Chemical characterization of size-resolved aerosols in four seasons and hazy days in the megacity Beijing of China

被引:20
作者
Kang Sun [1 ,2 ]
Xingang Liu [2 ]
Jianwei Gu [1 ]
Yunpeng Li [1 ]
Yu Qu [3 ]
Junling An [3 ]
Jingli Wang [4 ]
Yuanhang Zhang [1 ]
Min Hu [1 ]
Fang Zhang [5 ]
机构
[1] College of Environmental Sciences and Engineering, Peking University
[2] State Key Laboratory of Water Environment Simulation, School of Environment, Beijing Normal University
[3] State Key Laboratory of Atmospheric Boundary Layer Physics and Atmospheric Chemistry, Institute of Atmospheric Physics,Chinese Academy of Sciences
[4] Institute for Urban Meteorology,China Meteorological Administration
[5] College of Global Change and Earth System Science, Beijing Normal University
基金
中国国家自然科学基金;
关键词
Chemical components; Size resolved aerosols; Seasonal variation; Haze day; Beijing;
D O I
暂无
中图分类号
X513 [粒状污染物];
学科分类号
0706 ; 070602 ;
摘要
Size-resolved aerosol samples were collected by MOUDI in four seasons in 2007 in Beijing. The PM10 and PM1.8mass concentrations were 166.0 ± 120.5 and 91.6 ± 69.7 μg/m3, respectively,throughout the measurement, with seasonal variation: nearly two times higher in autumn than in summer and spring. Serious fine particle pollution occurred in winter with the PM1.8/PM10 ratio of 0.63, which was higher than other seasons. The size distribution of PM showed obvious seasonal and diurnal variation, with a smaller fine mode peak in spring and in the daytime. OM(organic matter = 1.6 × OC(organic carbon)) and SIA(secondary inorganic aerosol) were major components of fine particles, while OM, SIA and Ca2+were major components in coarse particles. Moreover, secondary components, mainly SOA(secondary organic aerosol) and SIA,accounted for 46%–96% of each size bin in fine particles, which meant that secondary pollution existed all year. Sulfates and nitrates, primarily in the form of(NH4)2SO4, NH4NO3, Ca SO4, Na2SO4and K2SO4, calculated by the model ISORROPIA II, were major components of the solid phase in fine particles. The PM concentration and size distribution were similar in the four seasons on non-haze days, while large differences occurred on haze days, which indicated seasonal variation of PM concentration and size distribution were dominated by haze days. The SIA concentrations and fractions of nearly all size bins were higher on haze days than on non-haze days, which was attributed to heterogeneous aqueous reactions on haze days in the four seasons.
引用
收藏
页码:155 / 167
页数:13
相关论文
共 36 条
[31]  
The characteristics of PM 2.5 in Beijing, China[J] . Kebin He,Fumo Yang,Yongliang Ma,Qiang Zhang,Xiaohong Yao,Chak K Chan,Steven Cadle,Tai Chan,Patricia Mulawa.Atmospheric Environment . 2001 (29)
[32]  
Effect of particle mass size distribution on the deposition of aerosols in the human respiratory system[J] . Imre Salma,Imre Balásházy,Renate Winkler-Heil,Werner Hofmann,Gyula Záray.Journal of Aerosol Science . 2001 (1)
[33]  
Carbonaceous aerosol in urban and rural European atmospheres: estimation of secondary organic carbon concentrations[J] . L.M. Castro,C.A. Pio,Roy M. Harrison,D.J.T. Smith.Atmospheric Environment . 1999 (17)
[34]  
Characterisation of chemical species in PM 2.5 and PM 10 aerosols in Brisbane, Australia[J] . Y.C. Chan,R.W. Simpson,G.H. McTainsh,P.D. Vowles.Atmospheric Environment . 1997 (22)
[35]  
Acute Respiratory Effects of Particulate Air Pollution[J] . D W Dockery,C A Pope.Annual Review of Public Health . 1994
[36]  
A Microorifice Uniform Deposit Impactor (MOUDI): Description, Calibration, and Use[J] . Virgil A. Marple,Kenneth L. Rubow,Steven M. Behm.Aerosol Science and Technology . 1991 (4)