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	<journal>
		<journal_title>Atmospheric Chemistry and Physics</journal_title>
		<journal_url>www.atmos-chem-phys.net</journal_url>
		<issn>1680-7316</issn>
		<eissn>1680-7324</eissn>
		<volume_number>9</volume_number>
		<issue_number>9</issue_number>
		<publication_year>2009</publication_year>
	</journal>
	<doi>10.5194/acp-9-3049-2009</doi>
	<article_url>http://www.atmos-chem-phys.net/9/3049/2009/</article_url>
	<abstract_html>http://www.atmos-chem-phys.net/9/3049/2009/acp-9-3049-2009.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys.net/9/3049/2009/acp-9-3049-2009.pdf</fulltext_pdf>
	<start_page>3049</start_page>
	<end_page>3060</end_page>
	<publication_date>2009-05-12</publication_date>
	<article_title content_type="html">Secondary organic aerosol formation from photooxidation of naphthalene and alkylnaphthalenes: implications for oxidation of intermediate volatility organic compounds (IVOCs)</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>A. W. H. Chan</name>
		</author>
		<author numeration="2" affiliations="1">
			<name>K. E. Kautzman</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>P. S. Chhabra</name>
		</author>
		<author numeration="4" affiliations="1">
			<name>J. D. Surratt</name>
		</author>
		<author numeration="5" affiliations="2">
			<name>M. N. Chan</name>
		</author>
		<author numeration="6" affiliations="1">
			<name>J. D. Crounse</name>
		</author>
		<author numeration="7" affiliations="2,4">
			<name>A. Kürten</name>
		</author>
		<author numeration="8" affiliations="2,3">
			<name>P. O. Wennberg</name>
		</author>
		<author numeration="9" affiliations="1,2">
			<name>R. C. Flagan</name>
		</author>
		<author numeration="10" affiliations="1,2">
			<name>J. H. Seinfeld</name>
			<email>seinfeld@caltech.edu</email>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Division of Chemistry and Chemical Engineering, California Institute of Technology, Pasadena, CA, USA</affiliation>
		<affiliation numeration="2" content_type="html">Division of Engineering and Applied Sciences, California Institute of Technology, Pasadena, CA, USA</affiliation>
		<affiliation numeration="3" content_type="html">Division of Geological and Planetary Sciences, California Institute of Technology, Pasadena, CA, USA</affiliation>
		<affiliation numeration="4" content_type="html">current affiliation: Institute for Atmospheric and Environmental Sciences, Goethe-University Frankfurt am Main, Frankfurt, Germany</affiliation>
	</affiliations>
	<abstract content_type="html">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&lt;sup&gt;3&lt;/sup&gt; chambers. Under high-NO&lt;sub&gt;x&lt;/sub&gt; conditions and aerosol mass
loadings between 10 and 40 μg m&lt;sup&gt;&amp;minus;3&lt;/sup&gt;, 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-NO&lt;sub&gt;x&lt;/sub&gt; 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-NO&lt;sub&gt;x&lt;/sub&gt; conditions and
essentially nonvolatile under low-NO&lt;sub&gt;x&lt;/sub&gt; conditions, owing to the higher
fraction of ring-retaining products formed under low-NO&lt;sub&gt;x&lt;/sub&gt; 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.</abstract>
	<references>
		<reference numeration="1" content_type="text"> Arey, J., Atkinson, R., Zielinska, B., and Mcelroy, P A.: Diurnal concentrations of volatile polycyclic aromatic-hydrocarbons and nitroarenes during a photochemical air-pollution episode in Glendora, California, Environ. Sci. Technol., 23, 321–327, 1989. </reference>
		<reference numeration="2" content_type="text"> Atkinson, R. and Arey, J.: Atmospheric degradation of volatile organic compounds, Chem. Rev., 103, 4605–4638, 2003. </reference>
		<reference numeration="3" content_type="text"> Atkinson, R., Arey, J., Zielinska, B., and Aschmann, S M.: Kinetics and products of the gas-phase reactions of OH radicals and \chemN_2O_5 with naphthalene and biphenyl, Environ. Sci. Technol., 21, 1014–1022, 1987. </reference>
		<reference numeration="4" content_type="text"> Bahreini, R., Keywood, M D., Ng, N L., Varutbangkul, V., Gao, S., Flagan, R C., Seinfeld, J H., Worsnop, D R., and Jimenez, J L.: Measurements of secondary organic aerosol from oxidation of cycloalkenes, terpenes, and \textitm-xylene using an Aerodyne aerosol mass spectrometer, Environ. Sci. Technol., 39, 5674–5688, 2005. </reference>
