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<article language="en">
	<journal>
		<journal_title>Atmospheric Chemistry and Physics</journal_title>
		<journal_url>www.atmos-chem-phys.net</journal_url>
		<issn>1680-7316</issn>
		<eissn>1680-7324</eissn>
		<volume_number>6</volume_number>
		<issue_number>2</issue_number>
		<publication_year>2006</publication_year>
	</journal>
	<doi>10.5194/acp-6-447-2006</doi>
	<article_url>http://www.atmos-chem-phys.net/6/447/2006/</article_url>
	<abstract_html>http://www.atmos-chem-phys.net/6/447/2006/acp-6-447-2006.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys.net/6/447/2006/acp-6-447-2006.pdf</fulltext_pdf>
	<start_page>447</start_page>
	<end_page>469</end_page>
	<publication_date>2006-02-08</publication_date>
	<article_title content_type="html">Dry and wet deposition of inorganic nitrogen compounds to a tropical pasture site (Rondônia, Brazil)</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>I. Trebs</name>
		</author>
		<author numeration="2" affiliations="2">
			<name>L. L. Lara</name>
		</author>
		<author numeration="3" affiliations="3">
			<name>L. M. M. Zeri</name>
		</author>
		<author numeration="4" affiliations="4">
			<name>L. V. Gatti</name>
		</author>
		<author numeration="5" affiliations="5">
			<name>P. Artaxo</name>
		</author>
		<author numeration="6" affiliations="6">
			<name>R. Dlugi</name>
		</author>
		<author numeration="7" affiliations="7">
			<name>J. Slanina</name>
		</author>
		<author numeration="8" affiliations="1">
			<name>M. O. Andreae</name>
		</author>
		<author numeration="9" affiliations="1">
			<name>F. X. Meixner</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Max Planck Institute for Chemistry, Biogeochemistry Department, P.O. Box 3060, 55020, Mainz, Germany</affiliation>
		<affiliation numeration="2" content_type="html">Centro de Energia Nuclear na Agricultura (CENA), Laboratorio de Ecologia Isotópica, Universidade de São Paulo (USP), Av. Centenario, 303 13400-970, Piracicaba, São Paulo, SP, Brazil</affiliation>
		<affiliation numeration="3" content_type="html">Max Planck Institute for Biogeochemistry, Department Biogeochemical Processes, Hans-Knöll-Straße 10, 07745 Jena, Germany</affiliation>
		<affiliation numeration="4" content_type="html">Instituto de Pesquisas Energéticas e Nucleares, CQMA, Atmospheric Chemistry Laboratory, Av. Prof. Lineu Prestes, 2242, Cidade Universitaria, CEP 055508-900, São Paulo, SP, Brazil</affiliation>
		<affiliation numeration="5" content_type="html">Instituto de Física, Universidade de São Paulo (USP), Rua do Matão, Travessa R, 187, CEP 05508-900, São Paulo, SP, Brazil</affiliation>
		<affiliation numeration="6" content_type="html">Working Group Atmospheric Processes (WAP), Gernotstrasse 11, 80804 Munich, Germany</affiliation>
		<affiliation numeration="7" content_type="html">Peking University, College of Environmental Sciences, Beijing 100871, China</affiliation>
	</affiliations>
	<abstract content_type="html">The input of nitrogen (N) to ecosystems has increased dramatically over the
past decades. While total (wet&amp;nbsp;+&amp;nbsp;dry) N deposition has been extensively
determined in temperate regions, only very few data sets of N wet deposition
exist for tropical ecosystems, and moreover, reliable experimental
information about N dry deposition in tropical environments is lacking. In
this study we estimate dry and wet deposition of inorganic N for a remote
pasture site in the Amazon Basin based on in-situ measurements. The
measurements covered the late dry (biomass burning) season, a transition
period and the onset of the wet season (clean conditions) (12 September to 14
November 2002) and were a part of the LBA-SMOCC (Large-Scale
Biosphere-Atmosphere Experiment in Amazonia &amp;ndash; Smoke, Aerosols, Clouds,
Rainfall, and Climate) 2002 campaign. Ammonia (NH&lt;sub&gt;3&lt;/sub&gt;), nitric acid
(HNO&lt;sub&gt;3&lt;/sub&gt;), nitrous acid (HONO), nitrogen dioxide (NO&lt;sub&gt;2&lt;/sub&gt;), nitric oxide
(NO), ozone (O&lt;sub&gt;3&lt;/sub&gt;), aerosol ammonium (NH&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt;) and aerosol nitrate
(NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;-&lt;/sup&gt;) were measured in real-time, accompanied by simultaneous
meteorological measurements. Dry deposition fluxes of NO&lt;sub&gt;2&lt;/sub&gt; and HNO&lt;sub&gt;3&lt;/sub&gt;
are inferred using the &apos;&apos;big leaf multiple resistance approach&apos;&apos; and
particle deposition fluxes are derived using an established empirical
parameterization. Bi-directional surface-atmosphere exchange fluxes of
NH&lt;sub&gt;3&lt;/sub&gt; and HONO are estimated by applying a &apos;&apos;canopy compensation point
model&apos;&apos;. N dry and wet deposition is dominated by NH&lt;sub&gt;3&lt;/sub&gt; and
NH&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt;, which is largely the consequence of biomass burning during
the dry season. The grass surface appeared to have a strong potential for
daytime NH&lt;sub&gt;3&lt;/sub&gt; emission, owing to high canopy compensation points, which
are related to high surface temperatures and to direct NH&lt;sub&gt;3&lt;/sub&gt; emissions
from cattle excreta. NO&lt;sub&gt;2&lt;/sub&gt; also significantly accounted for N dry
deposition, whereas HNO&lt;sub&gt;3&lt;/sub&gt;, HONO and N-containing aerosol species were
only minor contributors. Ignoring NH&lt;sub&gt;3&lt;/sub&gt; emission from the vegetation
surface, the annual net N deposition rate is estimated to be about &amp;minus;11 kgN
ha&lt;sup&gt;-1&lt;/sup&gt; yr&lt;sup&gt;-1&lt;/sup&gt;. If on the other hand, surface-atmosphere exchange of
NH&lt;sub&gt;3&lt;/sub&gt; is considered to be bi-directional, the annual net N budget at the
pasture site is estimated to range from &amp;minus;2.15 to &amp;minus;4.25 kgN ha&lt;sup&gt;-1&lt;/sup&gt; yr&lt;sup&gt;-1&lt;/sup&gt;.</abstract>
	<references>
	</references>
</article>

