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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>George N. Breit</dc:contributor>
  <dc:contributor>Alan H. Welch</dc:contributor>
  <dc:contributor>James C. Yount</dc:contributor>
  <dc:contributor>John W. Whitney</dc:contributor>
  <dc:contributor>Andrea L. Foster</dc:contributor>
  <dc:contributor>M.N. Uddin</dc:contributor>
  <dc:contributor>R.K. Majumder</dc:contributor>
  <dc:contributor>N. Ahmed</dc:contributor>
  <dc:creator>Kenneth G. Stollenwerk</dc:creator>
  <dc:date>2007</dc:date>
  <dc:description>&lt;p&gt;Recognition of arsenic (As) contamination of shallow fluvio-deltaic aquifers in the Bengal Basin has resulted in increasing exploitation of groundwater from deeper aquifers that generally contain low concentrations of dissolved As. Pumping-induced infiltration of high-As groundwater could eventually cause As concentrations in these aquifers to increase. This study investigates the adsorption capacity for As of sediment from a low-As aquifer near Dhaka, Bangladesh. A shallow, chemically-reducing aquifer at this site extends to a depth of 50&amp;nbsp;m and has maximum As concentrations in groundwater of 900&amp;nbsp;μg/L. At depths greater than 50&amp;nbsp;m, geochemical conditions are more oxidizing and groundwater has &amp;lt;&amp;nbsp;5&amp;nbsp;μg/L As. There is no thick layer of clay at this site to inhibit vertical transport of groundwater.&lt;/p&gt;&lt;p&gt;Arsenite [As(III)] is the dominant oxidation state in contaminated groundwater; however, data from laboratory batch experiments show that As(III) is oxidized to arsenate [As(V)] by manganese (Mn) minerals that are present in the oxidized sediment. Thus, the long-term viability of the deeper aquifers as a source of water supply is likely to depend on As(V) adsorption. The adsorption capacity of these sediments is a function of the oxidation state of As and the concentration of other solutes that compete for adsorption sites. Arsenite that was not oxidized did adsorb, but to a much lesser extent than As(V). Phosphate (P) caused a substantial decrease in As(V) adsorption. Increasing pH and concentrations of silica (Si) had lesser effects on As(V) adsorption. The effect of bicarbonate (HCO&lt;sub&gt;3&lt;/sub&gt;) on As(V) adsorption was negligible. Equilibrium constants for adsorption of As(V), As(III), P, Si, HCO&lt;sub&gt;3&lt;/sub&gt;, and H were determined from the experimental data and a quantitative model developed. Oxidation of As(III) was modeled with a first-order rate constant. This model was used to successfully simulate As(V) adsorption in the presence of multiple competing solutes. Results from these experiments show that oxidized sediments have a substantial but limited capacity for removal of As from groundwater.&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/j.scitotenv.2006.11.029</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>Arsenic attenuation by oxidized aquifer sediments in Bangladesh</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>