Distribution and Elimination of Polychlorinated Dibenzo-p-dioxins, Dibenzofurans, Biphenyls, and p,p‘-DDE in Tissues of Bald Eagles from the Upper Peninsula of Michigan

Liver, muscle, fat, kidney, and gall bladder of eight bald eagles (Haliaeetus leucocephalus) found dead in the Upper Peninsula of Michigan during 2000 were analyzed for the presence of polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and biphenyls (including coplanar PCBs), p,p‘-DDE...

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Veröffentlicht in:Environmental science & technology 2002-07, Vol.36 (13), p.2789-2796
Hauptverfasser: Senthil Kumar, Kurunthachalam, Kannan, Kurunthachalam, Giesy, John P, Masunaga, Shigeki
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Kannan, Kurunthachalam
Giesy, John P
Masunaga, Shigeki
description Liver, muscle, fat, kidney, and gall bladder of eight bald eagles (Haliaeetus leucocephalus) found dead in the Upper Peninsula of Michigan during 2000 were analyzed for the presence of polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and biphenyls (including coplanar PCBs), p,p‘-DDE, and hexachlorobenzene (HCB). Necropsy results showed that the birds suffered from peritonitis, bacterial infection, or trauma. Concentrations of PCDD/DFs in livers ranged from 23 to 4500 pg/g on a wet weight basis (wet wt), whereas the least concentrations were found in blood plasma of bald eagle nestlings (2.3−49 pg/g, wet wt). A maximum total PCB concentration of 280000 ng/g, wet wt, was found in the liver of a dead bald eagle affected by peritonitis. The greatest concentrations of p,p‘-DDE and HCB in eagle livers were 17000 and 120 ng/g, wet wt, respectively. Eagles with elevated 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) or total PCB concentra tions tended to have great TCDD/TCDF or PCB126/PCB77 ratios, hypothesized to be due to induction of cytochrome P450 enzymes and subsequent metabolism of TCDF and PCB77. Concentrations of TCDD toxic equivalents (TEQs) in the tissues of bald eagles exceeded the thresholds for toxicity in a few avian species. Non-ortho coplanar PCBs accounted for 68−88% of the total TEQs in bald eagle tissues. PCDDs and PCDFs collectively accounted for, on average, 17% of the total TEQs. On the basis of the analysis of a single gall bladder with bile, biliary excretion rates of PCDDs, PCDFs, and PCBs were estimated as 0.015−0.02% per day.
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Non-ortho coplanar PCBs accounted for 68−88% of the total TEQs in bald eagle tissues. PCDDs and PCDFs collectively accounted for, on average, 17% of the total TEQs. 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Psychology ; Insecticides - analysis ; Insecticides - pharmacokinetics ; Michigan ; PCB ; Polychlorinated biphenyls ; Polychlorinated Biphenyls - analysis ; Polychlorinated Biphenyls - pharmacokinetics ; Polychlorinated Dibenzodioxins - analogs &amp; derivatives ; Polychlorinated Dibenzodioxins - analysis ; Polychlorinated Dibenzodioxins - pharmacokinetics ; Raptors ; Soil Pollutants - analysis ; Soil Pollutants - pharmacokinetics ; Tissue Distribution ; Wildfowl</subject><ispartof>Environmental science &amp; technology, 2002-07, Vol.36 (13), p.2789-2796</ispartof><rights>Copyright © 2002 American Chemical Society</rights><rights>2002 INIST-CNRS</rights><rights>Copyright American Chemical Society Jul 1, 2002</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-a563t-64883a104e435da2d1391f6ee71587a8cd440ceb03aec5cf373fd8febf2322923</citedby><cites>FETCH-LOGICAL-a563t-64883a104e435da2d1391f6ee71587a8cd440ceb03aec5cf373fd8febf2322923</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://pubs.acs.org/doi/pdf/10.1021/es0114660$$EPDF$$P50$$Gacs$$H</linktopdf><linktohtml>$$Uhttps://pubs.acs.org/doi/10.1021/es0114660$$EHTML$$P50$$Gacs$$H</linktohtml><link.rule.ids>314,776,780,2752,27053,27901,27902,56713,56763</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&amp;idt=13791357$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/12144248$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Senthil Kumar, Kurunthachalam</creatorcontrib><creatorcontrib>Kannan, Kurunthachalam</creatorcontrib><creatorcontrib>Giesy, John P</creatorcontrib><creatorcontrib>Masunaga, Shigeki</creatorcontrib><title>Distribution and Elimination of Polychlorinated Dibenzo-p-dioxins, Dibenzofurans, Biphenyls, and p,p‘-DDE in Tissues of Bald Eagles from the Upper Peninsula of Michigan</title><title>Environmental science &amp; technology</title><addtitle>Environ. Sci. Technol</addtitle><description>Liver, muscle, fat, kidney, and gall bladder of eight bald eagles (Haliaeetus leucocephalus) found dead in the Upper Peninsula of Michigan during 2000 were analyzed for the presence of polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and biphenyls (including coplanar PCBs), p,p‘-DDE, and hexachlorobenzene (HCB). Necropsy results showed that the birds suffered from peritonitis, bacterial infection, or trauma. Concentrations of PCDD/DFs in livers ranged from 23 to 4500 pg/g on a wet weight basis (wet wt), whereas the least concentrations were found in blood plasma of bald eagle nestlings (2.3−49 pg/g, wet wt). A maximum total PCB concentration of 280000 ng/g, wet wt, was found in the liver of a dead bald eagle affected by peritonitis. The greatest concentrations of p,p‘-DDE and HCB in eagle livers were 17000 and 120 ng/g, wet wt, respectively. Eagles with elevated 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) or total PCB concentra tions tended to have great TCDD/TCDF or PCB126/PCB77 ratios, hypothesized to be due to induction of cytochrome P450 enzymes and subsequent metabolism of TCDF and PCB77. Concentrations of TCDD toxic equivalents (TEQs) in the tissues of bald eagles exceeded the thresholds for toxicity in a few avian species. Non-ortho coplanar PCBs accounted for 68−88% of the total TEQs in bald eagle tissues. PCDDs and PCDFs collectively accounted for, on average, 17% of the total TEQs. 