Secondary organic aerosol formation from gasoline vehicle emissions in a new mobile environmental reaction chamber

被引:192
作者
Platt, S. M. [1 ]
El Haddad, I. [1 ]
Zardini, A. A. [2 ]
Clairotte, M. [2 ]
Astorga, C. [2 ]
Wolf, R. [1 ]
Slowik, J. G. [1 ]
Temime-Roussel, B. [3 ]
Marchand, N. [3 ]
Jezek, I. [4 ]
Drinovec, L. [4 ]
Mocnik, G. [4 ]
Moehler, O. [5 ]
Richter, R. [1 ]
Barmet, P. [1 ]
Bianchi, F. [1 ]
Baltensperger, U. [1 ]
Prevot, A. S. H. [1 ]
机构
[1] Paul Scherrer Inst, Lab Atmospher Chem, CH-5232 Villigen, Switzerland
[2] Commiss European Communities, Joint Res Ctr, Inst Energy & Transport, Sustainable Transport Unit, I-21027 Ispra, Italy
[3] Univ Aix Marseille, CNRS, LCE FRE 3416, F-13331 Marseille, France
[4] Aerosol Doo, Ljubljana 100, Slovenia
[5] Karlsruhe Inst Technol, Inst Meteorol & Climate Res, D-76021 Karlsruhe, Germany
基金
瑞士国家科学基金会;
关键词
GAS-PHASE REACTIONS; ATMOSPHERIC CHEMISTRY; HIGH-RESOLUTION; COLLECTION EFFICIENCIES; PHOTOCHEMICAL DATA; MASS-SPECTROMETER; DIESEL; OXIDATION; IMPACT; COMPONENTS;
D O I
10.5194/acp-13-9141-2013
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
We present a new mobile environmental reaction chamber for the simulation of the atmospheric aging of different emission sources without limitation from the instruments or facilities available at any single site. Photochemistry is simulated using a set of 40 UV lights (total power 4 KW). Characterisation of the emission spectrum of these lights shows that atmospheric aging of emissions may be simulated over a range of temperatures (-7 to 25 degrees C). A photolysis rate of NO2, J(NO2), of (8.0 +/- 0.7) x 10(-3) s(-1) was determined at 25 degrees C. We demonstrate the utility of this new system by presenting results on the aging (OH = 12x10(6) cm(-3) h) of emissions from a modern (Euro 5) gasoline car operated during a driving cycle (New European Driving Cycle, NEDC) on a chassis dynamometer in a vehicle test cell. Emissions from the entire NEDC were sampled and aged in the chamber. Total organic aerosol (OA; primary organic aerosol (POA) emission + secondary organic aerosol (SOA) formation) was (369.8-397.5) 10(-3) g kg(-1) fuel, or (13.2-15.4) x 10(-3) g km(-1), after aging, with aged OA/POA in the range 9-15. A thorough investigation of the composition of the gas phase emissions suggests that the observed SOA is from previously unconsidered precursors and processes. This large enhancement in particulate matter mass from gasoline vehicle aerosol emissions due to SOA formation, if it occurs across a wider range of gasoline vehicles, would have significant implications for our understanding of the contribution of on-road gasoline vehicles to ambient aerosols.
引用
收藏
页码:9141 / 9158
页数:18
相关论文
共 50 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]  
[Anonymous], 1970, OFFICIAL J EUROPEAN, VL076, P1
[3]   Evaluated kinetic and photochemical data for atmospheric chemistry: Volume II - gas phase reactions of organic species [J].
Atkinson, R. ;
Baulch, D. L. ;
Cox, R. A. ;
Crowley, J. N. ;
Hampson, R. F. ;
Hynes, R. G. ;
Jenkin, M. E. ;
Rossi, M. J. ;
Troe, J. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2006, 6 :3625-4055
[4]   Evaluated kinetic and photochemical data for atmospheric chemistry:: Volume I -: gas phase reactions of Ox, HOx, NOx and SOx species [J].
Atkinson, R ;
Baulch, DL ;
Cox, RA ;
Crowley, JN ;
Hampson, RF ;
Hynes, RG ;
Jenkin, ME ;
Rossi, MJ ;
Troe, J .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2004, 4 :1461-1738
[5]  
Bahreini R., 2012, Geophys. Res. Lett, V39, pL06805, DOI [DOI 10.1029/2011GL050718, 10.1029/2011GL050718.]
[6]  
Barlow T. J., 2009, REF BOOK DRIVING CYC
[7]   OH clock determination by proton transfer reaction mass spectrometry at an environmental chamber [J].
Barmet, P. ;
Dommen, J. ;
DeCarlo, P. F. ;
Tritscher, T. ;
Praplan, A. P. ;
Platt, S. M. ;
Prevot, A. S. H. ;
Donahue, N. M. ;
Baltensperger, U. .
ATMOSPHERIC MEASUREMENT TECHNIQUES, 2012, 5 (03) :647-656
[8]   A technology-based global inventory of black and organic carbon emissions from combustion [J].
Bond, TC ;
Streets, DG ;
Yarber, KF ;
Nelson, SM ;
Woo, JH ;
Klimont, Z .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2004, 109 (D14) :D14203
[9]  
Carter W.P. L., 1995, ENV CHAMBER STUDIES
[10]   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