		<reference numeration="5" content_type="text"> Bunce, N J., Liu, L., Zhu, J., and Lane, D A.: Reaction of naphthalene and its derivatives with hydroxyl radicals in the gas phase, Environ. Sci. Technol., 31, 2252–2259, 1997. </reference>
		<reference numeration="6" content_type="text"> Burkhardt, M R., Maniga, N I., Stedman, D H., and Paur, R J.: Gas-chromatographic method for measuring nitrogen-dioxide and peroxyacetyl nitrate in air without compressed gas-cylinders, Anal. Chem., 60, 816–819, 1988. </reference>
		<reference numeration="7" content_type="text"> Chan, A. W H., Kroll, J H., Ng, N L., and Seinfeld, J H.: Kinetic modeling of secondary organic aerosol formation: effects of particle- and gas-phase reactions of semivolatile products, Atmos. Chem. Phys., 7, 4135–4147, 2007. </reference>
		<reference numeration="8" content_type="text"> Cocker, D R., Flagan, R C., and Seinfeld, J H.: State-of-the-art chamber facility for studying atmospheric aerosol chemistry, Environ. Sci. Technol., 35, 2594–2601, 2001. </reference>
		<reference numeration="9" content_type="text"> de~Gouw, J A., Middlebrook, A M., Warneke, C., Goldan, P D., Kuster, W C., Roberts, J M., Fehsenfeld, F C., Worsnop, D R., Canagaratna, M R., Pszenny, A. A P., Keene, W C., Marchewka, M., Bertman, S B., and Bates, T S.: Budget of organic carbon in a polluted atmosphere: Results from the New England Air Quality Study in 2002, J. Geophys. Res.-Atmos., 110, \doi10.1029/2004JD005623, 2005. </reference>
		<reference numeration="10" content_type="text"> DeCarlo, P F., Kimmel, J R., Trimborn, A., Northway, M J., Jayne, J T., Aiken, A C., Gonin, M., Fuhrer, K., Horvath, T., Docherty, K S., Worsnop, D R., and Jimenez, J L.: Field-deployable, high-resolution, time-of-flight aerosol mass spectrometer, Anal. Chem., 78, 8281–8289, 2006. </reference>
		<reference numeration="11" content_type="text"> Docherty, K S., Stone, E A., Ulbrich, I M., DeCarlo, P F., Snyder, D C., Schauer, J J., Peltier, R E., Weber, R J., Murphy, S M., Seinfeld, J H., Grover, B D., Eatough, D J., and Jimenez, J L.: Apportionment of primary and secondary organic aerosols in southern California during the 2005 Study of Organic Aerosols in Riverside (SOAR-1), Environ. Sci. Technol., 42, 7655–7662, 2008. </reference>
		<reference numeration="12" content_type="text"> Donahue, N M., Robinson, A L., and Pandis, S N.: Atmospheric organic particulate matter: From smoke to secondary organic aerosol, Atmos. Environ., 43, 94–106, 2009. </reference>
		<reference numeration="13" content_type="text"> Goldstein, A H. and Galbally, I E.: Known and unexplored organic constituents in the earth&apos;s atmosphere, Environ. Sci. Technol., 41, 1514–1521, 2007. </reference>
		<reference numeration="14" content_type="text"> Grieshop, A P., Donahue, N M., and Robinson, A L.: Laboratory investigation of photochemical oxidation of organic aerosol from wood fires 2: analysis of aerosol mass spectrometer data, Atmos. Chem. Phys., 9, 2227–2240, 2009a. </reference>
		<reference numeration="15" content_type="text"> Grieshop, A P., Logue, J M., Donahue, N M., and Robinson, A L.: Laboratory investigation of photochemical oxidation of organic aerosol from wood fires 1: measurement and simulation of organic aerosol evolution, Atmos. Chem. Phys., 9, 1263–1277, 2009b. </reference>
		<reference numeration="16" content_type="text"> Heald, C L., Jacob, D J., Park, R J., Russell, L M., Huebert, B J., Seinfeld, J H., Liao, H., and Weber, R J.: A large organic aerosol source in the free troposphere missing from current models, Geophys. Res. Lett., 32, \doidoi:10.1029/2005GL023831, 2005. </reference>
		<reference numeration="17" content_type="text"> Henze, D K., Seinfeld, J H., Ng, N L., Kroll, J H., Fu, T.-M., Jacob, D J., and Heald, C L.: Global modeling of secondary organic aerosol formation from aromatic hydrocarbons: high- vs low-yield pathways, Atmos. Chem. Phys., 8, 2405–2420, 2008. </reference>
		<reference numeration="18" content_type="text"> Jordan, C E., Ziemann, P J., Griffin, R J., Lim, Y B., Atkinson, R., and Arey, J.: Modeling SOA formation from OH reactions with C8–C17 \textitn-alkanes, Atmos. Environ., 42, 8015–8026, 2008. </reference>
