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	<journal>
		<journal_title>Biogeosciences</journal_title>
		<journal_url>www.biogeosciences.net</journal_url>
		<issn>1726-4170</issn>
		<eissn>1726-4189</eissn>
		<volume_number>5</volume_number>
		<issue_number>1</issue_number>
		<publication_year>2008</publication_year>
	</journal>
	<doi>10.5194/bg-5-129-2008</doi>
	<article_url>http://www.biogeosciences.net/5/129/2008/</article_url>
	<abstract_html>http://www.biogeosciences.net/5/129/2008/bg-5-129-2008.html</abstract_html>
	<fulltext_pdf>http://www.biogeosciences.net/5/129/2008/bg-5-129-2008.pdf</fulltext_pdf>
	<start_page>129</start_page>
	<end_page>132</end_page>
	<publication_date>2008-02-01</publication_date>
	<article_title content_type="html">The fate of N&lt;sub&gt;2&lt;/sub&gt;O consumed in soils</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>B. Vieten</name>
			<email>b.vieten@unibas.ch</email>
		</author>
		<author numeration="2" affiliations="1">
			<name>F. Conen</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>B. Seth</name>
		</author>
		<author numeration="4" affiliations="1">
			<name>C. Alewell</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Institute of Environmental Geosciences, University of Basel, Bernoullistrasse 30, 4056 Basel, Switzerland</affiliation>
	</affiliations>
	<abstract content_type="html">Soils are capable to consume N&lt;sub&gt;2&lt;/sub&gt;O. It is generally assumed that
consumption occurs exclusively via respiratory reduction to N&lt;sub&gt;2&lt;/sub&gt; by
denitrifying organisms (i.e. complete denitrification). Yet, we are not
aware of any verification of this assumption. Some N&lt;sub&gt;2&lt;/sub&gt;O may be
assimilatorily reduced to NH&lt;sub&gt;3&lt;/sub&gt;. Reduction of N&lt;sub&gt;2&lt;/sub&gt;O to NH&lt;sub&gt;3&lt;/sub&gt; is
thermodynamically advantageous compared to the reduction of N&lt;sub&gt;2&lt;/sub&gt;. Is this
an ecologically relevant process? To find out, we treated four contrasting
soil samples in a flow-through incubation experiment with a mixture of
labelled (98%) &lt;sup&gt;15&lt;/sup&gt;N&lt;sub&gt;2&lt;/sub&gt;O (0.5&amp;ndash;4 ppm) and O&lt;sub&gt;2&lt;/sub&gt; (0.2&amp;ndash;0.4%) in
He. We measured N&lt;sub&gt;2&lt;/sub&gt;O consumption by GC-ECD continuously and &amp;delta;&lt;sup&gt;15&lt;/sup&gt;N 
of soil organic matter before and after an 11 to 29 day incubation
period. Any &lt;sup&gt;15&lt;/sup&gt;N&lt;sub&gt;2&lt;/sub&gt;O assimilatorily reduced would have resulted in
the enrichment of soil organic matter with &lt;sup&gt;15&lt;/sup&gt;N, whereas dissimilatorily
reduced &lt;sup&gt;15&lt;/sup&gt;N&lt;sub&gt;2&lt;/sub&gt;O would not have left a trace. None of the soils
showed a change in &amp;delta;&lt;sup&gt;15&lt;/sup&gt;N that was statistically different from
zero. A maximum of 0.27% (s.e. &amp;plusmn;0.19%) of consumed
&lt;sup&gt;15&lt;/sup&gt;N&lt;sub&gt;2&lt;/sub&gt;O may have been retained as &lt;sup&gt;15&lt;/sup&gt;N in soil organic matter in
one sample. On average, &lt;sup&gt;15&lt;/sup&gt;N enrichment of soil organic matter during
the incubation may have corresponded to a retention of 0.019% (s.e. &amp;plusmn;0.14%; &lt;i&gt;n&lt;/i&gt;=4)
of the &lt;sup&gt;15&lt;/sup&gt;N&lt;sub&gt;2&lt;/sub&gt;O consumed by the soils. We
conclude that assimilatory reduction of N&lt;sub&gt;2&lt;/sub&gt;O plays, if at all, only a
negligible role in the consumption of N&lt;sub&gt;2&lt;/sub&gt;O in soils.</abstract>
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</article>

