Secondary organic aerosol formation from idling gasoline passenger vehicle emissions investigated in a smog chamber

被引:117
作者
Nordin, E. Z. [1 ]
Eriksson, A. C. [2 ]
Roldin, P. [2 ]
Nilsson, P. T. [1 ]
Carlsson, J. E. [1 ]
Kajos, M. K. [3 ]
Hellen, H. [4 ]
Wittbom, C. [2 ]
Rissler, J. [1 ]
Londahl, J. [1 ]
Swietlicki, E. [2 ]
Svenningsson, B. [2 ]
Bohgard, M. [1 ]
Kulmala, M. [2 ,3 ]
Hallquist, M. [5 ]
Pagels, J. H. [1 ]
机构
[1] Lund Univ, S-22100 Lund, Sweden
[2] Lund Univ, Div Nucl Phys, S-22100 Lund, Sweden
[3] Univ Helsinki, Dept Phys, Helsinki 00014, Finland
[4] Finnish Meteorol Inst, FIN-00101 Helsinki, Finland
[5] Univ Gothenburg, Dept Chem, S-41296 Gothenburg, Sweden
基金
瑞典研究理事会;
关键词
MASS-SPECTROMETER; M-XYLENE; PTR-MS; PHOTOCHEMICAL OXIDATION; HIGH-RESOLUTION; MOTOR-VEHICLES; AIR-POLLUTION; COLD-START; PHOTOOXIDATION; IMPACT;
D O I
10.5194/acp-13-6101-2013
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Gasoline vehicles have recently been pointed out as potentially the main source of anthropogenic secondary organic aerosol (SOA) in megacities. However, there is a lack of laboratory studies to systematically investigate SOA formation in real-world exhaust. In this study, SOA formation from pure aromatic precursors, idling and cold start gasoline exhaust from three passenger vehicles (EURO2-EURO4) were investigated with photo-oxidation experiments in a 6 m(3) smog chamber. The experiments were carried out down to atmospherically relevant organic aerosol mass concentrations. The characterization instruments included a high-resolution aerosol mass spectrometer and a proton transfer mass spectrometer. It was found that gasoline exhaust readily forms SOA with a signature aerosol mass spectrum similar to the oxidized organic aerosol that commonly dominates the organic aerosol mass spectra downwind of urban areas. After a cumulative OH exposure of similar to 5 x 10(6) cm(-3) h, the formed SOA was 1-2 orders of magnitude higher than the primary OA emissions. The SOA mass spectrum from a relevant mixture of traditional light aromatic precursors gave f(43) (mass fraction at m/z = 43), approximately two times higher than to the gasoline SOA. However O:C and H:C ratios were similar for the two cases. Classical C-6-C-9 light aromatic precursors were responsible for up to 60% of the formed SOA, which is significantly higher than for diesel exhaust. Important candidates for additional precursors are higher-order aromatic compounds such as C-10 and C-11 light aromatics, naphthalene and methyl-naphthalenes. We conclude that approaches using only light aromatic precursors give an incomplete picture of the magnitude of SOA formation and the SOA composition from gasoline exhaust.
引用
收藏
页码:6101 / 6116
页数:16
相关论文
共 53 条
[1]   O/C and OM/OC ratios of primary, secondary, and ambient organic aerosols with high-resolution time-of-flight aerosol mass spectrometry [J].
Aiken, Allison C. ;
Decarlo, Peter F. ;
Kroll, Jesse H. ;
Worsnop, Douglas R. ;
Huffman, J. Alex ;
Docherty, Kenneth S. ;
Ulbrich, Ingrid M. ;
Mohr, Claudia ;
Kimmel, Joel R. ;
Sueper, Donna ;
Sun, Yele ;
Zhang, Qi ;
Trimborn, Achim ;
Northway, Megan ;
Ziemann, Paul J. ;
Canagaratna, Manjula R. ;
Onasch, Timothy B. ;
Alfarra, M. Rami ;
Prevot, Andre S. H. ;
Dommen, Josef ;
Duplissy, Jonathan ;
Metzger, Axel ;
Baltensperger, Urs ;
Jimenez, Jose L. .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2008, 42 (12) :4478-4485
[2]   Gasoline emissions dominate over diesel in formation of secondary organic aerosol mass [J].
