Vehicular Emissions Enhanced Ammonia Concentrations in Winter Mornings: Insights from Diurnal Nitrogen Isotopic Signatures

被引:60
作者
Gu, Mengna [1 ,2 ]
Pan, Yuepeng [1 ,2 ]
Walters, Wendell W. [3 ,4 ]
Sun, Qian [1 ,2 ]
Song, Linlin [2 ,5 ]
Wang, Yuesi [1 ]
Xue, Yifeng [6 ]
Fang, Yunting [5 ]
机构
[1] Chinese Acad Sci, Inst Atmospher Phys, State Key Lab Atmospher Boundary Layer Phys & Atm, Beijing 100029, Peoples R China
[2] Univ Chinese Acad Sci, Sch Earth & Planetary, Beijing 100049, Peoples R China
[3] Brown Univ, Dept Earth Environm & Planetary Sci, Providence, RI 02912 USA
[4] Brown Univ, Inst Brown Environm & Soc, Providence, RI 02912 USA
[5] Chinese Acad Sci, Inst Appl Ecol, CAS Key Lab Forest Ecol & Management, Shenyang 110016, Liaoning, Peoples R China
[6] Beijing Municipal Res Inst Ecoenvironm Protect, Natl Engn Res Ctr Urban Environm Pollut Control, Beijing 100037, Peoples R China
基金
中国国家自然科学基金;
关键词
ammonia; nitrogen isotope; source apportionment; morning peak; diurnal variations; haze pollution; ATMOSPHERIC AMMONIA; SOURCE APPORTIONMENT; URBAN-ENVIRONMENT; AIR-POLLUTION; DEPOSITION; SAMPLERS; EXCHANGE; NITRATE; TRENDS; CHINA;
D O I
10.1021/acs.est.1c05884
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
A general feature in the diurnal cycle of atmospheric ammonia (NH3) concentrations is a morning spike that typically occurs around 07:00 to 10:00 (LST). Current hypotheses to explain this morning's NH3 increase remain elusive, and there is still no consensus whether traffic emissions are among the major sources of urban NH3. Here, we confirmed that the NH3 morning pulse in urban Beijing is a universal feature, with an annual occurrence frequency of 73.0% and a rapid growth rate (>20%) in winter. The stable nitrogen isotopic composition of NH3 (6 45 N-NH3) in winter also exhibited a significant diurnal variation with an obvious morning peak at 07:00 to 10:00 (-18.6 parts per thousand, mass-weighted mean), higher than other times of the day (-26.3 parts per thousand). This diurnal pattern suggests that a large fraction of NH3 in the morning originated from nonagricultural sources, for example, power plants, vehicles, and coal combustion that tend to have higher delta N-15-NH3 emission signatures relative to agricultural emissions. In particular, the contribution from vehicular emissions increased from 18% (00:00 to 07:00) to 40% (07:00 to 10:00), while the contribution of fertilizer sources to NH3 was reduced from 15.8% at 00:00 to 07:00 to 5.2% at 07:00 to 10:00. We concluded that NH3 concentrations in winter mornings in urban Beijing were indeed enhanced by vehicle emissions, which should be considered in air pollution regulations.
引用
收藏
页码:1578 / 1585
页数:8
相关论文
共 53 条
[1]   Cavity ring-down spectroscopy: Experimental schemes and applications [J].
Berden, G ;
Peeters, R ;
Meijer, G .
INTERNATIONAL REVIEWS IN PHYSICAL CHEMISTRY, 2000, 19 (04) :565-607
[2]   NEW REFERENCE MATERIALS FOR NITROGEN-ISOTOPE-RATIO MEASUREMENTS [J].
BOHLKE, JK ;
GWINN, CJ ;
COPLEN, TB .
GEOSTANDARDS NEWSLETTER, 1993, 17 (01) :159-164
[3]   Increasing ammonia concentration trends in large regions of the USA derived from the NADP/AMoN network [J].
Butler, T. ;
Vermeylen, F. ;
Lehmann, C. M. ;
Likens, G. E. ;
Puchalski, M. .
ATMOSPHERIC ENVIRONMENT, 2016, 146 :132-140
[4]   Traffic-related air pollution modeling during the 2008 Beijing Olympic Games: The effects of an odd-even day traffic restriction scheme [J].
Cai, Hao ;
Xie, Shaodong .
SCIENCE OF THE TOTAL ENVIRONMENT, 2011, 409 (10) :1935-1948
[5]   Source apportionment of atmospheric ammonia before, during, and after the 2014 APEC summit in Beijing using stable nitrogen isotope signatures [J].
Chang, Yunhua ;
Liu, Xuejun ;
Deng, Congrui ;
Dore, Anthony J. ;
Zhuang, Guoshun .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2016, 16 (18) :11635-11647
[6]  
Driscoll CT, 2001, BIOSCIENCE, V51, P180, DOI 10.1641/0006-3568(2001)051[0180:ADITNU]2.0.CO
[7]  
2
[8]   The influence of gas-particle partitioning and surface-atmosphere exchange on ammonia during BAQS-Met [J].
Ellis, R. A. ;
Murphy, J. G. ;
Markovic, M. Z. ;
VandenBoer, T. C. ;
Makar, P. A. ;
Brook, J. ;
Mihele, C. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2011, 11 (01) :133-145
[9]   Examining the transport of ammonia emissions across landscapes using nitrogen isotope ratios [J].
Felix, J. David ;
Elliott, Emily M. ;
Gish, Timothy ;
Maghirang, Ronaldo ;
Cambal, Leah ;
Clougherty, Jane .
ATMOSPHERIC ENVIRONMENT, 2014, 95 :563-570
[10]   Characterizing the isotopic composition of atmospheric ammonia emission sources using passive samplers and a combined oxidation-bacterial denitrifier approach [J].
Felix, J. David ;
Elliott, Emily M. ;
Gish, Timothy J. ;
McConnell, Laura L. ;
Shaw, Stephanie L. .
RAPID COMMUNICATIONS IN MASS SPECTROMETRY, 2013, 27 (20) :2239-2246