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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>5</issue_number>
		<publication_year>2009</publication_year>
	</journal>
	<doi>10.5194/bg-6-819-2009</doi>
	<article_url>http://www.biogeosciences.net/6/819/2009/</article_url>
	<abstract_html>http://www.biogeosciences.net/6/819/2009/bg-6-819-2009.html</abstract_html>
	<fulltext_pdf>http://www.biogeosciences.net/6/819/2009/bg-6-819-2009.pdf</fulltext_pdf>
	<start_page>819</start_page>
	<end_page>834</end_page>
	<publication_date>2009-05-15</publication_date>
	<article_title content_type="html">Ammonia fluxes in relation to cutting and fertilization of an intensively managed grassland derived from an inter-comparison of gradient measurements</article_title>
	<authors>
		<author numeration="1" affiliations="1,7">
			<name>C. Milford</name>
			<email>cmilford@inm.es</email>
		</author>
		<author numeration="2" affiliations="1">
			<name>M. R. Theobald</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>E. Nemitz</name>
		</author>
		<author numeration="4" affiliations="1">
			<name>K. J. Hargreaves</name>
		</author>
		<author numeration="5" affiliations="2">
			<name>L. Horvath</name>
		</author>
		<author numeration="6" affiliations="2">
			<name>J. Raso</name>
		</author>
		<author numeration="7" affiliations="3">
			<name>U. Dämmgen</name>
		</author>
		<author numeration="8" affiliations="4">
			<name>A. Neftel</name>
		</author>
		<author numeration="9" affiliations="1,4">
			<name>S. K. Jones</name>
		</author>
		<author numeration="10" affiliations="5">
			<name>A. Hensen</name>
		</author>
		<author numeration="11" affiliations="6">
			<name>B. Loubet</name>
		</author>
		<author numeration="12" affiliations="6">
			<name>P. Cellier</name>
		</author>
		<author numeration="13" affiliations="1">
			<name>M. A. Sutton</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Centre for Ecology and Hydrology (Edinburgh Research Station), Bush Estate, Penicuik, Midlothian, EH26 0QB, UK</affiliation>
		<affiliation numeration="2" content_type="html">Institute of Atmospheric Physics, P.O. Box 39, 1675 Budapest, Hungary</affiliation>
		<affiliation numeration="3" content_type="html">Institut für Agrarökologie, Bundesforschungsanstalt für Landwirtschaft (FAL), Bundesallee 50, 38116 Braunschweig, Germany</affiliation>
		<affiliation numeration="4" content_type="html">Agroscope Reckenholz-Tänikon Research Station ART, Reckenholzstrasse 191, 8046 Zurich, Switzerland</affiliation>
		<affiliation numeration="5" content_type="html">Energy research Centre of the Netherlands (ECN), Postbus 1, 1755 ZG Petten, The Netherlands</affiliation>
		<affiliation numeration="6" content_type="html">Institut National de la Recherche Agronomique (INRA), UMR Environnement et Grandes Cultures,  Thiverval-Grignon, 78850, France</affiliation>
		<affiliation numeration="7" content_type="html">now at: Institute of Earth Sciences &quot;Jaume Almera&quot;, CSIC, C/Lluis Solé i Sabarís s/n, Barcelona, 08028, Spain</affiliation>
	</affiliations>
	<abstract content_type="html">Quantification of ammonia (NH&lt;sub&gt;3&lt;/sub&gt;) land-atmosphere exchange is required
for atmospheric modelling and assessment of nitrogen deposition, yet flux
measurement methods remain highly uncertain. To address this issue, a major
inter-comparison of ammonia fluxes over intensively managed grassland was
conducted during the GRAMINAE Integrated Experiment held in Braunschweig,
Germany. In order to provide a robust dataset of ammonia exchange with the
vegetation, four independent continuous flux gradient systems were operated.
Three independently operated continuous wet denuders systems (AMANDA) were
compared with a Wet Effluent Diffusion Denuder (mini-WEDD) system.
Measurements were made at two distances from an adjacent livestock farm,
allowing effects of advection to be quantified in a real landscape setting.
Data treatment included filtering for instrument failure, disturbed wind
sectors and unsuitable micrometeorological conditions, with corrections made
for storage and advection errors.
&lt;br&gt;&lt;br&gt;
The inter-comparison demonstrated good agreement in measured ammonia
concentrations and fluxes (relative standard error &lt;20%) for some
periods, although the performance of the ammonia analyzers were variable,
with much poorer agreement on particular days. However, by using four
systems, the inter-comparison was able to provide a robust mean estimate of
continuous ammonia fluxes through the experiment. The observed fluxes were:
a) small bi-directional fluxes prior to cutting (&amp;minus;64 to 42 ng NH&lt;sub&gt;3&lt;/sub&gt; m&lt;sup&gt;&amp;minus;2&lt;/sup&gt; s&lt;sup&gt;&amp;minus;1&lt;/sup&gt;),
b) larger diurnally-varying emissions following cutting
(&amp;minus;49 to 703 ng NH&lt;sub&gt;3&lt;/sub&gt; m&lt;sup&gt;&amp;minus;2&lt;/sup&gt; s&lt;sup&gt;&amp;minus;1&lt;/sup&gt;) and c) much larger emissions
following fertilizer application (0 to 3820 ng NH&lt;sub&gt;3&lt;/sub&gt; m&lt;sup&gt;&amp;minus;2&lt;/sup&gt; s&lt;sup&gt;&amp;minus;1&lt;/sup&gt;).
The results are a salutary reminder of the uncertainty in unreplicated
ammonia flux measurements, while the replication of the present study
provides a uniquely robust dataset for the evaluation of ammonia exchange
processes. It is clear that consistently reliable determination of ammonia
concentrations remains the major measurement challenge.</abstract>
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</article>

