PM2.5 vertical variation during a fog episode in a rural area of the Yangtze River Delta, China

被引:24
作者
Zhu, Jun [1 ,2 ]
Zhu, Bin [1 ,2 ]
Huang, Yong [3 ,4 ]
An, Junlin [1 ,2 ]
Xu, Jiaping [5 ]
机构
[1] Nanjing Univ Informat Sci & Technol, Collaborat Innovat Ctr Forecast & Evaluat Meteoro, Joint Int Res Lab Climate & Environm Change ILCEC, Key Lab Meteorol Disaster,Minist Educ KLME, Nanjing, Jiangsu, Peoples R China
[2] China Meteorol Adm, Key Lab Aerosol Cloud Precipitat, Beijing, Peoples R China
[3] Anhui Meteorol Inst, Key Lab Atmospher Sci & Remote Sensing Anhui Prov, Hefei 230031, Anhui, Peoples R China
[4] Shouxian Natl Climatol Observ, Shouxian 232200, Peoples R China
[5] Jiangsu Inst Meteorol Sci, Nanjing 210009, Jiangsu, Peoples R China
基金
中国国家自然科学基金;
关键词
Radiation fog; PM2.5; profile; Planetary boundary layer structure; Turbulence; Scavenging of PM2.5; BLACK CARBON; RADIATION FOG; DISTRIBUTION PATTERNS; CHEMICAL-COMPOSITION; PARTICULATE MATTER; AIR-POLLUTION; HAZE EPISODE; AEROSOL; WATER; DEPOSITION;
D O I
10.1016/j.scitotenv.2019.05.319
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
A dense radiation fog event occurred at the Shouxian site, Anhui Province, China, from the evening of January 2 to noon on January 3, 2017. During this event, vertical profiles of particulate matter (PM) and meteorological parameters within the lower troposphere (0-1000 m) were collected using a tethered balloon. This study assessed the evolution of the PM2.5 profile with the planetary boundary layer (PBL) structure and the effects of fog on the PM2.5 concentration. The results showed the following: (1) At the surface, the average diurnal variation in Aitken mode, accumulation mode and coarse mode particles had bimodal patterns before fog formation and was mainly influenced by diurnal variation in the mixing level depth (MLD). The aerosol number concentrations decreased remarkably, and the PM2.5 was strongly scavenged from 150 mu g/m(3) to 45 mu g/m(3) during the fog process. (2) In the vertical direction, the PM2.5 distribution was affected by the PBL height and the vertical fog structure. At 05:00 LT (local time) (i.e., early morning before the fog event), the PM2.5 concentration was slightly higher in the stable layer (260 mu g/m(3)) than in the residual layer (200 mu g/m(3)). At 14:00 LT (haze period), PM2.5 was well mixed below 500 m, with a concentration of 310 mu g/m(3). After 20:00 LT, when fog formed, PM2.5 was scavenged from the surface to the upper layers, and the scavenging height was controlled by the fog top height. (3) The vertical development of fog was promoted by turbulent mixing and radiation cooling at the fog top. Turbulent mixing enhanced the particle scavenging efficiency of fog droplets by the collision-coalescence process. The PM2.5 scavenging height was corresponded to the turbulence height. Therefore, turbulence development in the fog was the essential dynamic factor driving PM2.5 reduction. (C) 2019 Elsevier B.V. All rights reserved.
引用
收藏
页码:555 / 563
页数:9
相关论文
共 50 条
[1]   Observational Support for the Stability Dependence of the Bulk Richardson Number Across the Stable Boundary Layer [J].
Basu, S. ;
Holtslag, A. A. M. ;
Caporaso, L. ;
Riccio, A. ;
Steeneveld, G-J .
BOUNDARY-LAYER METEOROLOGY, 2014, 150 (03) :515-523
[2]   Small-scale structure of radiation fog: a large-eddy simulation study [J].
Bergot, Thierry .
QUARTERLY JOURNAL OF THE ROYAL METEOROLOGICAL SOCIETY, 2013, 139 (673) :1099-1112
[3]   A study of aerosol liquid water content based on hygroscopicity measurements at high relative humidity in the North China Plain [J].
Bian, Y. X. ;
Zhao, C. S. ;
Ma, N. ;
Chen, J. ;
Xu, W. Y. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2014, 14 (12) :6417-6426
[4]   Tethered balloon-born and ground-based measurements. of black carbon and particulate profiles within the lower troposphere during the foggy period in Delhi, India [J].
Bisht, D. S. ;
Tiwari, S. ;
Dumka, U. C. ;
Srivastava, A. K. ;
Safai, P. D. ;
Ghude, S. D. ;
Chate, D. M. ;
Rao, P. S. P. ;
Ali, K. ;
Prabhakaran, T. ;
Panickar, A. S. ;
Soni, V. K. ;
Attri, S. D. ;
Tunved, P. ;
Chakrabarty, R. K. ;
Hopke, P. K. .
SCIENCE OF THE TOTAL ENVIRONMENT, 2016, 573 :894-905
[5]   Temporal and spatial variations of fog in the Western Sudety Mts., Poland [J].
Blas, M ;
Sobik, M ;
Quiel, F ;
Netzel, P .
ATMOSPHERIC RESEARCH, 2002, 64 (1-4) :19-28
[6]   Fog water chemical composition in different geographic regions of Poland [J].
Blas, Marek ;
Polkowska, Zaneta ;
Sobik, Mieczyslaw ;
Klimaszewska, Kamila ;
Nowinski, Kamil ;
Namiesnik, Jacek .
ATMOSPHERIC RESEARCH, 2010, 95 (04) :455-469
[7]   Haze trends over the capital cities of 31 provinces in China, 1981-2005 [J].
Che, Huizheng ;
Zhang, Xiaoye ;
Li, Yang ;
Zhou, Zijiang ;
Qu, John J. ;
Hao, Xianjun .
THEORETICAL AND APPLIED CLIMATOLOGY, 2009, 97 (3-4) :235-242
[8]  
Cheng T T, 2010, J GEOPHYS RES-ATMOS, V115, pD23
[9]   Real-time secondary aerosol formation during a fog event in London [J].
Dall'Osto, M. ;
Harrison, R. M. ;
Coe, H. ;
Williams, P. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2009, 9 (07) :2459-2469
[10]   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