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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>Christopher G. Ingersoll</dc:contributor>
  <dc:contributor>William G. Brumbaugh</dc:contributor>
  <dc:contributor>Nile E. Kemble</dc:contributor>
  <dc:contributor>Thomas W. May</dc:contributor>
  <dc:contributor>Ning Wang</dc:contributor>
  <dc:contributor>Donald D. MacDonald</dc:contributor>
  <dc:contributor>Andrew D. Roberts</dc:contributor>
  <dc:creator>John M. Besser</dc:creator>
  <dc:date>2015</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;Sediment toxicity tests compared chronic effects on survival, growth, and biomass of juvenile freshwater mussels (28-d exposures with &lt;/span&gt;&lt;i&gt;Lampsilis siliquoidea&lt;/i&gt;&lt;span&gt;) to the responses of standard test organisms&amp;mdash;amphipods (28-d exposures with&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;/span&gt;&lt;i&gt;Hyalella azteca&lt;/i&gt;&lt;span&gt;) and midges (10-d exposures with&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;/span&gt;&lt;i&gt;Chironomus dilutus&lt;/i&gt;&lt;span&gt;)&amp;mdash;in sediments from 2 lead&amp;ndash;zinc mining areas: the Tri-State Mining District and Southeast Missouri Mining District. Mussel tests were conducted in sediments sieved to &amp;lt;0.25&amp;thinsp;mm to facilitate recovery of juvenile mussels (2&amp;ndash;4 mo old). Sediments were contaminated primarily with lead, zinc, and cadmium, with greater zinc and cadmium concentrations in Tri-State sediments and greater lead concentrations in southeast Missouri sediments. The frequency of highly toxic responses (reduced 10% or more relative to reference sites) in Tri-State sediments was greatest for amphipod survival (25% of samples), midge biomass (20%), and mussel survival (14%). In southeast Missouri sediments, the frequency of highly toxic samples was greatest for mussel biomass (25%) and amphipod biomass (13%). Thresholds for metal toxicity to mussels, expressed as hazard quotients based on probable effect concentrations, were lower for southeast Missouri sediments than for Tri-State sediments. Southeast Missouri sites with toxic sediments had 2 or fewer live mussel taxa in a concurrent mussel population survey, compared with 7 to 26 taxa at reference sites. These results demonstrate that sediment toxicity tests with juvenile mussels can be conducted reliably by modifying existing standard methods; that the sensitivity of mussels to metals can be similar to or greater than standard test organisms; and that responses of mussels in laboratory toxicity tests are consistent with effects on wild mussel populations.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1002/etc.2849</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>John Wiley &amp; Sons, Inc.</dc:publisher>
  <dc:title>Toxicity of sediments from lead-zinc mining areas to juvenile freshwater mussels (Lampsilis siliquoidea) compared to standard test organisms</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>