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Psychology</topic><topic>Insecticides - analysis</topic><topic>Insecticides - pharmacokinetics</topic><topic>Michigan</topic><topic>PCB</topic><topic>Polychlorinated biphenyls</topic><topic>Polychlorinated Biphenyls - analysis</topic><topic>Polychlorinated Biphenyls - pharmacokinetics</topic><topic>Polychlorinated Dibenzodioxins - analogs &amp; derivatives</topic><topic>Polychlorinated Dibenzodioxins - analysis</topic><topic>Polychlorinated Dibenzodioxins - pharmacokinetics</topic><topic>Raptors</topic><topic>Soil Pollutants - analysis</topic><topic>Soil Pollutants - pharmacokinetics</topic><topic>Tissue Distribution</topic><topic>Wildfowl</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Senthil Kumar, Kurunthachalam</creatorcontrib><creatorcontrib>Kannan, Kurunthachalam</creatorcontrib><creatorcontrib>Giesy, John P</creatorcontrib><creatorcontrib>Masunaga, Shigeki</creatorcontrib><collection>Istex</collection><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Biotechnology Research Abstracts</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Toxicology Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Environment Abstracts</collection><collection>Pollution Abstracts</collection><jtitle>Environmental science &amp; technology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Senthil Kumar, Kurunthachalam</au><au>Kannan, Kurunthachalam</au><au>Giesy, John P</au><au>Masunaga, Shigeki</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Distribution and Elimination of Polychlorinated Dibenzo-p-dioxins, Dibenzofurans, Biphenyls, and p,p‘-DDE in Tissues of Bald Eagles from the Upper Peninsula of Michigan</atitle><jtitle>Environmental science &amp; technology</jtitle><addtitle>Environ. Sci. Technol</addtitle><date>2002-07-01</date><risdate>2002</risdate><volume>36</volume><issue>13</issue><spage>2789</spage><epage>2796</epage><pages>2789-2796</pages><issn>0013-936X</issn><eissn>1520-5851</eissn><coden>ESTHAG</coden><abstract>Liver, muscle, fat, kidney, and gall bladder of eight bald eagles (Haliaeetus leucocephalus) found dead in the Upper Peninsula of Michigan during 2000 were analyzed for the presence of polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and biphenyls (including coplanar PCBs), p,p‘-DDE, and hexachlorobenzene (HCB). Necropsy results showed that the birds suffered from peritonitis, bacterial infection, or trauma. Concentrations of PCDD/DFs in livers ranged from 23 to 4500 pg/g on a wet weight basis (wet wt), whereas the least concentrations were found in blood plasma of bald eagle nestlings (2.3−49 pg/g, wet wt). A maximum total PCB concentration of 280000 ng/g, wet wt, was found in the liver of a dead bald eagle affected by peritonitis. The greatest concentrations of p,p‘-DDE and HCB in eagle livers were 17000 and 120 ng/g, wet wt, respectively. Eagles with elevated 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) or total PCB concentra tions tended to have great TCDD/TCDF or PCB126/PCB77 ratios, hypothesized to be due to induction of cytochrome P450 enzymes and subsequent metabolism of TCDF and PCB77. Concentrations of TCDD toxic equivalents (TEQs) in the tissues of bald eagles exceeded the thresholds for toxicity in a few avian species. Non-ortho coplanar PCBs accounted for 68−88% of the total TEQs in bald eagle tissues. PCDDs and PCDFs collectively accounted for, on average, 17% of the total TEQs. On the basis of the analysis of a single gall bladder with bile, biliary excretion rates of PCDDs, PCDFs, and PCBs were estimated as 0.015−0.02% per day.</abstract><cop>Washington, DC</cop><pub>American Chemical Society</pub><pmid>12144248</pmid><doi>10.1021/es0114660</doi><tpages>8</tpages></addata></record>
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subjects Animal, plant and microbial ecology
Animals
Applied ecology
Aves
Benzofurans - analysis
Benzofurans - pharmacokinetics
Biological and medical sciences
Chemicals
Contamination
Cytochrome P-450 Enzyme System - pharmacology
Dibenzofurans, Polychlorinated
Dichlorodiphenyl Dichloroethylene - analysis
Dichlorodiphenyl Dichloroethylene - pharmacokinetics
Dioxins
Ecotoxicology, biological effects of pollution
Effects of pollution and side effects of pesticides on vertebrates
Environmental Monitoring
Environmental Pollutants - analysis
Environmental Pollutants - pharmacokinetics
Fundamental and applied biological sciences. Psychology
Insecticides - analysis
Insecticides - pharmacokinetics
Michigan
PCB
Polychlorinated biphenyls
Polychlorinated Biphenyls - analysis
Polychlorinated Biphenyls - pharmacokinetics
Polychlorinated Dibenzodioxins - analogs & derivatives
Polychlorinated Dibenzodioxins - analysis
Polychlorinated Dibenzodioxins - pharmacokinetics
Raptors
Soil Pollutants - analysis
Soil Pollutants - pharmacokinetics
Tissue Distribution
Wildfowl
title Distribution and Elimination of Polychlorinated Dibenzo-p-dioxins, Dibenzofurans, Biphenyls, and p,p‘-DDE in Tissues of Bald Eagles from the Upper Peninsula of Michigan
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