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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>John A.D. Burnett</dc:contributor>
  <dc:creator>Robert O’Gorman</dc:creator>
  <dc:date>2001</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;Fishes were assessed in Guffin, Chaumount, and Black River bays in northeastern Lake Ontario with a 7.9-m (headrope) bottom trawl during late September and early October, 1978 to 1997. Fish density declined in the early 1990s with sharp declines in abundance of spottail shiner (&lt;/span&gt;&lt;i&gt;Notropis hudsonius&lt;/i&gt;&lt;span&gt;), trout-perch (&lt;/span&gt;&lt;i&gt;Percopsis omiscomaycus&lt;/i&gt;&lt;span&gt;), and johnny darter (Etheostoma nigrum) occurring in 1993 to 1995. Rising numbers of piscivores, walleye (&lt;/span&gt;&lt;i&gt;Stizostedion vitreum&lt;/i&gt;&lt;span&gt;) and double-crested cormorant (&lt;/span&gt;&lt;i&gt;Phalacrocorax auritus&lt;/i&gt;&lt;span&gt;), increased predation pressure, presumably acting in concert with oligotrophication to lower fish density, particularly after 1991 when large numbers of adult alewife (&lt;/span&gt;&lt;i&gt;Alosa pseudoharengus&lt;/i&gt;&lt;span&gt;) no longer migrated to the northeast basin in spring. Annual mortality of yellow perch (&lt;/span&gt;&lt;i&gt;Perca flavescens&lt;/i&gt;&lt;span&gt;) from age 2 to 5 rose from 33% in 1980&amp;ndash;83 to 65% in 1992&amp;ndash;95 and was positively related to piscivore numbers (&lt;/span&gt;&lt;i&gt;P&lt;/i&gt;&lt;span&gt;&amp;nbsp;= 0.01, r = 0.96, n = 5). Annual mortality of yellow perch from age 0 to 2 also peaked in 1992&amp;ndash;95. Abundance of yellow perch YOY in fall varied 40 fold and was not related to water warming in spring (&lt;/span&gt;&lt;i&gt;P&lt;/i&gt;&lt;span&gt;&amp;nbsp;= 0.45, r = &amp;minus;0.19, n = 18) but was negatively related to the abundance of adult alewives in spring (&lt;/span&gt;&lt;i&gt;P&lt;/i&gt;&lt;span&gt;&amp;nbsp;= 0.04, r = &amp;minus;0.49, n = 18). Although yellow perch produced moderate to strong year classes each year during 1991&amp;ndash;95, stock size failed to increase because of rapidly accelerating mortality. Fully 85% of the variation in mean length of yellow perch YOY was explained by a multiple regression model which included YOY abundance, mean total phosphorus, and cumulative degree days &amp;gt; 13.5&amp;deg;C (&lt;/span&gt;&lt;i&gt;P&lt;/i&gt;&lt;span&gt;&amp;nbsp;&amp;lt; 0.01, n = 15). Abundance of white perch (&lt;/span&gt;&lt;i&gt;Morone americana&lt;/i&gt;&lt;span&gt;) YOY varied nearly 200 fold and was not related to water warming or spring alewife abundance (&lt;/span&gt;&lt;i&gt;P&lt;/i&gt;&lt;span&gt;&amp;nbsp;&amp;gt; 0.15). Variation in mean length of white perch YOY was related to cumulative degree days &amp;gt; 15&amp;deg;C (&lt;/span&gt;&lt;i&gt;P&lt;/i&gt;&lt;span&gt;&amp;nbsp;&amp;lt; 0.01, r = 0.69).&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/S0380-1330(01)70652-1</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>Fish community dynamics in northeastern Lake Ontario with emphasis on the growth and reproductive success of yellow perch (&lt;i&gt;Perca flavescens&lt;/i&gt;) and white perch (&lt;i&gt;Morone americana&lt;/i&gt;), 1978 to1997</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>