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      <dc:title>Improving Cr (VI) Extraction through Electrodialysis</dc:title>
      <dc:creator>García-Delgado, Rafael Antonio</dc:creator>
      <dc:creator>Nieto-Castilo, A</dc:creator>
      <dc:creator>Villén-Guzmán, María Dolores</dc:creator>
      <dc:creator>Cerrillo-González, María del Mar</dc:creator>
      <dc:creator>Gómez-Lahoz, César</dc:creator>
      <dc:creator>Vereda-Alonso, Carlos</dc:creator>
      <dc:creator>Paz-García, Juan Manuel</dc:creator>
      <dc:creator>Rodríguez-Maroto, José Miguel</dc:creator>
      <dc:subject>Electrodiálisis</dc:subject>
      <dc:description>A laboratory study has been carried out to determine the feasibility of in situ remediation of chromium (VI)&#xd;
contaminated soil using electrodialysis. In a classic setup, this technique implies the application of a low intensity direct&#xd;
current to the soil, which is separated from the electrode compartments by ion-exchange membranes. If the pollutants&#xd;
are ionic compounds, they can be forced to migrate to the oppositely charged electrode by electro-migration.&#xd;
Membranes selectively impede the flow of ions in the electrode compartments back to the soil. If a metal species is&#xd;
naturally present as an anion, mobilization from the soil at alkaline pH can be realized and, at the same time, the&#xd;
mobilization of other metal cations that occur at low pH can be minimized.&#xd;
Experiments have been carried out with clayey soils (kaolinite clay and soil clay mixtures) that have been&#xd;
characterized and then contaminated by mixing with a potassium dichromate solution for several days. Initial Cr (VI)&#xd;
content ranges from 500 to 4000 mg/kg. Treatment tests were carried out in an acrylic laboratory cells consisting of a&#xd;
central soil compartment and two electrode compartments located at both ends of the column. Dimensionally stable&#xd;
titanium electrodes coated with mixed metal oxides were placed in the electrode compartments. 0.01M Na2SO4&#xd;
electrolytes were recirculated through them from two 1-liter deposits using a peristaltic pump. Two commercial ion&#xd;
exchange membranes separated the anolyte and catholyte compartments from the soil in the standard configuration. A&#xd;
programmable DC: power supply was connected to the electrodes and a computer for data acquisition.</dc:description>
      <dc:date>2019-10-08T07:53:58Z</dc:date>
      <dc:date>2019-10-08T07:53:58Z</dc:date>
      <dc:date>2019</dc:date>
      <dc:date>2019-10-08</dc:date>
      <dc:type>conference output</dc:type>
      <dc:identifier>https://hdl.handle.net/10630/18535</dc:identifier>
      <dc:language>eng</dc:language>
      <dc:relation>The 17th International Symposium on Electrokinetic Remediation (EREM 2019)</dc:relation>
      <dc:relation>San Miguel de Allende (Guanajuato, México)</dc:relation>
      <dc:relation>22 - 27 septiembre de 2019</dc:relation>
      <dc:rights>open access</dc:rights>
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