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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>Paul D. Brooks</dc:contributor>
  <dc:contributor>Arvin Mosier</dc:contributor>
  <dc:contributor>Kathy A. Tonnessen</dc:contributor>
  <dc:creator>Mark W. Williams</dc:creator>
  <dc:date>1996</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;In an effort to understand sources of nitrate (NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;) in surface waters of high-elevation catchments, nitrogen (N) transformations in and under seasonal snow were investigated from 1993 to 1995 on Niwot Ridge, an alpine ecosystem at 3,500 m located in the Colorado Front Range of the Rocky Mountains. Ammonium (NH&lt;/span&gt;&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt;&lt;span&gt;) and NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;labeled with&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;/span&gt;&lt;sup&gt;15&lt;/sup&gt;&lt;span&gt;N applied as nonconservative tracers to the snow showed no evidence of nitrification in the snowpack. Furthermore, NH&lt;/span&gt;&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt;&lt;span&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;movement through the amended snowpack was highly correlated with a conservative chloride tracer (&lt;/span&gt;&lt;i&gt;r&lt;/i&gt;&lt;sup&gt;2&lt;/sup&gt;&lt;span&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;= 0.99). In an unamended snowpack NH&lt;/span&gt;&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt;&lt;span&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;concentrations in meltwater before contact with the ground were highly correlated with NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;concentrations (&lt;/span&gt;&lt;i&gt;r&lt;/i&gt;&lt;sup&gt;2&lt;/sup&gt;&lt;span&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;= 0.98), which is consistent with no nitrification in the snowpack. The isotopically labeled&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;/span&gt;&lt;sup&gt;15&lt;/sup&gt;&lt;span&gt;NH&lt;/span&gt;&lt;sup&gt;+&lt;/sup&gt;&lt;sub&gt;4&lt;/sub&gt;&lt;span&gt;applied to the snowpack was found in underlying soils, showing that NH&lt;/span&gt;&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt;&lt;span&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;released from snow can be rapidly immobilized. Resin bag (mixed-bed ion-exchange resins) measurements (n = 22) showed that 80% of the mobile inorganic N in unamended subnivial soils was NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;. Measurements of KCl-extractable inorganic N from surface soils showed that highest values were prior to the initiation of snowmelt and lowest values were during the growing season. The natural δ&lt;/span&gt;&lt;sup&gt;15&lt;/sup&gt;&lt;span&gt;N abundance of unamended soils was negative and ranged from −12 to −2, suggesting that atmospheric deposition of δ&lt;/span&gt;&lt;sup&gt;15&lt;/sup&gt;&lt;span&gt;N-depleted N is an important component of N cycling in these alpine soils. These results suggest that soil mineralization under seasonal snow, rather than snowmelt release of NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;, may control NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;concentrations in surface waters of high-elevation catchments.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1029/96WR02240</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>American Geophysical Union</dc:publisher>
  <dc:title>Mineral nitrogen transformations in and under seasonal snow in a high-elevation catchment in the Rocky Mountains, United States</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>