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<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" article-type="research-article" dtd-version="3.0" xml:lang="en">
<front>
<journal-meta>
<journal-id journal-id-type="publisher">ACP</journal-id>
<journal-title-group>
<journal-title>Atmospheric Chemistry and Physics</journal-title>
<abbrev-journal-title abbrev-type="publisher">ACP</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">1680-7324</issn>
<publisher><publisher-name>Copernicus GmbH</publisher-name>
<publisher-loc>GÃ¶ttingen, Germany</publisher-loc>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.5194/acp-10-4187-2010</article-id>
<title-group>
<article-title>NO&lt;sub&gt;3&lt;/sub&gt; radical measurements in a polluted marine environment: links to ozone formation</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>McLaren</surname>
<given-names>R.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Wojtal</surname>
<given-names>P.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Majonis</surname>
<given-names>D.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>McCourt</surname>
<given-names>J.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Halla</surname>
<given-names>J. D.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Brook</surname>
<given-names>J.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>Centre for Atmospheric Chemistry, York University, North York, ON, Canada</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>Air Quality Research Division, Environment Canada, Toronto, ON, Canada</addr-line>
</aff>
<pub-date pub-type="epub">
<day>05</day>
<month>05</month>
<year>2010</year>
</pub-date>
<volume>10</volume>
<issue>9</issue>
<fpage>4187</fpage>
<lpage>4206</lpage>
<permissions>
<license xlink:type="simple">
<license-p>This is an open-access article ditributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.</license-p>
</license>
</permissions>
<self-uri xlink:href="http://www.atmos-chem-phys.net/10/4187/2010/acp-10-4187-2010.html">This article is available from http://www.atmos-chem-phys.net/10/4187/2010/acp-10-4187-2010.html</self-uri>
<self-uri xlink:href="http://www.atmos-chem-phys.net/10/4187/2010/acp-10-4187-2010.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys.net/10/4187/2010/acp-10-4187-2010.pdf</self-uri>
<abstract>
<p>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 the 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 1.1â€“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, but not verification of, 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 aerosols with a rate constant
&lt;i&gt;k&lt;/i&gt;&lt;sub&gt;het&lt;/sub&gt;=(1.2&amp;plusmn;0.4)&amp;times;10&lt;sup&gt;&amp;minus;3&lt;/sup&gt; s&lt;sup&gt;&amp;minus;1&lt;/sup&gt;&amp;minus;(1.6&amp;plusmn;0.4)&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.</p>
</abstract>
<counts><page-count count="20"/></counts>
</article-meta>
</front>
<body/>
<back>
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