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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>Erwin E. Klaas</dc:contributor>
  <dc:contributor>T. Earl Kaiser</dc:contributor>
  <dc:creator>Harry M. Ohlendorf</dc:creator>
  <dc:date>1978</dc:date>
  <dc:description>&lt;p&gt; Residues of organochlorine compounds occur commonly in environmental samples and have been associated with adverse effects in numerous avian species (Cooke 1973; L. F. Stickel 1973; W. H. Stickel 1975; Ohlendorf et al. 1977; H. M. Ohlendorf, R. W. Risebrough, and K. Vermeer, unpublished manuscript). The affected species are usually terminal consumers, generally those feeding on aquatic organisms (primarily fish) or birds. &lt;/p&gt;&lt;p&gt; Brown Pelicans (&lt;i&gt;Pelecanus occidentalis&lt;/i&gt;), Double-crested Cormorants &lt;i&gt;(Phalacrocorax auritus)&lt;/i&gt;, and certain herons are among the species that have exhibited shell thinning in some regions (see Ohlendorf et al. 1977 for review). In 1972, we began a study to determine: (1) geographic differences in the occurrence of environmental pollutants in Anhingas (&lt;i&gt;Anhinga anhinga&lt;/i&gt;) and waders in the eastern United States; (2) differences in environmental pollutant levels among those species nesting at the same localities; and (3) whether eggshell thickness had changed since the widespread use of organochlorine pesticides began in the mid-1940's.&lt;/p&gt;&lt;p&gt; The wader species included in our study were: Great Blue Heron (&lt;i&gt;Ardea herodias&lt;/i&gt;), Green Heron (&lt;i&gt;Butorides virescens&lt;/i&gt;), Little Blue Heron (&lt;i&gt;Florida caerulea&lt;/i&gt;), Cattle Egret (&lt;i&gt;Bubulcus ibis&lt;/i&gt;), Reddish Egret (&lt;i&gt;Dichromanassa rufescens&lt;/i&gt;), Great Egret (&lt;i&gt;Casmerodius albus&lt;/i&gt;), Snowy Egret (&lt;i&gt;Egretta thula&lt;/i&gt;), Louisiana Heron (&lt;i&gt;Hydranassa tricolor&lt;/i&gt;), Black-crowned Night Heron (&lt;i&gt;Nycticorax nycticorax&lt;/i&gt;), Yellow-crowned Night Heron (&lt;i&gt;Nyctanassa violacea&lt;/i&gt;), Least Bittern (&lt;i&gt;Ixobrychus exilis&lt;/i&gt;), American Bittern (&lt;i&gt;Botaurus lentiginosus&lt;/i&gt;), Wood Stork (&lt;i&gt;Mycteria americana&lt;/i&gt;), Glossy Ibis (&lt;i&gt;Plegadis falcinellus&lt;/i&gt;), White Ibis (&lt;i&gt;Eudocimus&lt;/i&gt; &lt;i&gt;albus&lt;/i&gt;), and Roseate Spoonbill (&lt;i&gt;Ajaia&lt;/i&gt; &lt;i&gt;ajaja&lt;/i&gt;). &lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.2307/1520919</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Waterbird Society</dc:publisher>
  <dc:title>Organochlorine residues and eggshell thinning in anhingas and waders</dc:title>
  <dc:type>text</dc:type>
</oai_dc:dc>