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<article language="en">
	<journal>
		<journal_title>Biogeosciences</journal_title>
		<journal_url>www.biogeosciences.net</journal_url>
		<issn>1726-4170</issn>
		<eissn>1726-4189</eissn>
		<volume_number>6</volume_number>
		<issue_number>8</issue_number>
		<publication_year>2009</publication_year>
	</journal>
	<doi>10.5194/bg-6-1627-2009</doi>
	<article_url>http://www.biogeosciences.net/6/1627/2009/</article_url>
	<abstract_html>http://www.biogeosciences.net/6/1627/2009/bg-6-1627-2009.html</abstract_html>
	<fulltext_pdf>http://www.biogeosciences.net/6/1627/2009/bg-6-1627-2009.pdf</fulltext_pdf>
	<start_page>1627</start_page>
	<end_page>1645</end_page>
	<publication_date>2009-08-12</publication_date>
	<article_title content_type="html">Aerosol fluxes and particle growth above managed grassland</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>E. Nemitz</name>
			<email>en@ceh.ac.uk</email>
		</author>
		<author numeration="2" affiliations="2">
			<name>J. R. Dorsey</name>
		</author>
		<author numeration="3" affiliations="2">
			<name>M. J. Flynn</name>
		</author>
		<author numeration="4" affiliations="2">
			<name>M. W. Gallagher</name>
		</author>
		<author numeration="5" affiliations="3">
			<name>A. Hensen</name>
		</author>
		<author numeration="6" affiliations="3">
			<name>J.-W. Erisman</name>
		</author>
		<author numeration="7" affiliations="1,4">
			<name>S. M. Owen</name>
		</author>
		<author numeration="8" affiliations="5">
			<name>U. Dämmgen</name>
		</author>
		<author numeration="9" affiliations="1">
			<name>M. A. Sutton</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Centre for Ecology and Hydrology (Edinburgh), Bush Estate, Penicuik, Midlothian, EH26 0QB, UK</affiliation>
		<affiliation numeration="2" content_type="html">School for Earth, Atmospheric and Environmental Sciences, Univ. of Manchester, PO Box 88, Manchester, M60 1QD, UK</affiliation>
		<affiliation numeration="3" content_type="html">Energy Research Centre for the Netherlands (ECN), 1755-ZG Petten, The Netherlands</affiliation>
		<affiliation numeration="4" content_type="html">Institute for Environmental and Natural Sciences, University of Lancaster, UK</affiliation>
		<affiliation numeration="5" content_type="html">Institute for Agroecology, Federal Agricultural Research Centre, Braunschweig, Germany</affiliation>
	</affiliations>
	<abstract content_type="html">Particle deposition velocities (11–3000 nm diameter)
measured above grassland by eddy covariance during the EU GRAMINAE
experiment in June 2000 averaged 0.24 and 0.03 mm s&lt;sup&gt;&amp;minus;1&lt;/sup&gt; to long (0.75 m)
and short (0.07 m) grass, respectively. After fertilisation with 108 kg N ha&lt;sup&gt;&amp;minus;1&lt;/sup&gt;
as calcium ammonium nitrate, sustained apparent upward fluxes of
particles were observed. Analysis of concentrations and fluxes of potential
precursor gases, including NH&lt;sub&gt;3&lt;/sub&gt;, HNO&lt;sub&gt;3&lt;/sub&gt;, HCl and selected VOCs, shows
that condensation of HNO&lt;sub&gt;3&lt;/sub&gt; and NH&lt;sub&gt;3&lt;/sub&gt; on the surface of existing
particles is responsible for this effect. A novel approach is developed to
derive particle growth rates at the field scale, from a combination of
measurements of vertical fluxes and particle size-distributions. For the
first 9 days after fertilization, growth rates of 11 nm particles of
7.04 nm hr&lt;sup&gt;&amp;minus;1&lt;/sup&gt; and 1.68 nm hr&lt;sup&gt;&amp;minus;1&lt;/sup&gt; were derived for day and night-time
conditions, respectively. This implies total NH&lt;sub&gt;4&lt;/sub&gt;NO&lt;sub&gt;3&lt;/sub&gt; production
rates of 1.11 and 0.44 μg m&lt;sup&gt;&amp;minus;3&lt;/sup&gt; h&lt;sup&gt;&amp;minus;1&lt;/sup&gt;, respectively. The
effect translates into a small error in measured ammonia fluxes (0.06%
day, 0.56% night) and a large error in NH&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt; and NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;minus;&lt;/sup&gt;
aerosol fluxes of 3.6% and 10%, respectively. By converting rapidly
exchanged NH&lt;sub&gt;3&lt;/sub&gt; and HNO&lt;sub&gt;3&lt;/sub&gt; into slowly depositing NH&lt;sub&gt;4&lt;/sub&gt;NO&lt;sub&gt;3&lt;/sub&gt;,
the reaction modifies the total N budget, though this effect is small
(&amp;lt;1% for the 10 days following fertilization), as NH&lt;sub&gt;3&lt;/sub&gt; emission
dominates the net flux. It is estimated that 3.8% of the fertilizer N was
volatilised as NH&lt;sub&gt;3&lt;/sub&gt;, of which 0.05% re-condensed to form
NH&lt;sub&gt;4&lt;/sub&gt;NO&lt;sub&gt;3&lt;/sub&gt; particles within the lowest 2 m of the surface layer. This
surface induced process would at least scale up to a global NH&lt;sub&gt;4&lt;/sub&gt;NO&lt;sub&gt;3&lt;/sub&gt;
formation of ca. 0.21 kt N yr&lt;sup&gt;&amp;minus;1&lt;/sup&gt; from NH&lt;sub&gt;4&lt;/sub&gt;NO&lt;sub&gt;3&lt;/sub&gt; fertilisers and
potentially 45 kt N yr&lt;sup&gt;&amp;minus;1&lt;/sup&gt; from NH&lt;sub&gt;3&lt;/sub&gt; emissions in general.</abstract>
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</article>

