Secondary organic aerosol formation from photooxidation of naphthalene and alkylnaphthalenes: implications for oxidation of intermediate volatility organic compounds (IVOCs)

被引:263
作者
Chan, A. W. H. [1 ]
Kautzman, K. E. [1 ]
Chhabra, P. S. [1 ]
Surratt, J. D. [1 ]
Chan, M. N. [2 ]
Crounse, J. D. [1 ]
Kuerten, A. [2 ]
Wennberg, P. O. [2 ,3 ]
Flagan, R. C. [1 ,2 ]
Seinfeld, J. H. [1 ,2 ]
机构
[1] CALTECH, Div Chem & Chem Engn, Pasadena, CA 91125 USA
[2] CALTECH, Div Engn & Appl Sci, Pasadena, CA 91125 USA
[3] CALTECH, Div Geol & Planetary Sci, Pasadena, CA 91125 USA
基金
美国国家科学基金会;
关键词
AIR-POLLUTION SOURCES; RADICAL-INITIATED REACTIONS; GAS-PHASE REACTIONS; PHOTOCHEMICAL OXIDATION; AROMATIC-HYDROCARBONS; PARTICULATE MATTER; RATE CONSTANTS; SOA FORMATION; OH RADICALS; M-XYLENE;
D O I
10.5194/acp-9-3049-2009
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Current atmospheric models do not include secondary organic aerosol (SOA) production from gas-phase reactions of polycyclic aromatic hydrocarbons (PAHs). Recent studies have shown that primary emissions undergo oxidation in the gas phase, leading to SOA formation. This opens the possibility that low-volatility gas-phase precursors are a potentially large source of SOA. In this work, SOA formation from gas-phase photooxidation of naphthalene, 1-methylnaphthalene (1-MN), 2-methylnaphthalene (2-MN), and 1,2-dimethylnaphthalene (1,2-DMN) is studied in the Caltech dual 28-m(3) chambers. Under high-NOx conditions and aerosol mass loadings between 10 and 40 mu g m(-3), the SOA yields (mass of SOA per mass of hydrocarbon reacted) ranged from 0.19 to 0.30 for naphthalene, 0.19 to 0.39 for 1-MN, 0.26 to 0.45 for 2-MN, and constant at 0.31 for 1,2-DMN. Under low-NOx conditions, the SOA yields were measured to be 0.73, 0.68, and 0.58, for naphthalene, 1-MN, and 2-MN, respectively. The SOA was observed to be semivolatile under high-NOx conditions and essentially nonvolatile under low-NOx conditions, owing to the higher fraction of ring-retaining products formed under low-NOx conditions. When applying these measured yields to estimate SOA formation from primary emissions of diesel engines and wood burning, PAHs are estimated to yield 3-5 times more SOA than light aromatic compounds over photooxidation timescales of less than 12 h. PAHs can also account for up to 54% of the total SOA from oxidation of diesel emissions, representing a potentially large source of urban SOA.
引用
收藏
页码:3049 / 3060
页数:12
相关论文
共 46 条
[1]   DIURNAL CONCENTRATIONS OF VOLATILE POLYCYCLIC AROMATIC-HYDROCARBONS AND NITROARENES DURING A PHOTOCHEMICAL AIR-POLLUTION EPISODE IN GLENDORA, CALIFORNIA [J].
AREY, J ;
ATKINSON, R ;
ZIELINSKA, B ;
MCELROY, PA .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1989, 23 (03) :321-327
[2]   Atmospheric degradation of volatile organic compounds [J].
Atkinson, R ;
Arey, J .
CHEMICAL REVIEWS, 2003, 103 (12) :4605-4638
[3]   KINETICS AND PRODUCTS OF THE GAS-PHASE REACTIONS OF OH RADICALS AND N2O5 WITH NAPHTHALENE AND BIPHENYL [J].
ATKINSON, R ;
AREY, J ;
ZIELINSKA, B ;
ASCHMANN, SM .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1987, 21 (10) :1014-1022
[4]   Measurements of secondary organic aerosol from oxidation of cycloalkenes, terpenes, and m-xylene using an Aerodyne aerosol mass spectrometer [J].
Bahreini, R ;
Keywood, MD ;
Ng, NL ;
Varutbangkul, V ;
Gao, S ;
Flagan, RC ;
Seinfeld, JH ;
Worsnop, DR ;
Jimenez, JL .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2005, 39 (15) :5674-5688
[5]   Reaction of naphthalene and its derivatives with hydroxyl radicals in the gas phase [J].
Bunce, NJ ;
Liu, L ;
Zhu, J ;
Lane, DA .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1997, 31 (08) :2252-2259
[6]   GAS-CHROMATOGRAPHIC METHOD FOR MEASURING NITROGEN-DIOXIDE AND PEROXYACETYL NITRATE IN AIR WITHOUT COMPRESSED GAS-CYLINDERS [J].
BURKHARDT, MR ;
MANIGA, NI ;
STEDMAN, DH ;
PAUR, RJ .
ANALYTICAL CHEMISTRY, 1988, 60 (08) :816-819
[7]   Kinetic modeling of secondary organic aerosol formation: effects of particle- and gas-phase reactions of semivolatile products [J].
Chan, A. W. H. ;
Kroll, J. H. ;
Ng, N. L. ;
Seinfeld, J. H. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2007, 7 (15) :4135-4147
[8]   State-of-the-art chamber facility for studying atmospheric aerosol chemistry [J].
Cocker, DR ;
Flagan, RC ;
Seinfeld, JH .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2001, 35 (12) :2594-2601
[9]   Budget of organic carbon in a polluted atmosphere: Results from the New England Air Quality Study in 2002 [J].
de Gouw, JA ;
Middlebrook, AM ;
Warneke, C ;
Goldan, PD ;
Kuster, WC ;
Roberts, JM ;
Fehsenfeld, FC ;
Worsnop, DR ;
Canagaratna, MR ;
Pszenny, AAP ;
Keene, WC ;
Marchewka, M ;
Bertman, SB ;
Bates, TS .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2005, 110 (D16) :1-22
[10]   Field-deployable, high-resolution, time-of-flight aerosol mass spectrometer [J].
DeCarlo, Peter F. ;
Kimmel, Joel R. ;
Trimborn, Achim ;
Northway, Megan J. ;
Jayne, John T. ;
Aiken, Allison C. ;
Gonin, Marc ;
Fuhrer, Katrin ;
Horvath, Thomas ;
Docherty, Kenneth S. ;
Worsnop, Doug R. ;
Jimenez, Jose L. .
ANALYTICAL CHEMISTRY, 2006, 78 (24) :8281-8289