		<reference numeration="19" content_type="text"> Keywood, M D., Varutbangkul, V., Bahreini, R., Flagan, R C., and Seinfeld, J H.: Secondary organic aerosol formation from the ozonolysis of cycloalkenes and related compounds, Environ. Sci. Technol., 38, 4157–4164, 2004. </reference>
		<reference numeration="20" content_type="text"> Kroll, J H., Ng, N L., Murphy, S M., Flagan, R C., and Seinfeld, J H.: Secondary organic aerosol formation from isoprene photooxidation, Environ. Sci. Technol., 40, 1869–1877, 2006. </reference>
		<reference numeration="21" content_type="text"> Kwok, E. S C. and Atkinson, R.: Estimation of hydroxyl radical reaction-rate constants for gas-phase organic-compounds using a structure-reactivity relationship – an update, Atmos. Environ., 29, 1685–1695, 1995. </reference>
		<reference numeration="22" content_type="text"> Lim, Y B. and Ziemann, P J.: Products and mechanism of secondary organic aerosol formation from reactions of \textitn-alkanes with OH radicals in the presence of NOx, Environ. Sci. Technol., 39, 9229–9236, 2005. </reference>
		<reference numeration="23" content_type="text"> Mihele, C M., Wiebe, H A., and Lane, D A.: Particle formation and gas/particle partition measurements of the products of the naphthalene-OH radical reaction in a smog chamber, Polycycl. Aromat. Comp., 22, 729–736, 2002. </reference>
		<reference numeration="24" content_type="text"> Ng, N L., Kroll, J H., Keywood, M D., Bahreini, R., Varutbangkul, V., Flagan, R C., Seinfeld, J H., Lee, A., and Goldstein, A H.: Contribution of first- versus second-generation products to secondary organic aerosols formed in the oxidation of biogenic hydrocarbons, Environ. Sci. Technol., 40, 2283–2297, 2006. </reference>
		<reference numeration="25" content_type="text"> Ng, N L., Chhabra, P S., Chan, A. W H., Surratt, J D., Kroll, J H., Kwan, A J., McCabe, D C., Wennberg, P O., Sorooshian, A., Murphy, S M., Dalleska, N F., Flagan, R C., and Seinfeld, J H.: Effect of NO&lt;sub&gt;x&lt;/sub&gt; level on secondary organic aerosol (SOA) formation from the photooxidation of terpenes, Atmos. Chem. Phys., 7, 5159–5174, 2007a. </reference>
		<reference numeration="26" content_type="text"> Ng, N L., Kroll, J H., Chan, A. W H., Chhabra, P S., Flagan, R C., and Seinfeld, J H.: Secondary organic aerosol formation from m-xylene, toluene, and benzene, Atmos. Chem. Phys., 7, 3909–3922, 2007b. </reference>
		<reference numeration="27" content_type="text"> Nishino, N., Atkinson, R., and Arey, J.: Formation of nitro products from the gas-phase OH radical-initiated reactions of toluene, naphthalene, and biphenyl: effect of \chemNO_2 concentration, Environ. Sci. Technol., 42, 9203–9209, 2008. </reference>
		<reference numeration="28" content_type="text"> Nishino, N., Arey, J., and Atkinson, R.: Formation and reactions of 2-Formylcinnamaldehyde in the OH radical-initiated reaction of naphthalene, Environ. Sci. Technol., 43, 1349–1353, 2009. </reference>
		<reference numeration="29" content_type="text"> Odum, J R., Hoffmann, T., Bowman, F., Collins, D., Flagan, R C., and Seinfeld, J H.: Gas/particle partitioning and secondary organic aerosol yields, Environ. Sci. Technol., 30, 2580–2585, 1996. </reference>
		<reference numeration="30" content_type="text"> Odum, J R., Jungkamp, T. P W., Griffin, R J., Flagan, R C., and Seinfeld, J H.: The atmospheric aerosol-forming potential of whole gasoline vapor, Science, 276, 96–99, 1997. </reference>
		<reference numeration="31" content_type="text"> Phousongphouang, P T. and Arey, J.: Rate constants for the gas-phase reactions of a series of alkylnaphthalenes with the OH radical, Environ. Sci. Technol., 36, 1947–1952, 2002. </reference>
		<reference numeration="32" content_type="text"> Presto, A A., Hartz, K. E H., and Donahue, N M.: Secondary organic aerosol production from terpene ozonolysis. 2. Effect of NO&lt;sub&gt;x&lt;/sub&gt; concentration, Environ. Sci. Technol., 39, 7046–7054, 2005. </reference>
		<reference numeration="33" content_type="text"> Robinson, A L., Donahue, N M., Shrivastava, M K., Weitkamp, E A., Sage, A M., Grieshop, A P., Lane, T E., Pierce, J R., and Pandis, S N.: Rethinking organic aerosols: Semivolatile emissions and photochemical aging, Science, 315, 1259–1262, 2007. </reference>
