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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">ACPD</journal-id>
<journal-title-group>
<journal-title>Atmospheric Chemistry and Physics Discussions</journal-title>
<abbrev-journal-title abbrev-type="publisher">ACPD</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">1680-7375</issn>
<publisher><publisher-name>Copernicus GmbH</publisher-name>
<publisher-loc>Göttingen, Germany</publisher-loc>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.5194/acpd-5-8421-2005</article-id>
<title-group>
<article-title>Hydrocarbon-like and oxygenated organic aerosols in Pittsburgh: insights into sources and processes of organic aerosols</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Zhang</surname>
<given-names>Q.</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>Worsnop</surname>
<given-names>D. R.</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Canagaratna</surname>
<given-names>M. R.</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Jimenez</surname>
<given-names>J.-L.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>Cooperative Institute for Research in Environmental Sciences (CIRES), 216 UCB, University of Colorado-Boulder, Boulder, Colorado 80309-0216, USA</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>Department of Chemistry and Biochemistry, 216 UCB, University of Colorado-Boulder, Boulder, Colorado 80309-0216, USA</addr-line>
</aff>
<aff id="aff3">
<label>3</label>
<addr-line>Aerodyne Research Inc., Billerica, Massachusetts 01821-3976, USA</addr-line>
</aff>
<pub-date pub-type="epub">
<day>09</day>
<month>09</month>
<year>2005</year>
</pub-date>
<volume>5</volume>
<issue>5</issue>
<fpage>8421</fpage>
<lpage>8471</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-discuss.net/5/8421/2005/acpd-5-8421-2005.html">This article is available from http://www.atmos-chem-phys-discuss.net/5/8421/2005/acpd-5-8421-2005.html</self-uri>
<self-uri xlink:href="http://www.atmos-chem-phys-discuss.net/5/8421/2005/acpd-5-8421-2005.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys-discuss.net/5/8421/2005/acpd-5-8421-2005.pdf</self-uri>
<abstract>
<p>A recently developed algorithm (Zhang et al., 2005) has been applied to deconvolve the mass spectra of
organic aerosols acquired with the Aerosol Mass Spectrometer (AMS) in
Pittsburgh during September 2002. The results are used here to characterize
the mass concentrations, size distributions, and mass spectra of
hydrocarbon-like and oxygenated organic aerosol (HOA and OOA, respectively).
HOA accounts for 34% of the measured organic aerosol mass and OOA
accounts for 66%. The mass concentrations of HOA demonstrate a prominent
diurnal profile that peaks in the morning during the rush hour and decreases
with the rise of the boundary layer. The diurnal profile of OOA is
relatively flat and resembles those of SO&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;2&amp;minus;&lt;/sup&gt; and NH&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt;.
The size distribution of HOA shows a distinct ultrafine mode that is
commonly associated with fresh emissions while OOA is generally concentrated
in the accumulation mode and appears to be mostly internally mixed with the
inorganic ions, such as SO&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;2&amp;minus;&lt;/sup&gt; and NH&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt;. These
observations suggest that HOA is likely primary aerosol from local,
combustion-related emissions and that OOA is secondary organic aerosol (SOA)
influenced by regional contributions. There is strong evidence of the direct
correspondence of OOA to SOA during an intense new particle formation and
growth event, when condensational growth of OOA was observed. The mass spectrum
of OOA of this new particle formation event is very similar to the OOA spectrum
of the entire study, which strongly suggests that most OOA during this study is SOA. O&lt;sub&gt;3&lt;/sub&gt;
appears to be a poor indicator for SOA concentration while SO&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;2&amp;minus;&lt;/sup&gt;
is a relatively good surrogate for this dataset. Since the diurnal averages
of HOA tightly track those of CO during day time, oxidation/aging of HOA
appears to be very small on the time scale of several hours. Based on
extracted mass spectra and the likely elemental compositions of major
&lt;i&gt;m/z&lt;/i&gt;&apos;s, the organic mass to organic carbon ratios (OM:OC) of HOA and OOA are
estimated at 1.2 and 2.2 &amp;mu;g/&amp;mu;g C, respectively, leading to an
average OM:OC ratio of 1.8 for submicron OA in Pittsburgh during September.
The C:O ratio of OOA is estimated at 1:0.8. The carbon contents in HOA and
OOA calculated accordingly correlate well to primary and secondary organic
carbon, respectively, estimated by the OC/EC tracer technique (assuming
POC-to-EC ratio=1). In addition, the total carbon concentrations
calculated from the AMS data agree well with those measured by the Sunset
Laboratory Carbon analyzer (&lt;i&gt;r&lt;/i&gt;&lt;sup&gt;2&lt;/sup&gt;=0.87; slope=1.01&amp;plusmn;0.11).</p>
</abstract>
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