北京春季亚微米气溶胶的化学组分、特性及有机气溶胶来源解析
Chemical composition, characteristics and sources of PM_1 in Beijing spring
查看参考文献44篇
王瑛
1,2,3,4
黄汝锦
1,3,4
*
钟昊斌
1,2,3,4
段静
1,2,3,4
古仪方
1,2,3,4
文摘
|
基于颗粒物化学组分监测仪(Aerosol Chemical Speciation Monitor, ACSM)的在线实时观测,对北京春季亚微米气溶胶(PM_1)的化学组分和特性进行分析,并利用PMF & ME-2 (Positive Matrix Factorization & Multilinear Engine)源解析模式对其中的有机物进行来源解析。结果表明,在观测期间PM_1的浓度变化范围为2.40-249.10 µg·m~(-3),平均浓度58.0 µg·m~(-3),其中有机物为主要组分,占比41.4%。有机物的来源包括四个一次源:机动车排放源(hydrocarbon-like organic aerosol, HOA)、烹饪源(cooking organic aerosol,COA)、燃煤燃烧源(coal combustion organic aerosol,CCOA)、生物质燃烧源(biomass burning organic aerosol, BBOA)和一个二次有机源(oxygenated organic aerosol,OOA)。通过不同污染事件的对比结果表明,二次气溶胶在重污染期所占比重会明显上升,并且静稳气象条件也对污染的形成产生重要影响。 |
其他语种文摘
|
Background, aim, and scope Frequent occurrence of haze days has caused widespread concern in last decade. Atmospheric aerosol can absorb and scatter solar radiation, affect regional and global climate, reduce atmospheric visibility, and deposit in the human respiratory tract and lungs, affecting human health. Therefore, to perform a series of research on the chemical composition, characteristics, evolution mechanism of atmospheric aerosol and the source apportionment of organic aerosol, which are closely related to the formation of haze, is essential. This study aims to carry out targeted research on spring aerosol after heating season, hoping to get a comprehensive understand of the characteristics, sources and seasonal features of fine particulate matter (PM). Materials and methods A 13-day online real-time measurement was conducted using a Quadrupole-Aerosol Chemical Speciation Monitor (Q-ACSM) equipped with gaseous analyzers and an Aethalometer. The ACSM dataset was analyzed by the standard ACSM data analysis software in Igor Pro (WaveMetrics, Inc., Lake Oswego, Oregon USA). The chemical composition, mass concentrations and daily variations of the submicron aerosol were obtained after that. What's more, Positive Matrix Factorization (PMF) was used to perform the source apportionment on the ACSM organic data as implemented by the Multiliner Engine (ME-2) via the interface SoFi (Source Finder) coded in Igor Wavematrics. Results The average mass concentration of PM_1 during the whole observation period was 58.0 µg·m~(-3). OA was the component with the largest contribution (41.4%), followed by nitrate 27.3%, ammonium 15.0%, sulfate 7.9%, black carbon 4.8% and chloride 3.6%. According to result of the source apportionment, organic aerosol consisted of four primary sources: HOA, COA, CCOA, BBOA and a secondary source OOA. The mass fractions were 10.3%, 9.3%, 18.0%, 8.0% and 54.4%, respectively. Discussion The concentration of PM_1 during the whole observation period was significantly lower than that of the 2014 winter, which may be related to the end of heating season. OA was the most contributing component in PM_1, followed by nitrate. The vigorous implementation of desulfurization technology in coal-fired power plants had greatly reduced the emission of SO2, so that the sulfate concentration was low throughout the whole period. Factors of organic aerosol were well correlated with external markers, and the mass spectra were consistent with previous studies. In addition, different pollution events occurred during the observation period, we found the accumulation process of pollutants was slow, but the removal process was faster. Through the comparison among different pollution events, effects of gases, meteorological factors and regional transmission on the formation of atmospheric pollution were discussed in depth. Finally, the relationship between air mass transmission and pollution formation was also analyzed by using the backward trajectory. Conclusions Even though some pollution prevention and control measures have begun to bear fruit, the situation of air pollution in China is still very serious. Among the components of PM_1, organic aerosol and nitrate were the major components. OOA was the highest proportion factor of organic aerosol. This study found that compared with clean stage, the pollution period was often accompanied by higher relative humidity, lower wind speed and higher gaseous precursor concentrations. And the mass fraction of secondary aerosol (sulfate, nitrate and OOA) increased significantly from clean to pollution episode. Recommendations and perspectives These results show that it is of great significance to pay attention to the formation and oxidation mechanism of secondary aerosol (organic and inorganic) and to control emissions of precursors of secondary pollutants. |
来源
|
地球环境学报
,2019,10(6):556-566 【扩展库】
|
DOI
|
10.7515/JEE192014
|
关键词
|
亚微米气溶胶
;
来源解析
;
二次气溶胶
|
地址
|
1.
