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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>3</volume_number>
		<issue_number>2</issue_number>
		<publication_year>2006</publication_year>
	</journal>
	<doi>10.5194/bg-3-121-2006</doi>
	<article_url>http://www.biogeosciences.net/3/121/2006/</article_url>
	<abstract_html>http://www.biogeosciences.net/3/121/2006/bg-3-121-2006.html</abstract_html>
	<fulltext_pdf>http://www.biogeosciences.net/3/121/2006/bg-3-121-2006.pdf</fulltext_pdf>
	<start_page>121</start_page>
	<end_page>133</end_page>
	<publication_date>2006-03-16</publication_date>
	<article_title content_type="html">N&lt;sub&gt;2&lt;/sub&gt;O, NO and CH&lt;sub&gt;4&lt;/sub&gt; exchange, and microbial N turnover over a Mediterranean pine forest soil</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>P. Rosenkranz</name>
		</author>
		<author numeration="2" affiliations="1">
			<name>N. Brüggemann</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>H. Papen</name>
		</author>
		<author numeration="4" affiliations="2">
			<name>Z. Xu</name>
		</author>
		<author numeration="5" affiliations="3">
			<name>G. Seufert</name>
		</author>
		<author numeration="6" affiliations="1">
			<name>K. Butterbach-Bahl</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Karlsruhe Research Centre, Institute for Meteorology and Climate Research, Atmospheric Environmental Research (IMK-IFU), Kreuzeckbahnstr. 19, 82467 Garmisch-Partenkirchen, Germany</affiliation>
		<affiliation numeration="2" content_type="html">Institute for Atmospheric Physics, Beijing 100029, PR China</affiliation>
		<affiliation numeration="3" content_type="html">EC-Joint Research Centre, Environmental Institute, Via E. Fermi, 21020 Ispra, Italy</affiliation>
	</affiliations>
	<abstract content_type="html">Trace gas exchange of N&lt;sub&gt;2&lt;/sub&gt;O, NO/NO&lt;sub&gt;2&lt;/sub&gt; and CH&lt;sub&gt;4&lt;/sub&gt; between soil and
the atmosphere was measured in a typical Mediterranean pine (&lt;I&gt;Pinus pinaster&lt;/I&gt;) forest during
two intensive field campaigns in spring and autumn 2003. Furthermore, gross
and net turnover rates of N mineralization and nitrification as well as soil
profiles of N&lt;sub&gt;2&lt;/sub&gt;O and CH&lt;sub&gt;4&lt;/sub&gt; concentrations were determined. For both
seasons a weak but significant N&lt;sub&gt;2&lt;/sub&gt;O uptake from the atmosphere into the
soil was observed. During the unusually dry and hot spring mean N&lt;sub&gt;2&lt;/sub&gt;O
uptake was &amp;minus;4.32 &amp;micro;g N m&lt;sup&gt;-2&lt;/sup&gt; h&lt;sup&gt;-1&lt;/sup&gt;, whereas during the wet and
mild autumn mean N&lt;sub&gt;2&lt;/sub&gt;O uptake was &amp;minus;7.85 &amp;micro;g N m&lt;sup&gt;-2&lt;/sup&gt; h&lt;sup&gt;-1&lt;/sup&gt;. The
observed N&lt;sub&gt;2&lt;/sub&gt;O uptake into the soil was linked to the very low
availability of inorganic nitrogen at the study site. Organic layer gross N
mineralization decreased from 5.06 mg N kg&lt;sup&gt;-1&lt;/sup&gt; SDW d&lt;sup&gt;-1&lt;/sup&gt; in
springtime to 2.68 mg N kg&lt;sup&gt;-1&lt;/sup&gt; SDW d&lt;sup&gt;-1&lt;/sup&gt; in autumn. Mean NO emission
rates were significantly higher in springtime (9.94 &amp;micro;g N m&lt;sup&gt;-2&lt;/sup&gt;
h&lt;sup&gt;-1&lt;/sup&gt;) than in autumn (1.43 &amp;micro;g N m&lt;sup&gt;-2&lt;/sup&gt; h&lt;sup&gt;-1&lt;/sup&gt;). A significant
positive correlation between NO emission rates and gross N mineralization as
well as nitrification rates was found. The negative correlation between NO
emissions and soil moisture was explained with a stimulation of aerobic NO
uptake under N limiting conditions. Since NO&lt;sub&gt;2&lt;/sub&gt; deposition was
continuously higher than NO emission rates the examined forest soil
functioned as a net NO&lt;sub&gt;x&lt;/sub&gt; sink. Observed mean net CH&lt;sub&gt;4&lt;/sub&gt; uptake rates
were in spring significantly higher (&amp;minus;73.34 &amp;micro;g C m&lt;sup&gt;-2&lt;/sup&gt; h&lt;sup&gt;-1&lt;/sup&gt;)
than in autumn (&amp;minus;59.67 &amp;micro;g C m&lt;sup&gt;-2&lt;/sup&gt; h&lt;sup&gt;-1&lt;/sup&gt;). Changes in CH&lt;sub&gt;4&lt;/sub&gt;
uptake rates were strongly negatively correlated with changes in soil
moisture. The N&lt;sub&gt;2&lt;/sub&gt;O and CH&lt;sub&gt;4&lt;/sub&gt; concentrations in different soil depths
revealed the organic layer and the upper 0.1 m of mineral soil as the most
important soil horizons for N&lt;sub&gt;2&lt;/sub&gt;O and CH&lt;sub&gt;4&lt;/sub&gt; consumption.</abstract>
	<references>
	</references>
</article>

