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<front>
<journal-meta>
<journal-id journal-id-type="publisher">BGD</journal-id>
<journal-title-group>
<journal-title>Biogeosciences Discussions</journal-title>
<abbrev-journal-title abbrev-type="publisher">BGD</abbrev-journal-title>
<abbrev-journal-title abbrev-type="nlm-ta">Biogeosciences Discuss.</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">1810-6285</issn>
<publisher><publisher-name></publisher-name>
<publisher-loc>Göttingen, Germany</publisher-loc>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.5194/bgd-11-12341-2014</article-id>
<title-group>
<article-title>Are C-loss rates from drained peatlands constant over time? The additive value of soil profile based and flux budget approach</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Leifeld</surname>
<given-names>J.</given-names>
<ext-link>https://orcid.org/0000-0002-7245-9852</ext-link>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Bader</surname>
<given-names>C.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Borraz</surname>
<given-names>E.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Hoffmann</surname>
<given-names>M.</given-names>
<ext-link>https://orcid.org/0000-0002-2776-1403</ext-link>
</name>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Giebels</surname>
<given-names>M.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Sommer</surname>
<given-names>M.</given-names>
</name>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Augustin</surname>
<given-names>J.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>Agroscope, Institute for Sustainability Sciences, Climate/Air Pollution Group, Reckenholzstrasse 191, 8046 Zürich, Switzerland</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>Institute for Landscape Biogeochemistry, Leibniz-Centre for Agricultural Landscape Research (ZALF), Eberswalder Str. 84, 15374 Müncheberg, Germany</addr-line>
</aff>
<aff id="aff3">
<label>3</label>
<addr-line>Institute of Soil Landscape Research, Leibniz-Centre for Agricultural Landscape Research (ZALF), Eberswalder Str. 84, 15374 Müncheberg, Germany</addr-line>
</aff>
<aff id="aff4">
<label>4</label>
<addr-line>Institute of Earth- and Environmental Sciences, University of Potsdam, Karl-Liebknecht-Str. 24–25, 14476 Potsdam-Golm, Germany</addr-line>
</aff>
<pub-date pub-type="epub">
<day>15</day>
<month>08</month>
<year>2014</year>
</pub-date>
<volume>11</volume>
<issue>8</issue>
<fpage>12341</fpage>
<lpage>12373</lpage>
<permissions>
<copyright-statement>Copyright: &#x000a9; 2014 J. Leifeld et al.</copyright-statement>
<copyright-year>2014</copyright-year>
<license license-type="open-access">
<license-p>This work is licensed under the Creative Commons Attribution 3.0 Unported License. To view a copy of this licence, visit <ext-link ext-link-type="uri"  xlink:href="https://creativecommons.org/licenses/by/3.0/">https://creativecommons.org/licenses/by/3.0/</ext-link></license-p>
</license>
</permissions>
<self-uri xlink:href="https://bg.copernicus.org/preprints/11/12341/2014/bgd-11-12341-2014.html">This article is available from https://bg.copernicus.org/preprints/11/12341/2014/bgd-11-12341-2014.html</self-uri>
<self-uri xlink:href="https://bg.copernicus.org/preprints/11/12341/2014/bgd-11-12341-2014.pdf">The full text article is available as a PDF file from https://bg.copernicus.org/preprints/11/12341/2014/bgd-11-12341-2014.pdf</self-uri>
<abstract>
<p>Drained peatlands are CO&lt;sub&gt;2&lt;/sub&gt; hotspots and lose important soil functions over time. In
  contrast to mineral soils, their high carbon density induces long lasting and high
  emissions. These emissions can be estimated using various approaches which cover different system
  boundaries in time and space. Here we compare 5 years flux measurements from manual chambers with
  a soil profile based method to estimate carbon losses from two temperate fens under different
  management intensity drained at the end of the 19th century. According to the flux measurements,
  both grassland sites currently lose significant amounts of carbon as CO&lt;sub&gt;2&lt;/sub&gt; in the order of
  7.1 and 9.1 t CO&lt;sub&gt;2&lt;/sub&gt;-C ha&lt;sup&gt;&amp;minus;1&lt;/sup&gt;a&lt;sup&gt;&amp;minus;1&lt;/sup&gt; when managed non-intensively or
  intensively, respectively. Profile based estimates, which make use of the difference in ash
  concentration along the soil profile, reveal a total of 284 and 619 t C ha&lt;sup&gt;&amp;minus;1&lt;/sup&gt; since
  the onset of drainage. These substantial losses are accompanied by a sharp decrease in peat
  quality as measured by NMR spectroscopy, confirming that a large part of former topsoil material
  is already mineralized. On average, the profile based estimate converts to smaller annual loss
  rates of 2.2 (non-intensive) and 4.8 t CO&lt;sub&gt;2&lt;/sub&gt;&amp;minus;C ha&lt;sup&gt;&amp;minus;1&lt;/sup&gt;a&lt;sup&gt;&amp;minus;1&lt;/sup&gt; (intensive)
  management. Our data, together with historical flux measurements at this site, provide evidence
  that peat decomposition rates increased over time, despite declining organic matter quality. We
  suggest that higher management intensities (i.e., higher fertilization and changes in carbon
  export from the field), including drainage, and increased mean annual temperature may be important
  factors for higher emissions today. These two methods are complementary in terms of time horizon
  and system boundary and, in conjunction, confirm the long-term emission potential of temperate
  drained organic grassland soils.</p>
</abstract>
<counts><page-count count="33"/></counts>
</article-meta>
</front>
<body/>
<back>
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