Impacts of aerosol direct effects on tropospheric ozone through changes in atmospheric dynamics and photolysis rates

被引:175
作者
Xing, Jia [1 ]
Wang, Jiandong [1 ]
Mathur, Rohit [2 ]
Wang, Shuxiao [1 ]
Sarwar, Golam [2 ]
Pleim, Jonathan [2 ]
Hogrefe, Christian [2 ]
Zhang, Yuqiang [2 ]
Jiang, Jingkun [1 ]
Wong, David C. [2 ]
Hao, Jiming [1 ]
机构
[1] Tsinghua Univ, Sch Environm, State Key Joint Lab Environm Simulat & Pollut Con, Beijing 100084, Peoples R China
[2] US EPA, Res Triangle Pk, NC 27711 USA
基金
美国国家科学基金会;
关键词
PARTICULATE MATTER POLLUTION; WRF-CMAQ MODEL; COUPLED METEOROLOGY; AIR-QUALITY; NORTH-AMERICA; SURFACE; CHEMISTRY; SYSTEM; CHINA; SENSITIVITY;
D O I
10.5194/acp-17-9869-2017
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Aerosol direct effects (ADEs), i.e., scattering and absorption of incoming solar radiation, reduce radiation reaching the ground and the resultant photolysis attenuation can decrease ozone (O-3) formation in polluted areas. One the other hand, evidence also suggests that ADE-associated cooling suppresses atmospheric ventilation, thereby enhancing surface-level O-3. Assessment of ADE impacts is thus important for understanding emission reduction strategies that seek co-benefits associated with reductions in both particulate matter and O-3 levels. This study quantifies the impacts of ADEs on tropospheric ozone by using a two-way online coupled meteorology and atmospheric chemistry model, WRFCMAQ, using a process analysis methodology. Two manifestations of ADE impacts on O-3 including changes in atmospheric dynamics (Delta Dynamics) and changes in photolysis rates (Delta Photolysis) were assessed separately through multiple scenario simulations for January and July of 2013 over China. Results suggest that ADEs reduced surface daily maxima 1 h O-3 (DM1O(3)) in China by up to 39 mu gm(-)3 through the combination of Delta Dynamics and Delta Photolysis in January but enhanced surface DM1O(3) by up to 4 mu gm(-3) in July. Increased O-3 in July is largely attributed to 1 Dynamics, which causes a weaker O-3 sink of dry deposition and a stronger O-3 source of photochemistry due to the stabilization of the atmosphere. Meanwhile, surface OH is also enhanced at noon in July, though its daytime average values are reduced in January. An increased OH chain length and a shift towards more volatile organic compound (VOC)-limited conditions are found due to ADEs in both January and July. This study suggests that reducing ADEs may have the potential risk of increasing O-3 in winter, but it will benefit the reduction in maxima O-3 in summer.
引用
收藏
页码:9869 / 9883
页数:15
相关论文
共 51 条
[1]   AEROSOLS, CLOUD MICROPHYSICS, AND FRACTIONAL CLOUDINESS [J].
ALBRECHT, BA .
SCIENCE, 1989, 245 (4923) :1227-1230
[2]   China's air pollution reduction efforts may result in an increase in surface ozone levels in highly polluted areas [J].
Anger, Annela ;
Dessens, Olivier ;
Xi, Fengming ;
Barker, Terry ;
Wu, Rui .
AMBIO, 2016, 45 (02) :254-265
[3]   Evaluation of dust and trace metal estimates from the Community Multiscale Air Quality (CMAQ) model version 5.0 [J].
Appel, K. W. ;
Pouliot, G. A. ;
Simon, H. ;
Sarwar, G. ;
Pye, H. O. T. ;
Napelenok, S. L. ;
Akhtar, F. ;
Roselle, S. J. .
GEOSCIENTIFIC MODEL DEVELOPMENT, 2013, 6 (04) :883-899
[4]   Surface ozone photolysis rate trends in the Eastern Mediterranean: Modeling the effects of aerosols and total column ozone based on Terra MODIS data [J].
Benas, N. ;
Mourtzanou, E. ;
Kouvarakis, G. ;
Bais, A. ;
Mihalopoulos, N. ;
Vardavas, I. .
ATMOSPHERIC ENVIRONMENT, 2013, 74 :1-9
[5]   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
[6]  
Bohren C.F., 2008, Absorption and scattering oflight by small particles, V1st ed.
[7]   Parameterization of N2O5 reaction probabilities on the surface of particles containing ammonium, sulfate, and nitrate [J].
Davis, J. M. ;
Bhave, P. V. ;
Foley, K. M. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2008, 8 (17) :5295-5311
[8]   The impact of aerosols on solar ultraviolet radiation and photochemical smog [J].
Dickerson, RR ;
Kondragunta, S ;
Stenchikov, G ;
Civerolo, KL ;
Doddridge, BG ;
Holben, BN .
SCIENCE, 1997, 278 (5339) :827-830
[9]   Enhanced haze pollution by black carbon in megacities in China [J].
Ding, A. J. ;
Huang, X. ;
Nie, W. ;
Sun, J. N. ;
Kerminen, V. -M. ;
Petaja, T. ;
Su, H. ;
Cheng, Y. F. ;
Yang, X. -Q. ;
Wang, M. H. ;
Chi, X. G. ;
Wang, J. P. ;
Virkkula, A. ;
Guo, W. D. ;
Yuan, J. ;
Wang, S. Y. ;
Zhang, R. J. ;
Wu, Y. F. ;
Song, Y. ;
Zhu, T. ;
Zilitinkevich, S. ;
Kulmala, M. ;
Fu, C. B. .
GEOPHYSICAL RESEARCH LETTERS, 2016, 43 (06) :2873-2879
[10]   Assessment of the aerosol optics component of the coupled WRF-CMAQ model using CARES field campaign data and a single column model [J].
Gan, Chuen Meei ;
Binkowski, Francis ;
Pleim, Jonathan ;
Xing, Jia ;
Wong, David ;
Mathur, Rohit ;
Gilliam, Robert .
ATMOSPHERIC ENVIRONMENT, 2015, 115 :670-682