George A. ;
Sarwar, Golam ;
Fahey, Kathleen M. ;
Gantt, Brett ;
Gilliam, Robert C. ;
Heath, Nicholas K. ;
Kang, Daiwen ;
Mathur, Rohit ;
Schwede, Donna B. ;
Spero, Tanya L. ;
Wong, David C. ;
Young, Jeffrey O. .
GEOSCIENTIFIC MODEL DEVELOPMENT, 2017, 10 (04) :1703-1732
[4]   Photochemical Renoxification of Nitric Acid on Real Urban Grime [J].
Baergen, Alyson M. ;
Donaldson, D. J. .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2013, 47 (02) :815-820
[5]   Measurements of nitrous acid (HONO) in urban area of Shanghai, China [J].
Bernard, Francois ;
Cazaunau, Mathieu ;
Grosselin, Benoit ;
Zhou, Bin ;
Zheng, Jun ;
Liang, Peng ;
Zhang, Yujie ;
Ye, Xingnan ;
Daele, Veronique ;
Mu, Yujing ;
Zhang, Renyi ;
Chen, Jianmin ;
Mellouki, Abdelwahid .
ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH, 2016, 23 (06) :5818-5829
[6]   Winter and Summer PM2.5 Chemical Compositions in Fourteen Chinese Cities [J].
Cao, Jun-Ji ;
Shen, Zhen-Xing ;
Chow, Judith C. ;
Watson, John G. ;
Lee, Shun-Cheng ;
Tie, Xue-Xi ;
Ho, Kin-Fai ;
Wang, Ge-Hui ;
Han, Yong-Ming .
JOURNAL OF THE AIR & WASTE MANAGEMENT ASSOCIATION, 2012, 62 (10) :1214-1226
[7]   Air pollution in mega cities in China [J].
Chan, Chak K. ;
Yao, Xiaohong .
ATMOSPHERIC ENVIRONMENT, 2008, 42 (01) :1-42
[8]  
Chen F, 2001, MON WEATHER REV, V129, P569, DOI 10.1175/1520-0493(2001)129<0569:CAALSH>2.0.CO
[9]  
2
[10]   Modeling nitrous acid and its impact on ozone and hydroxyl radical during the Texas Air Quality Study 2006 [J].
Czader, B. H. ;
Rappenglueck, B. ;
Percell, P. ;
Byun, D. W. ;
Ngan, F. ;
Kim, S. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2012, 12 (15) :6939-6951