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<!DOCTYPE article SYSTEM "http://www.atmos-chem-phys-discuss.net/inc/acpd/copernicus.dtd">
<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>5</volume_number>
		<issue_number>3</issue_number>
		<publication_year>2005</publication_year>
	</journal>
	<doi>10.5194/acpd-5-2791-2005</doi>
	<article_url>http://www.atmos-chem-phys-discuss.net/5/2791/2005/</article_url>
	<abstract_html>http://www.atmos-chem-phys-discuss.net/5/2791/2005/acpd-5-2791-2005.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys-discuss.net/5/2791/2005/acpd-5-2791-2005.pdf</fulltext_pdf>
	<start_page>2791</start_page>
	<end_page>2831</end_page>
	<publication_date>2005-05-09</publication_date>
	<article_title content_type="html">Airborne measurements of trace gas and aerosol particle emissions from biomass burning in Amazonia</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>P. Guyon</name>
		</author>
		<author numeration="2" affiliations="1">
			<name>G. Frank</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>M. Welling</name>
		</author>
		<author numeration="4" affiliations="1">
			<name>D. Chand</name>
		</author>
		<author numeration="5" affiliations="2">
			<name>P. Artaxo</name>
		</author>
		<author numeration="6" affiliations="2">
			<name>L. Rizzo</name>
		</author>
		<author numeration="7" affiliations="2">
			<name>G. Nishioka</name>
		</author>
		<author numeration="8" affiliations="3">
			<name>O. Kolle</name>
		</author>
		<author numeration="9" affiliations="3">
			<name>H. Fritsch</name>
		</author>
		<author numeration="10" affiliations="4">
			<name>M. A. F. Silva Dias</name>
		</author>
		<author numeration="11" affiliations="5">
			<name>L. V. Gatti</name>
		</author>
		<author numeration="12" affiliations="6">
			<name>M. Cordova</name>
		</author>
		<author numeration="13" affiliations="1">
			<name>M. O. Andreae</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Max Planck Institute for Chemistry, Department of Biogeochemistry, Mainz, Germany</affiliation>
		<affiliation numeration="2" content_type="html">Institute of Physics, University of S&amp;atilde;o Paulo, S&amp;atilde;o Paulo, Brazil</affiliation>
		<affiliation numeration="3" content_type="html">Max Planck Institute for Biogeochemistry, Jena, Germany</affiliation>
		<affiliation numeration="4" content_type="html">Atmospheric Sciences Department, IAG, University of S&amp;atilde;o Paulo, S&amp;atilde;o Paulo, Brazil</affiliation>
		<affiliation numeration="5" content_type="html">Divis&amp;atilde;o de Qu&amp;iacute;mica Ambiental, Laborat&amp;oacute;rio de Qu&amp;iacute;mica Atmosf&amp;eacute;rica, IPEN, S&amp;atilde;o Paulo, Brazil</affiliation>
		<affiliation numeration="6" content_type="html">Center for Advanced Studies in Arid Zones (CEAZA), La Serena, Chile</affiliation>
	</affiliations>
	<abstract content_type="html">As part of the LBA-SMOCC (Large-Scale Biosphere-Atmosphere Experiment in
Amazonia &amp;ndash; Smoke, Aerosols, Clouds, Rainfall, and Climate) 2002 campaign, we
studied the emission of carbon monoxide (CO), carbon dioxide (CO&lt;sub&gt;2&lt;/sub&gt;), and
aerosol particles from Amazonian deforestation fires using an instrumented
aircraft. Emission ratios for aerosol number (CN) relative to CO
(ER&lt;sub&gt;CN/CO&lt;/sub&gt;) fell in the range 14&amp;ndash;32 cm&lt;sup&gt;-3&lt;/sup&gt;&amp;nbsp;ppb&lt;sup&gt;-1&lt;/sup&gt; for most of the
time, in agreement with values usually found from tropical savanna fires.
The number of particles emitted per amount biomass burned was found to be
dependant on the fire condition (combustion efficiency). Variability in the
ER&lt;sub&gt;CN/CO&lt;/sub&gt; between fires was similar to the variability caused by
variations in combustion behavior within each individual fire. This was
confirmed by observations of CO-to-CO&lt;sub&gt;2&lt;/sub&gt; emission ratios (ER&lt;sub&gt;CO/CO2&lt;/sub&gt;),
which stretched across the same wide range of values for individual fires as
for all the fires observed during the sampling campaign, indicating that
flaming and smoldering phases are present simultaneously in deforestation
fires. Emission factors (EF) for CO and aerosol particles were computed and
a correction was applied for the residual smoldering combustion (RSC)
fraction of emissions that are not sampled by the aircraft. The correction,
previously unpublished for tropical deforestation fires, suggested an EF
about one and a half to twice as large for these species. Vertical transport
of biomass-burning plumes from the boundary layer (BL) to the cloud
detrainment layer (CDL) and the free troposphere (FT) was found to be a very
common phenomenon. We observed a 20% loss in particle number as a result
of this vertical transport and subsequent cloud processing, attributable to
in-cloud coagulation. This small loss fraction suggests that this mode of
transport is very efficient in terms of particle numbers and occurs mostly
via non-precipitating clouds. The detrained aerosol particles released in
the CDL and FT were larger due to coagulation and secondary growth, and
therefore more efficient at scattering radiation and nucleating cloud
droplets than the fresh particles. This process may have significant
atmospheric implications on a regional and larger scale.</abstract>
	<references>
	</references>
</article>

