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<oai_dc:dc xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
  <dc:contributor>M.R. Chivers</dc:contributor>
  <dc:contributor>M.R. Turetsky</dc:contributor>
  <dc:contributor>Claire C. Treat</dc:contributor>
  <dc:contributor>D.G. Petersen</dc:contributor>
  <dc:contributor>M. Waldrop</dc:contributor>
  <dc:contributor>J.W. Harden</dc:contributor>
  <dc:contributor>A. D. McGuire</dc:contributor>
  <dc:creator>E.S. Kane</dc:creator>
  <dc:date>2013</dc:date>
  <dc:description>To test the effects of altered hydrology on organic soil decomposition, we investigated CO&lt;sub&gt;2&lt;/sub&gt; and CH&lt;sub&gt;4&lt;/sub&gt; production potential of rich-fen peat (mean surface pH = 6.3) collected from a field water table manipulation experiment including control, raised and lowered water table treatments. Mean anaerobic CO&lt;sub&gt;2&lt;/sub&gt; production potential at 10 cm depth (14.1 ± 0.9 μmol C g&lt;sup&gt;−1&lt;/sup&gt; d&lt;sup&gt;−1&lt;/sup&gt;) was as high as aerobic CO&lt;sub&gt;2&lt;/sub&gt; production potential (10.6 ± 1.5 μmol C g&lt;sup&gt;−1&lt;/sup&gt; d&lt;sup&gt;−1&lt;/sup&gt;), while CH4 production was low (mean of 7.8 ± 1.5 nmol C g&lt;sup&gt;−1&lt;/sup&gt; d&lt;sup&gt;−1&lt;/sup&gt;). Denitrification enzyme activity indicated a very high denitrification potential (197 ± 23 μg N g&lt;sup&gt;−1&lt;/sup&gt; d&lt;sup&gt;−1&lt;/sup&gt;), but net NO&lt;sup&gt;-&lt;/sup&gt;&lt;sub&gt;3&lt;/sub&gt; reduction suggested this was a relatively minor pathway for anaerobic CO&lt;sub&gt;2&lt;/sub&gt; production. Abundances of denitrifier genes (&lt;i&gt;nirK&lt;/i&gt; and &lt;i&gt;nosZ&lt;/i&gt;) did not change across water table treatments. SO&lt;sup&gt;2-&lt;/sup&gt;&lt;sub&gt;4&lt;/sub&gt; reduction also did not appear to be an important pathway for anaerobic CO&lt;sub&gt;2&lt;/sub&gt; production. The net accumulation of acetate and formate as decomposition end products in the raised water table treatment suggested that fermentation was a significant pathway for carbon mineralization, even in the presence of NO&lt;sup&gt;-&lt;/sup&gt;&lt;sub&gt;3&lt;/sub&gt;. Dissolved organic carbon (DOC) concentrations were the strongest predictors of potential anaerobic and aerobic CO&lt;sub&gt;2&lt;/sub&gt; production. Across all water table treatments, the CO&lt;sub&gt;2&lt;/sub&gt;:CH&lt;sub&gt;4&lt;/sub&gt; ratio increased with initial DOC leachate concentrations. While the field water table treatment did not have a significant effect on mean CO&lt;sub&gt;2&lt;/sub&gt; or CH&lt;sub&gt;4&lt;/sub&gt; production potential, the CO&lt;sub&gt;2&lt;/sub&gt;:CH&lt;sub&gt;4&lt;/sub&gt; ratio was highest in shallow peat incubations from the drained treatment. These data suggest that with continued drying or with a more variable water table, anaerobic CO&lt;sub&gt;2&lt;/sub&gt; production may be favored over CH&lt;sub&gt;4&lt;/sub&gt; production in this rich fen. Future research examining the potential for dissolved organic substances to facilitate anaerobic respiration, or alternative redox processes that limit the effectiveness of organic acids as substrates in anaerobic metabolism, would help explain additional uncertainty concerning carbon mineralization in this system.</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/j.soilbio.2012.10.032</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Pergamon</dc:publisher>
  <dc:title>Response of anaerobic carbon cycling to water table manipulation in an Alaskan rich fen</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>