中国科学院地球环境研究所, 黄土与第四纪地质国家重点实验室, 西安, 710061
2.
中国科学院大学, 北京, 100049
3.
中国科学院气溶胶化学与物理重点实验室, 中国科学院气溶胶化学与物理重点实验室, 西安, 710061
4.
中国科学院第四纪科学与全球变化卓越创新中心, 中国科学院第四纪科学与全球变化卓越创新中心, 西安, 710061
|
语种
|
中文 |
文献类型
|
研究性论文 |
ISSN
|
1674-9901 |
基金
|
国家自然科学基金项目
;
国家重点研发计划项目
|
文献收藏号
|
CSCD:6663824
|
参考文献 共
44
共3页
|
1.
曹军骥. 我国PM_(2.5)污染现状与控制对策.
地球环境学报,2012,3(5):1030-1036
|
被引
19
次
|
|
|
|
2.
徐鹏.
北京城区亚微米气溶胶特征及其有机气溶胶的来源解析,2017
|
被引
8
次
|
|
|
|
3.
张养梅.
京津冀地区亚微米气溶胶特征及其变化的观测分析研究,2011
|
被引
3
次
|
|
|
|
4.
Alfarra M R. Identification of the mass spectral signature of organic aerosols from wood burning emissions.
Environmental Science & Technology,2007,41(16):5770-5777
|
被引
8
次
|
|
|
|
5.
Alicke B. OH formation by HONO photolysis during the BERLIOZ experiment.
Journal of Geophysical Research: Atmospheres,2003,108(D4)
|
被引
31
次
|
|
|
|
6.
Allan J D. Contributions from transport, solid fuel burning and cooking to primary organic aerosols in two UK cities.
Atmospheric Chemistry and Physics,2010,10(2):647-668
|
被引
13
次
|
|
|
|
7.
Canagaratna M R. Chemical and microphysical characterization of ambient aerosols with the aerodyne aerosol mass spectrometer.
Mass Spectrometry Reviews,2007,26(2):185-222
|
被引
54
次
|
|
|
|
8.
Cao J J. Winter and summer PM25 chemical compositions in fourteen Chinese cities.
Journal of the Air & Waste Management Association,2012,62(10):1214-1226
|
被引
86
次
|
|
|
|
9.
Chan C K. Air pollution in mega cities in China.
Atmospheric Environment,2008,42(1):1-42
|
被引
415
次
|
|
|
|
10.
Che H Z. Horizontal visibility trends in China 1981-2005.
Geophysical Research Letters,2007,34:L24706
|
被引
42
次
|
|
|
|
11.
Chen C. Characteristics and sources of submicron aerosols above the urban canopy (260 m) in Beijing, China, during the 2014 APEC summit.
Atmospheric Chemistry and Physics,2015,15(22):12879-12895
|
被引
10
次
|
|
|
|
12.
Crippa M. Wintertime aerosol chemical composition and source apportionment of the organic fraction in the metropolitan area of Paris.
Atmospheric Chemistry and Physics,2013,13(2):961-981
|
被引
10
次
|
|
|
|
13.
Dall'Osto M. Characterization of urban aerosol in Cork city (Ireland) using aerosol mass spectrometry.
Atmospheric Chemistry and Physics,2013,13(9):4997-5015
|
被引
3
次
|
|
|
|
14.
Duan J. Distinctions in source regions and formation mechanisms of secondary aerosol in Beijing from summer to winter.
Atmospheric Chemistry and Physics,19(15):10319-10334
|
被引
1
次
|
|
|
|
15.
Ebenstein A. New evidence on the impact of sustained exposure to air pollution on life expectancy from China's Huai River Policy.
Proceedings of the National Academy of Sciences of the United States of America,2017,114(39):10384-10389
|
被引
22
次
|
|
|
|
16.
Elser M. New insights into PM_(2.5) chemical composition and sources in two major cities in China during extreme haze events using aerosol mass spectrometry.
Atmospheric Chemistry and Physics,2016,16(5):3207-3225
|
被引
22
次
|
|
|
|
17.
Forster P. Changes in atmospheric constituents and in radiative forcing.
Climate change 2007: the physical science basis. Contribution of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change,2007
|
被引
28
次
|
|
|
|
18.
Han T T. Chemical apportionment of aerosol optical properties during the Asia-Pacific Economic Cooperation summit in Beijing, China.
Journal of Geophysical Research: Atmospheres,2015,120:12281-12295
|
被引
5
次
|
|
|
|
19.
He L Y. Characterization of high-resolution aerosol mass spectra of primary organic aerosol emissions from Chinese cooking and biomass burning.
Atmospheric Chemistry and Physics,2010,10(23):11535-11543
|
被引
18
次
|
|
|
|
20.
Huang R J. Source-specific health risk analysis on particulate trace elements: coal combustion and traffic emission as major contributors in wintertime Beijing.
Environmental Science & Technology,2018,52(19):10967-10974
|
被引
10
次
|
|
|
|
|