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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>James J. Garner</dc:contributor>
  <dc:contributor>Brian Weidel</dc:contributor>
  <dc:contributor>Daryl J. McGoldrick</dc:contributor>
  <dc:contributor>Maureen G. Walsh</dc:contributor>
  <dc:contributor>Thomas M. Holsen</dc:contributor>
  <dc:creator>James J. Pagano</dc:creator>
  <dc:date>2021</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;Alewife (&lt;/span&gt;&lt;i&gt;Alosa pseudoharengus&lt;/i&gt;&lt;span&gt;) are the preferred prey species of the top&amp;nbsp;piscivore&amp;nbsp;predators in the Lake Ontario food web and are an essential constituent in the bioaccumulation of&amp;nbsp;persistent organic contaminants. Year-class samples collected in 2016 represent the alewife age ranges of 2015 (Age-01) sequentially dating back to 2008 (Age-08). The most abundant contaminant measured in Lake Ontario alewife (151.5&amp;nbsp;ng/g) were total&amp;nbsp;polychlorinated biphenyls&amp;nbsp;(PCBs), increasing at a rate of 11.8&amp;nbsp;ng/g per year on an age-averaged concentration basis. Total mercury demonstrated the largest percent increase (240%) accumulated over alewife ages of 1–8&amp;nbsp;years. Average total concentrations of the most abundant polychlorinated dibenzo-p-dioxin&amp;nbsp;isomer&amp;nbsp;(2378-tetrachlorinated dibenzo-p-dioxin (TCDD), 1.3&amp;nbsp;pg/g) and polychlorinated&amp;nbsp;dibenzofuran&amp;nbsp;isomer (2378-tetrachlorinated dibenzofuran (2378-TCDF), 6.6&amp;nbsp;pg/g) comprised most of the overall total dioxin (2.5&amp;nbsp;pg/g) and total furan concentrations (8.7&amp;nbsp;pg/g). The vast majority (69%) of alewife total toxic equivalence (TEQ) was comprised of the non-ortho coplanar PCBs. Both mammal and avian wildlife protection values based on total TEQ were uniformly exceeded for the dioxin-like compounds measured in Lake Ontario alewife. Ontogenetic dietary influences expressed a significant impact on Age-01 alewife age-contaminant relationships and age-stable isotope concentrations and trends for legacy contaminants. Total Hg and all dioxin-like contaminants did not demonstrate the Age-01 ontogenetic dietary effects found in legacy contaminants. A prominent polychlorinated&amp;nbsp;naphthalene&amp;nbsp;(PCN) concentration peak measured in year-class Age-04 alewife was followed by a corresponding lake trout peak 3–4&amp;nbsp;years later illustrating a unique example of trophic-level contaminant uptake and concomitant integration delay.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/j.jglr.2021.04.016</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>Legacy contaminant-stable isotope-age relationships in Lake Ontario year-class Alewife (Alosa pseudoharengus)</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>