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<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-11-3529-2011</article-id>
<title-group>
<article-title>Field determination of biomass burning emission ratios and factors via open-path FTIR spectroscopy  and fire radiative power assessment: headfire, backfire and residual smouldering combustion in  African savannahs</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Wooster</surname>
<given-names>M. J.</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 contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Freeborn</surname>
<given-names>P. H.</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>Archibald</surname>
<given-names>S.</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>Oppenheimer</surname>
<given-names>C.</given-names>
</name>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
<xref ref-type="aff" rid="aff5">
<sup>5</sup>
</xref>
<xref ref-type="aff" rid="aff6">
<sup>6</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Roberts</surname>
<given-names>G. J.</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 contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Smith</surname>
<given-names>T. E. L.</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>Govender</surname>
<given-names>N.</given-names>
</name>
<xref ref-type="aff" rid="aff7">
<sup>7</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Burton</surname>
<given-names>M.</given-names>
</name>
<xref ref-type="aff" rid="aff8">
<sup>8</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Palumbo</surname>
<given-names>I.</given-names>
</name>
<xref ref-type="aff" rid="aff9">
<sup>9</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>King&apos;s College London, Environmental Monitoring and Modelling Research Group, Department of  Geography, Strand, London, WC2R 2LS, UK</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>NERC National Centre for Earth Observation, UK</addr-line>
</aff>
<aff id="aff3">
<label>3</label>
<addr-line>Natural Resources and the Environment, CSIR, P.O. Box 395, Pretoria 0001, South Africa</addr-line>
</aff>
<aff id="aff4">
<label>4</label>
<addr-line>Le Studium, Institute for Advanced Studies, Orléans and Tours, France</addr-line>
</aff>
<aff id="aff5">
<label>5</label>
<addr-line>Institut des Sciences de la Terre d&apos;Orléans, 1a rue de la Férollerie, Orléans 45071,  France</addr-line>
</aff>
<aff id="aff6">
<label>6</label>
<addr-line>Department of Geography, University of Cambridge, Cambridge CB2 3EN, UK</addr-line>
</aff>
<aff id="aff7">
<label>7</label>
<addr-line>Scientific Services, Kruger National Park, Private Bag X402, Skukuza, 1350, South Africa</addr-line>
</aff>
<aff id="aff8">
<label>8</label>
<addr-line>Istituto Nazionale di Geofisica e Vulcanologia, Via della Faggiola, 32-56126 Pisa, Italy</addr-line>
</aff>
<aff id="aff9">
<label>9</label>
<addr-line>DG Joint Research Centre, Global Environment Monitoring Unit, Ispra, Italy</addr-line>
</aff>
<pub-date pub-type="epub">
<day>01</day>
<month>02</month>
<year>2011</year>
</pub-date>
<volume>11</volume>
<issue>2</issue>
<fpage>3529</fpage>
<lpage>3578</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/11/3529/2011/acpd-11-3529-2011.html">This article is available from http://www.atmos-chem-phys-discuss.net/11/3529/2011/acpd-11-3529-2011.html</self-uri>
<self-uri xlink:href="http://www.atmos-chem-phys-discuss.net/11/3529/2011/acpd-11-3529-2011.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys-discuss.net/11/3529/2011/acpd-11-3529-2011.pdf</self-uri>
<abstract>
<p>Biomass burning emissions factors are vital to quantifying trace gases releases from
      vegetation fires. Here we evaluate emissions factors for a series of savannah fires in
      Kruger National Park (KNP), South Africa using ground-based open path Fourier transform
      infrared (FTIR) spectroscopy and an infrared lamp separated by 150–250 m
      distance. Molecular abundances along the extended open path are retrieved using a spectral
      forward model coupled to a non-linear least squares fitting approach. We demonstrate
      derivation of trace gas column amounts for horizontal paths transecting the width of the
      advected plume, and find, for example, that CO mixing ratio changes of ~0.001 μmol mol&lt;sup&gt;&amp;minus;1&lt;/sup&gt; (~10 ppbv) can be detected across the relatively
      long optical paths used here. We focus analysis on five key compounds whose production is
      preferential during the pyrolysis (CH&lt;sub&gt;2&lt;/sub&gt;O), flaming (CO&lt;sub&gt;2&lt;/sub&gt;) and smoldering (CO,
      CH&lt;sub&gt;4&lt;/sub&gt;, NH&lt;sub&gt;3&lt;/sub&gt;) fire phases. We demonstrate that well constrained emissions ratios
      for these gases to both CO&lt;sub&gt;2&lt;/sub&gt; and CO can be derived for the backfire, headfire and
      residual smouldering combustion stages of these savannah fires, from which stage-specific
      emission factors can then be calculated. Headfires and backfires in general show similar
      emission ratios and emission factors, but those of the residual smouldering combustion
      stage can
      differ substantially (e.g., ER&lt;sub&gt;CH&lt;sub&gt;4&lt;/sub&gt;/CO&lt;sub&gt;2&lt;/sub&gt;&lt;/sub&gt; up to ~7 times higher than
      for the flaming stages). The timing of each fire stage was identified via airborne optical
      and thermal IR imagery and ground-observer reports, with the airborne IR imagery also used
      to derive estimates of fire radiative energy, thus allowing the relative amount of fuel
      burned in each stage to be calculated and the &quot;fire averaged&quot; emission ratios and
      emission factors to be determined. The derived &quot;fire averaged&quot; emission ratios are
      dominated by the headfire contribution, since the vast majority of the fuel is burned in
      this stage. Our fire averaged emission ratios and factors for CO&lt;sub&gt;2&lt;/sub&gt; and CH&lt;sub&gt;4&lt;/sub&gt;
      agree with those from published studies conducted in the same area using airborne plume
      sampling, and we concur with past suggestions that emission factors for formaldehyde in this
      environment appear substantially underestimated in widely used databases. We also find the
      emission ratios and factors for CO and NH&lt;sub&gt;3&lt;/sub&gt; to be somewhat higher than most other
      estimates, however, we see no evidence to support suggestions of a major overestimation in
      the emission factor of ammonia. Our data also suggest that the contribution of burning
      animal (elephant) dung can be a significant factor in the emissions characteristics of
      certain KNP fires, and indicate some similarities between the time series of fire brightness
      temperature and modified combustion efficiency (MCE) that supports suggestions that
      EO-derived fire temperature estimates maybe useful when attempting to remotely classify fire
      activity into its different phases. We conclude that ground-based, extended open path FTIR
      spectroscopy is a practical and very effective means for determining emission ratios,
      emission factors and modified combustion efficiencies at open vegetation fire plumes,
      allowing these to be probed at temporal and spatial scales difficult to explore using other
      ground-based approaches. Though we limited our study to five key emissions products, open
      path FTIR spectroscopy can detect dozens of other species, as has been demonstrated during
      previous closed-path FTIR airborne deployments in the same study area.</p>
</abstract>
<counts><page-count count="50"/></counts>
</article-meta>
</front>
<body/>
<back>
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