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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>6</issue_number>
		<publication_year>2009</publication_year>
	</journal>
	<doi>10.5194/acpd-9-24531-2009</doi>
	<article_url>http://www.atmos-chem-phys-discuss.net/9/24531/2009/</article_url>
	<abstract_html>http://www.atmos-chem-phys-discuss.net/9/24531/2009/acpd-9-24531-2009.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys-discuss.net/9/24531/2009/acpd-9-24531-2009.pdf</fulltext_pdf>
	<start_page>24531</start_page>
	<end_page>24585</end_page>
	<publication_date>2009-11-18</publication_date>
	<article_title content_type="html">NO&lt;sub&gt;3&lt;/sub&gt; radical measurements in a polluted marine environment: links to ozone formation</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>R. McLaren</name>
			<email>rmclaren@yorku.ca</email>
		</author>
		<author numeration="2" affiliations="1">
			<name>P. Wojtal</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>D. Majonis</name>
		</author>
		<author numeration="4" affiliations="1">
			<name>J. McCourt</name>
		</author>
		<author numeration="5" affiliations="1">
			<name>J. D. Halla</name>
		</author>
		<author numeration="6" affiliations="2">
			<name>J. Brook</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Centre for Atmospheric Chemistry, York University, North York, ON, Canada</affiliation>
		<affiliation numeration="2" content_type="html">Air Quality Research Division, Environment Canada, Toronto, ON, Canada</affiliation>
	</affiliations>
	<abstract content_type="html">Nighttime chemistry in polluted regions is dominated by the nitrate radical
(NO&lt;sub&gt;3&lt;/sub&gt;) including its direct reaction with natural and anthropogenic
hydrocarbons, its reaction with NO&lt;sub&gt;2&lt;/sub&gt; to form N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt;, and
subsequent reactions of N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt; to form HNO&lt;sub&gt;3&lt;/sub&gt; and chlorine
containing photolabile species. We report nighttime measurements of
NO&lt;sub&gt;3&lt;/sub&gt;, NO&lt;sub&gt;2&lt;/sub&gt;, and O&lt;sub&gt;3&lt;/sub&gt;, in the polluted marine boundary layer
southwest of Vancouver, BC during a three week study in summer of 2005. The
concentration of N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt; was calculated using the well known
equilibrium, NO&lt;sub&gt;3&lt;/sub&gt;+NO&lt;sub&gt;2&lt;/sub&gt;&amp;harr;N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt;. Median
overnight mixing ratios of NO&lt;sub&gt;3&lt;/sub&gt;, N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt; and NO&lt;sub&gt;2&lt;/sub&gt; were 10.3 ppt,
122 ppt and 8.3 ppb with median N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt;/NO&lt;sub&gt;3&lt;/sub&gt; molar ratios of
13.1 and median nocturnal partitioning of 4.9%. Due to the high levels of
NO&lt;sub&gt;2&lt;/sub&gt; that can inhibit approach to steady-state, we use a method for
calculating NO&lt;sub&gt;3&lt;/sub&gt; lifetimes that does not assume the steady-state
approximation. Median and average lifetimes of NO&lt;sub&gt;3&lt;/sub&gt; in the
NO&lt;sub&gt;3&lt;/sub&gt;-N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt; nighttime reservoir were 1.1–2.3 min. We have
determined nocturnal profiles of the pseudo first order loss coefficient of
NO&lt;sub&gt;3&lt;/sub&gt; and the first order loss coefficients of N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt; by
regression of the NO&lt;sub&gt;3&lt;/sub&gt; inverse lifetimes with the
[N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt;]/[NO&lt;sub&gt;3&lt;/sub&gt;] ratio. Direct losses of NO&lt;sub&gt;3&lt;/sub&gt; are highest
early in the night, tapering off as the night proceeds. The magnitude of the
first order loss coefficient of N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt; is consistent with
recommended homogeneous rate coefficients for reaction of N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt;
with water vapor early in the night, but increases significantly in the
latter part of the night when relative humidity increases beyond 75%,
consistent with heterogeneous reactions of N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt; with sea salt
and/or other aerosols with rate constant k&lt;sub&gt;het&lt;/sub&gt;=1.2&amp;times;10&lt;sup&gt;&amp;minus;3&lt;/sup&gt; s&lt;sup&gt;&amp;minus;1&lt;/sup&gt;.
Analysis indicates that a correlation exists between overnight
integrated N&lt;sub&gt;2&lt;/sub&gt;O&lt;sub&gt;5&lt;/sub&gt; concentrations in the marine boundary layer, a
surrogate for the accumulation of chlorine containing photolabile species,
and maximum 1-h average O&lt;sub&gt;3&lt;/sub&gt; at stations in the Lower Fraser Valley the
next day when there is clear evidence of a sea breeze transporting marine
air into the valley. The range of maximum 1-h average O&lt;sub&gt;3&lt;/sub&gt; increase
attributable to the correlation is &amp;Delta;O&lt;sub&gt;3&lt;/sub&gt;=+1.1 to +8.3 ppb
throughout the study for the average of 20 stations, although higher
increases are seen for stations far downwind of the coastal urban area. The
correlation is still statistically significant on the second day after a
nighttime accumulation, but with a different spatial pattern favouring
increased O&lt;sub&gt;3&lt;/sub&gt; at the coastal urban stations, consistent with transport
of polluted air back to the coast.</abstract>
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