Bahreini, R. ;
Middlebrook, A. M. ;
de Gouw, J. A. ;
Warneke, C. ;
Trainer, M. ;
Brock, C. A. ;
Stark, H. ;
Brown, S. S. ;
Dube, W. P. ;
Gilman, J. B. ;
Hall, K. ;
Holloway, J. S. ;
Kuster, W. C. ;
Perring, A. E. ;
Prevot, A. S. H. ;
Schwarz, J. P. ;
Spackman, J. R. ;
Szidat, S. ;
Wagner, N. L. ;
Weber, R. J. ;
Zotter, P. ;
Parrish, D. D. .
GEOPHYSICAL RESEARCH LETTERS, 2012, 39
[3]   Three-way-catalyst induced benzene formation: A precursor study [J].
Bruehlmann, Stefan ;
Novak, Philippe ;
Lienemann, Peter ;
Trottmann, Matthias ;
Gfeller, Urs ;
Zwicky, Christoph N. ;
Bommer, Bastian ;
Huber, Hugo ;
Wolfensberger, Max ;
Heeb, Norbert V. .
APPLIED CATALYSIS B-ENVIRONMENTAL, 2007, 70 (1-4) :276-283
[4]   A new environmental chamber for evaluation of gas-phase chemical mechanisms and secondary aerosol formation [J].
Carter, WPL ;
Cocker, DR ;
Fitz, DR ;
Malkina, IL ;
Bumiller, K ;
Sauer, CG ;
Pisano, JT ;
Bufalino, C ;
Song, C .
ATMOSPHERIC ENVIRONMENT, 2005, 39 (40) :7768-7788
[5]   Secondary organic aerosol formation from photooxidation of naphthalene and alkylnaphthalenes: implications for oxidation of intermediate volatility organic compounds (IVOCs) [J].
Chan, A. W. H. ;
Kautzman, K. E. ;
Chhabra, P. S. ;
Surratt, J. D. ;
Chan, M. N. ;
Crounse, J. D. ;
Kuerten, A. ;
Wennberg, P. O. ;
Flagan, R. C. ;
Seinfeld, J. H. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2009, 9 (09) :3049-3060
[6]   Elemental composition and oxidation of chamber organic aerosol [J].
Chhabra, P. S. ;
Ng, N. L. ;
Canagaratna, M. R. ;
Corrigan, A. L. ;
Russell, L. M. ;
Worsnop, D. R. ;
Flagan, R. C. ;
Seinfeld, J. H. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2011, 11 (17) :8827-8845
[7]   Impact of aftertreatment devices on primary emissions and secondary organic aerosol formation potential from in-use diesel vehicles: results from smog chamber experiments [J].
Chirico, R. ;
DeCarlo, P. F. ;
Heringa, M. F. ;
Tritscher, T. ;
Richter, R. ;
Prevot, A. S. H. ;
Dommen, J. ;
Weingartner, E. ;
Wehrle, G. ;
Gysel, M. ;
Laborde, M. ;
Baltensperger, U. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2010, 10 (23) :11545-11563
[8]   Effects of low temperature on the cold start gaseous emissions from light duty vehicles fuelled by ethanol-blended gasoline [J].
Clairotte, M. ;
Adam, T. W. ;
Zardini, A. A. ;
Manfredi, U. ;
Martini, G. ;
Krasenbrink, A. ;
Vicet, A. ;
Tournie, E. ;
Astorga, C. .
APPLIED ENERGY, 2013, 102 :44-54
[9]   The effect of water on gas-particle partitioning of secondary organic aerosol:: II.: m-xylene and 1,3,5-trimethylbenzene photooxidation systems [J].
Cocker, DR ;
Mader, BT ;
Kalberer, M ;
Flagan, RC ;
Seinfeld, JH .
ATMOSPHERIC ENVIRONMENT, 2001, 35 (35) :6073-6085
[10]   Sources of particulate matter in the northeastern United States in summer: 1. Direct emissions and secondary formation of organic matter in urban plumes [J].
de Gouw, J. A. ;
Brock, C. A. ;
Atlas, E. L. ;
Bates, T. S. ;
Fehsenfeld, F. C. ;
Goldan, P. D. ;
Holloway, J. S. ;
Kuster, W. C. ;
Lerner, B. M. ;
Matthew, B. M. ;
Middlebrook, A. M. ;
Onasch, T. B. ;
Peltier, R. E. ;
Quinn, P. K. ;
Senff, C. J. ;
Stohl, A. ;
Sullivan, A. P. ;
Trainer, M. ;
Warneke, C. ;
Weber, R. J. ;
Williams, E. J. .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2008, 113 (D8)