		<reference numeration="34" content_type="text"> Sage, A M., Weitkamp, E A., Robinson, A L., and Donahue, N M.: Evolving mass spectra of the oxidized component of organic aerosol: results from aerosol mass spectrometer analyses of aged diesel emissions, Atmos. Chem. Phys., 8, 1139–1152, 2008. </reference>
		<reference numeration="35" content_type="text"> Sasaki, J., Aschmann, S M., Kwok, E. S C., Atkinson, R., and Arey, J.: Products of the gas-phase OH and \chemNO_3 radical-initiated reactions of naphthalene, Environ. Sci. Technol., 31, 3173–3179, 1997. </reference>
		<reference numeration="36" content_type="text"> Schauer, J J., Rogge, W F., Hildemann, L M., Mazurek, M A., and Cass, G R.: Source apportionment of airborne particulate matter using organic compounds as tracers, Atmos. Environ., 30, 3837–3855, 1996. </reference>
		<reference numeration="37" content_type="text"> Schauer, J J., Kleeman, M J., Cass, G R., and Simoneit, B R T.: Measurement of emissions from air pollution sources. 2. C-1 through C-30 organic compounds from medium duty diesel trucks, Environ. Sci. Technol., 33, 1578–1587, 1999a. </reference>
		<reference numeration="38" content_type="text"> Schauer, J J., Kleeman, M J., Cass, G R., and Simoneit, B. R T.: Measurement of emissions from air pollution sources. 1. C-1 through C-29 organic compounds from meat charbroiling, Environ. Sci. Technol., 33, 1566–1577, 1999b. </reference>
		<reference numeration="39" content_type="text"> Schauer, J J., Kleeman, M J., Cass, G R., and Simoneit, B. R T.: Measurement of emissions from air pollution sources. 3. C-1-C-29 organic compounds from fireplace combustion of wood, Environ. Sci. Technol., 35, 1716–1728, 2001. </reference>
		<reference numeration="40" content_type="text"> Schauer, J J., Kleeman, M J., Cass, G R., and Simoneit, B. R T.: Measurement of emissions from air pollution sources. 5. C-1-C-32 organic compounds from gasoline-powered motor vehicles, Environ. Sci. Technol., 36, 1169–1180, 2002a. </reference>
		<reference numeration="41" content_type="text"> Schauer, J J., Kleeman, M J., Cass, G R., and Simoneit, B. R T.: Measurement of emissions from air pollution sources. 4. C-1-C-27 organic compounds from cooking with seed oils, Environ. Sci. Technol., 36, 567–575, 2002b. </reference>
		<reference numeration="42" content_type="text"> Seinfeld, J H. and Pankow, J F.: Organic atmospheric particulate material, Annu. Rev. Phys. Chem., 54, 121–140, 2003. </reference>
		<reference numeration="43" content_type="text"> Volkamer, R., Jimenez, J L., San~Martini, F., Dzepina, K., Zhang, Q., Salcedo, D., Molina, L T., Worsnop, D R., and Molina, M J.: Secondary organic aerosol formation from anthropogenic air pollution: Rapid and higher than expected, Geophys. Res. Lett., 33, \doi10.1029/2006GL026899, 2006. </reference>
		<reference numeration="44" content_type="text"> Wang, L., Atkinson, R., and Arey, J.: Dicarbonyl products of the OH radical-initiated reactions of naphthalene and the C-1- and C-2-alkylnaphthalenes, Environ. Sci. Technol., 41, 2803–2810, 2007. </reference>
		<reference numeration="45" content_type="text"> Weitkamp, E A., Sage, A M., Pierce, J R., Donahue, N M., and Robinson, A L.: Organic aerosol formation from photochemical oxidation of diesel exhaust in a smog chamber, Environ. Sci. Technol., 41, 6969–6975, 2007. </reference>
		<reference numeration="46" content_type="text"> Zhang, Q., Jimenez, J L., Canagaratna, M R., Allan, J D., Coe, H., Ulbrich, I., Alfarra, M R., Takami, A., Middlebrook, A M., Sun, Y L., Dzepina, K., Dunlea, E., Docherty, K., DeCarlo, P F., Salcedo, D., Onasch, T., Jayne, J T., Miyoshi, T., Shimono, A., Hatakeyama, S., Takegawa, N., Kondo, Y., Schneider, J., Drewnick, F., Borrmann, S., Weimer, S., Demerjian, K., Williams, P., Bower, K., Bahreini, R., Cottrell, L., Griffin, R J., Rautiainen, J., Sun, J Y., Zhang, Y M., and Worsnop, D R.: Ubiquity and dominance of oxygenated species in organic aerosols in anthropogenically-influenced Northern Hemisphere midlatitudes, Geophys. Res. Lett., 34, \doi10.1029/2007GL029979, 2007. </reference>
	</references>
</article>

