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<article language="en">
	<journal>
		<journal_title>Atmospheric Chemistry and Physics Discussions</journal_title>
		<journal_url>www.atmos-chem-phys-discuss.net</journal_url>
		<issn>1680-7367</issn>
		<eissn>1680-7375</eissn>
		<volume_number>9</volume_number>
		<issue_number>2</issue_number>
		<publication_year>2009</publication_year>
	</journal>
	<doi>10.5194/acpd-9-8223-2009</doi>
	<article_url>http://www.atmos-chem-phys-discuss.net/9/8223/2009/</article_url>
	<abstract_html>http://www.atmos-chem-phys-discuss.net/9/8223/2009/acpd-9-8223-2009.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys-discuss.net/9/8223/2009/acpd-9-8223-2009.pdf</fulltext_pdf>
	<start_page>8223</start_page>
	<end_page>8260</end_page>
	<publication_date>2009-03-27</publication_date>
	<article_title content_type="html">New particle formation from the oxidation of direct emissions of pine seedlings</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>L. Q. Hao</name>
			<email>liqing@uku.fi</email>
		</author>
		<author numeration="2" affiliations="2">
			<name>P. Yli-Pirilä</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>P. Tiitta</name>
		</author>
		<author numeration="4" affiliations="1">
			<name>S. Romakkaniemi</name>
		</author>
		<author numeration="5" affiliations="1">
			<name>P. Vaattovaara</name>
		</author>
		<author numeration="6" affiliations="3">
			<name>M. K. Kajos</name>
		</author>
		<author numeration="7" affiliations="3">
			<name>J. Rinne</name>
		</author>
		<author numeration="8" affiliations="2">
			<name>J. Heijari</name>
		</author>
		<author numeration="9" affiliations="1">
			<name>A. Kortelainen</name>
		</author>
		<author numeration="10" affiliations="1">
			<name>P. Miettinen</name>
		</author>
		<author numeration="11" affiliations="4">
			<name>J. H. Kroll</name>
		</author>
		<author numeration="12" affiliations="2">
			<name>J.-K. Holopainen</name>
		</author>
		<author numeration="13" affiliations="1">
			<name>J. Joutsensaari</name>
		</author>
		<author numeration="14" affiliations="3">
			<name>M. Kumala</name>
		</author>
		<author numeration="15" affiliations="4">
			<name>D. R. Worsnop</name>
		</author>
		<author numeration="16" affiliations="1,5">
			<name>A. Laaksonen</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Department of Physics, University of Kuopio, Kuopio 70211, Finland</affiliation>
		<affiliation numeration="2" content_type="html">Department of Environmental Sciences, University of Kuopio, Kuopio 70211, Finland</affiliation>
		<affiliation numeration="3" content_type="html">Department of Physics, P.O. Box 68, University of Helsinki, Helsinki 00014, Finland</affiliation>
		<affiliation numeration="4" content_type="html">Aerodyne Research, Inc., Billerica, MA, 08121-3976, USA</affiliation>
		<affiliation numeration="5" content_type="html">Finnish Meteorological Institute, Helsinki 00101, Finland</affiliation>
	</affiliations>
	<abstract content_type="html">Measurements of particle formation following the gas phase oxidation of volatile organic
      compounds (VOCs) emitted by Scots pine (&lt;i&gt;Pinus sylvestris L.&lt;/i&gt;) seedlings are
      reported. Particle nucleation and condensational growth both from ozone (O&lt;sub&gt;3&lt;/sub&gt;) and
      hydroxyl radical (OH) initiated oxidation of pine emissions (about
      20–120 ppb) were investigated in a~smog chamber. During experiments,
      tetramethylethylene (TME) and 2-butanol were added to control the concentrations of
      O&lt;sub&gt;3&lt;/sub&gt; and OH. Particle nucleation and condensational growth rates were
      interpreted with a chemical kinetics model. Scots pine emissions mainly included
      α-pinene, β-pinene, &amp;Delta;&lt;sup&gt;3&lt;/sup&gt;-carene, limonene, myrcene,
      β-phellandrene and isoprene, composing more than 95% of total emissions. Modeled OH
      concentration in the O&lt;sub&gt;3&lt;/sub&gt;+OH induced experiments was at a level of
      ~10&lt;sup&gt;6&lt;/sup&gt; molecular cm&lt;sup&gt;&amp;minus;3&lt;/sup&gt;. Our results demonstrate that OH-initiated
      oxidation of VOCs plays an important role in the nucleation process during the initial new
      particle formation stage. The highest average nucleation rate of 360 cm&lt;sup&gt;&amp;minus;3&lt;/sup&gt; s&lt;sup&gt;&amp;minus;1&lt;/sup&gt;
      was observed for the OH-dominated nucleation events and the lowest aerosol mean
      formation rate less than 0.5 cm&lt;sup&gt;&amp;minus;3&lt;/sup&gt; s&lt;sup&gt;&amp;minus;1&lt;/sup&gt; for the case with only O&lt;sub&gt;3&lt;/sub&gt;
      present as an oxidant. On the other hand, ozonolysis of monoterpenes appears to be much more
      efficient to the aerosol growth process following nucleation. Higher contributions of more
      oxygenated products to the SOA mass loadings from OH-dominating oxidation systems
      were found as compared to the ozonolysis systems. Comparison of mass and volume
      distributions from the aerosol mass spectrometer and differential mobility analyzer yields
      estimated effective density of these SOA to be 1.34&amp;plusmn;0.06 g cm&lt;sup&gt;&amp;minus;3&lt;/sup&gt; with the
      OH plus O&lt;sub&gt;3&lt;/sub&gt; initiated oxidation systems and
      1.38&amp;plusmn;0.03 g cm&lt;sup&gt;&amp;minus;3&lt;/sup&gt; with the ozonolysis dominated chemistry.</abstract>
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</article>

