Measurement and modeling of O3 variability in Shanghai, China: Application of the WRF-Chem model

被引:133
作者
Tie, Xuexi [2 ]
Geng, Fuhai [1 ]
Peng, Li [1 ]
Gao, Wei [1 ]
Zhao, Chunsheng [3 ]
机构
[1] Shanghai Meteorol Bur, Shanghai, Peoples R China
[2] Natl Ctr Atmospher Res, Boulder, CO 80307 USA
[3] Peking Univ, Phys Coll, Beijing 100871, Peoples R China
基金
中国国家自然科学基金;
关键词
WRF-Chem model; O-3 in the Shanghai region; MEXICO-CITY; OZONE PRODUCTION; NOX; SENSITIVITY; EMISSIONS; REGION; VOCS; VISIBILITY; OXIDANTS; AEROSOLS;
D O I
10.1016/j.atmosenv.2009.06.008
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Since 2005, Shanghai Meteorological Bureau (SMB) has established an observational network for measuring VOC, NOx, O-3 and aerosols in the Shanghai region. In this study, a rapid O-3 changes from Aug/02/2007 to Aug/11/2007 was observed in the region. During this 10 day period, the noontime O-3 maximum decreased from 100 to 130 ppbv to about 20-30 ppbv. In order to analyze the processes in controlling this rapid change of O-3 during this short period, a newly developed regional chemical/dynamical model (WRF-Chem) is applied to study O-3 variability in the Shanghai region. The model performances are evaluated by comparing the model calculation to the measurement. The result shows that the calculated magnitudes and diurnal variations of O-3 are close to the measured results in city sites, but are underestimated at a rural petroleum industrial site, suggesting that the emissions from petroleum factories around this rural site are significantly underestimated and need to be improved. The calculated rapid changes of O-3 concentrations, O-3 precursors, and aerosols are consistent with the measured results, suggesting that the model is suitable to study the causes of this rapid O-3 change. The model analysis indicates that weather conditions play important roles in controlling the surface O-3 in the Shanghai region. During summer, there is a persistent sub-tropical high pressure system (SUBH) in southeast of Shanghai over Pacific Ocean. During the earlier time of the period (Aug/02-Aug/05), the SUBH system was weak, resulting in weak surface winds. With the calm winds, a noticeable noontime sea-breeze produced an inflow from ocean to land, generating a cycling pattern of wind directions. As a result, the high O-3 concentrations were trapped in the Shanghai region, with a maximum concentration of 100-130 ppbv. By contrast, during the later time of the period (Aug/06-Aug/11), the SUBH was enhanced, resulting in strong surface winds. The high O-3 concentrations formed in the city were rapidly transported to the downwind region of the city, resulting in low O-3 concentrations in the Shanghai region. This study illustrates that the WRF-Chem model is a useful tool for studying the high variability of O-3 concentrations in Shanghai, which has important implication for the prediction of high O-3 concentration events in the city. (C) 2009 Elsevier Ltd. All rights reserved.
引用
收藏
页码:4289 / 4302
页数:14
相关论文
共 30 条
[1]   Evidence of impact of aerosols on surface ozone concentration in Tianjin, China [J].
Bian, Hai ;
Han, Suqin ;
Tie, Xuexi ;
Sun, Meiling ;
Liu, Aixia .
ATMOSPHERIC ENVIRONMENT, 2007, 41 (22) :4672-4681
[2]  
Chang J. S., 1989, 4 NAT AC PREC ASS PR
[3]   Long-term trend of visibility and its characterizations in the Pearl River Delta (PRD) region, China [J].
Deng, Xuejiao ;
Tie, Xuexi ;
Wu, Dui ;
Zhou, Xiuji ;
Bi, Xueyan ;
Tan, Hanbo ;
Li, Fei ;
Hang, Chenglin .
ATMOSPHERIC ENVIRONMENT, 2008, 42 (07) :1424-1435
[4]   Characterizations of ozone, NOx, and VOCs measured in Shanghai, China [J].
Geng, Fuhai ;
Tie, Xuexi ;
Xu, Jianmin ;
Zhou, Guangqiang ;
Peng, Li ;
Gao, Wei ;
Tang, Xu ;
Zhao, Chunsheng .
ATMOSPHERIC ENVIRONMENT, 2008, 42 (29) :6873-6883
[5]   Analysis of ozone and VOCs measured in Shanghai: A case study [J].
Geng, Fuhai ;
Zhao, Chunsheng ;
Tang, Xu ;
Lu, Guoliang ;
Tie, Xuexi .
ATMOSPHERIC ENVIRONMENT, 2007, 41 (05) :989-1001
[6]   Aircraft measurements of O3, NOx, CO, VOCs, and SO2 in the Yangtze River Delta region [J].
Geng, Fuhai ;
Zhang, Qiang ;
Tie, Xuexi ;
Huang, Mengyu ;
Ma, Xincheng ;
Deng, Zhaoze ;
Yu, Qiong ;
Quan, Jiannong ;
Zhao, Chunsheng .
ATMOSPHERIC ENVIRONMENT, 2009, 43 (03) :584-593
[7]  
GRELL GA, 2005, J GEOPHYS RES UNPUB
[8]   Ozone production in the New York City urban plume [J].
Kleinman, LI ;
Daum, PH ;
Imre, DG ;
Lee, JH ;
Lee, YN ;
Nunnermacker, LJ ;
Springston, SR ;
Weinstein-Lloyd, J ;
Newman, L .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2000, 105 (D11) :14495-14511
[9]   Characterizing ozone production in the Mexico City Metropolitan Area: a case study using a chemical transport model [J].
Lei, W. ;
de Foy, B. ;
Zavala, M. ;
Volkamer, R. ;
Molina, L. T. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2007, 7 :1347-1366
[10]   Impacts of black carbon aerosol on photolysis and ozone [J].
Li, GH ;
Zhang, RY ;
Fan, JW ;
Tie, XX .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2005, 110 (D23) :1-10