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<article language="en">
	<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>8</volume_number>
		<issue_number>14</issue_number>
		<publication_year>2008</publication_year>
	</journal>
	<doi>10.5194/acp-8-3899-2008</doi>
	<article_url>http://www.atmos-chem-phys.net/8/3899/2008/</article_url>
	<abstract_html>http://www.atmos-chem-phys.net/8/3899/2008/acp-8-3899-2008.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys.net/8/3899/2008/acp-8-3899-2008.pdf</fulltext_pdf>
	<start_page>3899</start_page>
	<end_page>3917</end_page>
	<publication_date>2008-07-22</publication_date>
	<article_title content_type="html">Observations of HNO&lt;sub&gt;3&lt;/sub&gt;, &amp;Sigma;AN, &amp;Sigma;PN and NO&lt;sub&gt;2&lt;/sub&gt; fluxes: evidence for rapid HO&lt;sub&gt;x&lt;/sub&gt; chemistry within a pine forest canopy</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>D. K. Farmer</name>
		</author>
		<author numeration="2" affiliations="1,2,3">
			<name>R. C. Cohen</name>
			<email>rccohen@berkeley.edu</email>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Department of Chemistry, University of California Berkeley, Berkeley, CA, USA</affiliation>
		<affiliation numeration="2" content_type="html">Department of Earth and Planetary Science, University of California Berkeley, Berkeley, CA 94720, USA</affiliation>
		<affiliation numeration="3" content_type="html">Energy and Environment Technologies Division, Lawrence Berkeley National Laboratory, Berkeley, CA 94720, USA</affiliation>
	</affiliations>
	<abstract content_type="html">Measurements of exchange of reactive nitrogen oxides between the atmosphere
and a ponderosa pine forest in the Sierra Nevada Mountains are reported.
During winter, we observe upward fluxes of NO&lt;sub&gt;2&lt;/sub&gt;, and downward fluxes of
total peroxy and peroxy acyl nitrates (&amp;Sigma;PNs), total gas and particle
phase alkyl and multifunctional alkyl nitrates (&amp;Sigma;ANs&lt;sub&gt;(g+p)&lt;/sub&gt;), and
the sum of gaseous HNO&lt;sub&gt;3&lt;/sub&gt; and semi-volatile NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;minus;&lt;/sup&gt; particles
(HNO&lt;sub&gt;3(g+p)&lt;/sub&gt;). We use calculations of the vertical profile and flux of
NO, partially constrained by observations, to show that net midday &amp;Sigma;NO&lt;sub&gt;yi&lt;/sub&gt; fluxes in winter are –4.9 ppt m s&lt;sup&gt;&amp;minus;1&lt;/sup&gt;. The signs and
magnitudes of these wintertime individual and &amp;Sigma;NO&lt;sub&gt;yi&lt;/sub&gt; fluxes are
in the range of prior measurements. In contrast, during summer, we observe
downward fluxes only of &amp;Sigma;ANs&lt;sub&gt;(g+p)&lt;/sub&gt;, and upward fluxes of
HNO&lt;sub&gt;3(g+p)&lt;/sub&gt;, &amp;Sigma;PNs and NO&lt;sub&gt;2&lt;/sub&gt; with signs and magnitudes that are
unlike most, if not all, previous observations and analyses of fluxes of
individual nitrogen oxides. The results imply that the mechanisms
contributing to NO&lt;sub&gt;y&lt;/sub&gt; fluxes, at least at this site, are much more
complex than previously recognized. We show that the observations of upward
fluxes of HNO&lt;sub&gt;3(g+p)&lt;/sub&gt; and &amp;sigma;PNs during summer are consistent with
oxidation of NO&lt;sub&gt;2&lt;/sub&gt; and acetaldehyde by an OH x residence time of
1.1&amp;times;10&lt;sup&gt;10&lt;/sup&gt; molec OH cm&lt;sup&gt;&amp;minus;3&lt;/sup&gt; s, corresponding to 3 to
16&amp;times;10&lt;sup&gt;7&lt;/sup&gt; molecules cm&lt;sup&gt;&amp;minus;3&lt;/sup&gt; OH within the forest canopy for a 420 to
70 s
canopy residence time. We show that &amp;Sigma;AN&lt;sub&gt;(g+p)&lt;/sub&gt; fluxes are
consistent with this range in OH if the reaction of OH with &amp;Sigma;ANs
produces either HNO&lt;sub&gt;3&lt;/sub&gt; or NO&lt;sub&gt;2&lt;/sub&gt; with a 6–30% yield. Calculations of
NO fluxes constrained by the NO&lt;sub&gt;2&lt;/sub&gt; observations and the inferred OH
indicate that NO&lt;sub&gt;x&lt;/sub&gt; fluxes are downward into the canopy because of the
substantial conversion of NO&lt;sub&gt;x&lt;/sub&gt; to HNO&lt;sub&gt;3&lt;/sub&gt; and &amp;sigma;PNs in the
canopy. Even so, we derive that NO&lt;sub&gt;x&lt;/sub&gt; emission fluxes of
~15 ng(N) m&lt;sup&gt;&amp;minus;2&lt;/sup&gt; s&lt;sup&gt;&amp;minus;1&lt;/sup&gt; at midday during summer are required to balance the
NO&lt;sub&gt;x&lt;/sub&gt; and NO&lt;sub&gt;y&lt;/sub&gt; flux budgets. These fluxes are partly explained by
estimates of soil emissions (estimated to be between 3 and
6 ng(N) m&lt;sup&gt;&amp;minus;2&lt;/sup&gt; s&lt;sup&gt;-1&lt;/sup&gt;). One possibility for the remainder of the NO&lt;sub&gt;x&lt;/sub&gt; source is large
HONO emissions. Alternatively, the 15 ng(N) m&lt;sup&gt;&amp;minus;2&lt;/sup&gt; s&lt;sup&gt;&amp;minus;1&lt;/sup&gt; emission
estimate may be too large, and the budget balanced if the deposition of
HNO&lt;sub&gt;3&lt;/sub&gt; and &amp;sigma;PNs is slower than we estimate, if there are large
errors in either our understanding of peroxy radical chemistry, or our
assumptions that the budget is required to balance because the fluxes do not
obey similarity theory.</abstract>
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