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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>J.W. Ball</dc:contributor>
  <dc:contributor>T.D. Bullen</dc:contributor>
  <dc:contributor>S. J. Sutley</dc:contributor>
  <dc:creator>J. A. Izbicki</dc:creator>
  <dc:date>2008</dc:date>
  <dc:description>&lt;div id="abstracts" class="Abstracts"&gt;&lt;div id="aep-abstract-id19" class="abstract author" lang="en"&gt;&lt;div id="aep-abstract-sec-id20"&gt;&lt;p id="simple-para0115"&gt;Chromium(VI) concentrations in excess of the California Maximum Contaminant Level (MCL) of 50&amp;nbsp;μg/L occur naturally in alkaline, oxic ground-water in alluvial aquifers in the western Mojave Desert, southern California. The highest concentrations were measured in aquifers eroded from mafic rock, but Cr(VI) as high as 27&amp;nbsp;μg/L was measured in aquifers eroded from granitic rock. Chromium(VI) concentrations did not exceed 5&amp;nbsp;μg/L at pH&amp;nbsp;&amp;lt;&amp;nbsp;7.5 regardless of geology. δ&lt;sup&gt;53&lt;/sup&gt;Cr values in native ground-water ranged from 0.7 to 5.1‰ and values were fractionated relative to the average δ&lt;sup&gt;53&lt;/sup&gt;Cr composition of 0‰ in the earth’s crust. Positive δ&lt;sup&gt;53&lt;/sup&gt;Cr values of 1.2 and 2.3‰ were measured in ground-water recharge areas having low Cr concentrations, consistent with the addition of Cr(VI) that was fractionated on mineral surfaces prior to entering solution. δ&lt;sup&gt;53&lt;/sup&gt;Cr values, although variable, did not consistently increase or decrease with increasing Cr concentrations as ground-water flowed down gradient through more oxic portions of the aquifer. However, increasing δ&lt;sup&gt;53&lt;/sup&gt;Cr values were observed as dissolved O&lt;sub&gt;2&lt;/sub&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;concentrations decreased, and Cr(VI) was reduced to Cr(III), and subsequently removed from solution. As a result, the highest δ&lt;sup&gt;53&lt;/sup&gt;Cr values were measured in water from deep wells, and wells in discharge areas near dry lakes at the downgradient end of long flow paths through alluvial aquifers. δ&lt;sup&gt;53&lt;/sup&gt;Cr values at an industrial site overlying mafic alluvium having high natural background Cr(VI) concentrations ranged from −0.1 to 3.2‰. Near zero δ&lt;sup&gt;53&lt;/sup&gt;Cr values at the site were the result of anthropogenic Cr. However, mixing with native ground-water and fractionation of Cr within the plume increased δ&lt;sup&gt;53&lt;/sup&gt;Cr values at the site. Although δ&lt;sup&gt;53&lt;/sup&gt;Cr was not necessarily diagnostic of anthropogenic Cr, it was possible to identify the extent of anthropogenic Cr at the site on the basis of the δ&lt;sup&gt;53&lt;/sup&gt;Cr values in conjunction with major-ion data, and the δ&lt;sup&gt;18&lt;/sup&gt;O and δD composition of water from wells.&lt;/p&gt;&lt;/div&gt;&lt;/div&gt;&lt;/div&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/j.apgeochem.2007.11.015</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>Chromium, chromium isotopes and selected trace elements, western Mojave Desert, USA</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>