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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>B.A. Bekins</dc:contributor>
  <dc:contributor>M.J. Baedecker</dc:contributor>
  <dc:contributor>G. R. Aiken</dc:contributor>
  <dc:contributor>R.P. Eganhouse</dc:contributor>
  <dc:contributor>M.E. Tuccillo</dc:contributor>
  <dc:creator>I.M. Cozzarelli</dc:creator>
  <dc:date>2001</dc:date>
  <dc:description>&lt;div id="abstracts" class="Abstracts"&gt;&lt;div id="aep-abstract-id18" class="abstract author"&gt;&lt;div id="aep-abstract-sec-id19"&gt;&lt;p&gt;&lt;span&gt;A 16-year study of a hydrocarbon&amp;nbsp;plume&amp;nbsp;shows that the extent of contaminant migration and compound-specific&amp;nbsp;behavior&amp;nbsp;have changed as redox reactions, most notably iron reduction, have progressed over time. Concentration changes at a small scale, determined from analysis of&amp;nbsp;pore-water&amp;nbsp;samples drained from&amp;nbsp;aquifer&amp;nbsp;cores, are compared with concentration changes at the plume scale, determined from analysis of water samples from an observation&amp;nbsp;well&amp;nbsp;network. The small-scale data show clearly that the hydrocarbon plume is growing slowly as&amp;nbsp;sediment&amp;nbsp;iron oxides&amp;nbsp;are depleted. Contaminants, such as&amp;nbsp;&lt;/span&gt;&lt;i&gt;ortho&lt;/i&gt;&lt;span&gt;-xylene that appeared not to be moving downgradient from the&amp;nbsp;oil&amp;nbsp;on the basis of observation well data, are migrating in thin layers as the aquifer evolves to methanogenic conditions. However, the plume-scale observation well data show that the downgradient extent of the Fe&lt;/span&gt;&lt;sup&gt;2+&lt;/sup&gt;&lt;span&gt;&amp;nbsp;and BTEX plume did not change between 1992 and 1995. Instead, depletion of the unstable Fe (III)&amp;nbsp;oxides&amp;nbsp;near the subsurface crude-oil source has caused the maximum dissolved iron concentration zone within the plume to spread at a rate of approximately 3 m/year. The zone of maximum concentrations of&amp;nbsp;benzene, toluene, ethylbenzene and&amp;nbsp;xylene&amp;nbsp;(BTEX) has also spread within the anoxic plume. In monitoring the&amp;nbsp;remediation&amp;nbsp;of hydrocarbon-contaminated&amp;nbsp;ground water&amp;nbsp;by&amp;nbsp;natural attenuation, subtle concentration changes in observation well data from the anoxic zone may be diagnostic of depletion of the intrinsic electron-accepting capacity of the aquifer. Recognition of these subtle patterns may allow early&amp;nbsp;prediction&amp;nbsp;of growth of the hydrocarbon plume.&lt;/span&gt;&lt;/p&gt;&lt;/div&gt;&lt;/div&gt;&lt;/div&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/S0169-7722(01)00174-7</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>Progression of natural attenuation processes at a crude-oil spill site . I. Geochemical evolution of the plume</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>