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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>S.E. MacAvoy</dc:contributor>
  <dc:contributor>M.B. Steg</dc:contributor>
  <dc:contributor>A.J. Bulger</dc:contributor>
  <dc:creator>T.E. Dennis</dc:creator>
  <dc:date>1995</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;As part of the “Shenandoah National Park: Fish in Sensitive Habitats” (SNP:FISH) project, the blacknose dace (&lt;/span&gt;&lt;i class="EmphasisTypeItalic "&gt;Rhinichthys atratulus&lt;/i&gt;&lt;span&gt;) was utilized as an indicator species to assess the susceptibility of the ichthyofaunal community of Shenandoah National Park (USA) to acidification. Water chemistry (ANC, conductivity, pH, and concentrations of Ca&lt;/span&gt;&lt;sup&gt;2+&lt;/sup&gt;&lt;span&gt;, Mg&lt;/span&gt;&lt;sup&gt;2+&lt;/sup&gt;&lt;span&gt;, Na&lt;/span&gt;&lt;sup&gt;+&lt;/sup&gt;&lt;span&gt;, K&lt;/span&gt;&lt;sup&gt;+&lt;/sup&gt;&lt;span&gt;, Cl&lt;/span&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;, NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;, SO&lt;/span&gt;&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;2−&lt;/sup&gt;&lt;span&gt;, and SiO&lt;/span&gt;&lt;sub&gt;2&lt;/sub&gt;&lt;span&gt;) was sampled every three months over the course of 3 1/4 years which represents the probable maximum lifetime of&amp;nbsp;&lt;/span&gt;&lt;i class="EmphasisTypeItalic "&gt;R atratulus. Condition factors&lt;/i&gt;&lt;span&gt;&amp;nbsp;(K=[g/mm&lt;/span&gt;&lt;sup&gt;3&lt;/sup&gt;&lt;span&gt;]&lt;/span&gt;&lt;sup&gt;*&lt;/sup&gt;&lt;span&gt;10&lt;/span&gt;&lt;sup&gt;6&lt;/sup&gt;&lt;span&gt;) were calculated for samples of fish (age class 2+ yr; n=370) from nine montane, second/third order streams representing a range of ANCs. A principle components regression was performed on factor scores from a principle components analysis of the water chemistry variables and fish condition factor. Two factors, one associated with stream water ANC and ion concentrations, and another associated with SO&lt;/span&gt;&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;2−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;concentration, collectively explained 84% of the variance in condition factor. The influence of variables other than water chemistry upon&amp;nbsp;&lt;/span&gt;&lt;i class="EmphasisTypeItalic "&gt;R atratulus K&lt;/i&gt;&lt;span&gt;&amp;nbsp;is addressed. The results show that environmental chemistry is highly associated with the&amp;nbsp;&lt;/span&gt;&lt;i class="EmphasisTypeItalic "&gt;K&lt;/i&gt;&lt;span&gt;&amp;nbsp;of&amp;nbsp;&lt;/span&gt;&lt;i class="EmphasisTypeItalic "&gt;R atratulus.&lt;/i&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1007/BF00476856</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Springer</dc:publisher>
  <dc:title>The association of water chemistry variables and fish condition in streams of Shenandoah National Park (USA)</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>