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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>Elisabetta Dore</dc:contributor>
  <dc:contributor>Riccardo Biddau</dc:contributor>
  <dc:contributor>D. Kirk Nordstrom</dc:contributor>
  <dc:creator>Rosa Cidu</dc:creator>
  <dc:date>2018</dc:date>
  <dc:description>&lt;p&gt;We investigated the fate of Sb and As downstream of the abandoned Su Suergiu mine (Sardinia, Italy) and surrounding areas. The mined area is a priority in the Sardinian remediation plan for contaminated sites due to the high concentrations of Sb and As in the mining-related wastes, which may impact the Flumendosa River that supplies water for agriculture and domestic uses. Hydrogeochemical surveys conducted from 2005 to 2015 produced time-series data and downstream profiles of water chemistry at 46 sites. Water was sampled at: springs and streams unaffected by mining; adits and streams in the mine area; drainage from the slag heaps; stream water downstream of the slag drainages; and the Flumendosa River downstream from the confluence of the contaminated waters. At specific sites, water sampling was repeated under different flow conditions, resulting in a total of 99 samples. The water samples were neutral to slightly alkaline. Elevated Sb (up to 30&amp;nbsp;mg L&lt;sup&gt;−1&lt;/sup&gt;) and As (up to 16&amp;nbsp;mg L&lt;sup&gt;−1&lt;/sup&gt;) concentrations were observed in water flowing from the slag materials from where the Sb ore was processed. These slag materials were the main Sb and As source at Su Suergiu. A strong base, Na-carbonate, from the foundry wastes, had a major influence on mobilizing Sb and As. Downstream contamination can be explained by considering that: (1) the predominant aqueous species, Sb(OH)&lt;sub&gt;6&lt;/sub&gt; &lt;sup&gt;−&lt;/sup&gt; and HAsO&lt;sub&gt;4&lt;/sub&gt; &lt;sup&gt;−2&lt;/sup&gt;, are not favored in sorption processes at the observed pH conditions; (2) precipitation of Sb- and As-bearing solid phases was not observed, which is consistent with modeling results indicating undersaturation; and (3) the main decrease in dissolved Sb and As concentrations was by dilution. Dissolved As concentrations in the Flumendosa River did not generally exceed the EU limit of 10&amp;nbsp;µg L&lt;sup&gt;−1&lt;/sup&gt;, whereas dissolved Sb in the river downstream of the contamination source always exceeded the EU limit of 5&amp;nbsp;µg L&lt;sup&gt;−1&lt;/sup&gt;. Recent actions aimed at retaining runoff from the slag heaps are apparently not sufficiently mitigating contamination in the Flumendosa River.&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1007/s10230-017-0479-8</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Springer</dc:publisher>
  <dc:title>Fate of antimony and arsenic in contaminated waters at the abandoned Su Suergiu mine (Sardinia, Italy)</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>