Concentrations of polychlorinated dibenzo-p-dioxins and furans in fish downstream from a Ky-5 manufacturing.
Identifieur interne : 000144 ( PubMed/Checkpoint ); précédent : 000143; suivant : 000145Concentrations of polychlorinated dibenzo-p-dioxins and furans in fish downstream from a Ky-5 manufacturing.
Auteurs : M. Korhonen [États-Unis] ; M. Verta ; J. Lehtoranta ; H. Kiviranta ; T. VartiainenSource :
- Chemosphere [ 0045-6535 ]
Descripteurs français
- KwdFr :
- Animaux (MeSH), Benzofuranes (analyse), Benzofuranes (pharmacocinétique), Biodisponibilité (MeSH), Chaine alimentaire (MeSH), Contamination des aliments (MeSH), Distribution tissulaire (MeSH), Foie (composition chimique), Humains (MeSH), Industrie (MeSH), Poissons (MeSH), Polluants chimiques de l'eau (analyse), Polluants chimiques de l'eau (pharmacocinétique), Polluants du sol (analyse), Polluants du sol (pharmacocinétique), Santé publique (MeSH), Écosystème (MeSH).
- MESH :
- analyse : Benzofuranes, Polluants chimiques de l'eau, Polluants du sol.
- composition chimique : Foie.
- pharmacocinétique : Benzofuranes, Polluants chimiques de l'eau, Polluants du sol.
- Animaux, Biodisponibilité, Chaine alimentaire, Contamination des aliments, Distribution tissulaire, Humains, Industrie, Poissons, Santé publique, Écosystème.
English descriptors
- KwdEn :
- Animals (MeSH), Benzofurans (analysis), Benzofurans (pharmacokinetics), Biological Availability (MeSH), Ecosystem (MeSH), Fishes (MeSH), Food Chain (MeSH), Food Contamination (MeSH), Humans (MeSH), Industry (MeSH), Liver (chemistry), Public Health (MeSH), Soil Pollutants (analysis), Soil Pollutants (pharmacokinetics), Tetrachlorodibenzodioxin (administration & dosage), Tetrachlorodibenzodioxin (analogs & derivatives), Tetrachlorodibenzodioxin (pharmacokinetics), Tissue Distribution (MeSH), Water Pollutants, Chemical (analysis), Water Pollutants, Chemical (pharmacokinetics).
- MESH :
- chemical , administration & dosage : Tetrachlorodibenzodioxin.
- chemical , analogs & derivatives : Tetrachlorodibenzodioxin.
- chemical , analysis : Benzofurans, Soil Pollutants, Water Pollutants, Chemical.
- chemical , pharmacokinetics : Benzofurans, Soil Pollutants, Tetrachlorodibenzodioxin, Water Pollutants, Chemical.
- chemistry : Liver.
- Animals, Biological Availability, Ecosystem, Fishes, Food Chain, Food Contamination, Humans, Industry, Public Health, Tissue Distribution.
Abstract
Concentrations of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) were studied in seven fish species, burbot (Lota lota), pike (Esox lucius), perch (Perca fluviatilis), pikeperch (Stizopedion lucioperca), bream (Abramis brama), salmon (Salmo salar) and Baltic herring (Clupea harengus membras) in River Kymijoki and its estuary polluted by Ky-5 manufacturing. The fish were caught at 14 localities along the river and its estuary. The selected species represent different trophic levels and/or inhabit different environments. The concentrations of PCDD/Fs were low, in most samples below 1 pg g(-1) ITEQ (NATO/CCMS 1988) fresh weight (fw) in muscle, except salmon and Baltic herring. These two species graze at the open sea and consequently accumulate contaminants at a large area in the Baltic Sea. The lipid content in salmon and Baltic herring was an order of magnitude higher than in other species. PCDD/Fs in fish muscle showed only slightly elevated levels in the Kymijoki area and its estuary as compared to the levels in the same species in Finnish freshwaters and sea areas. The concentration of the main impurities of the fungicide Ky-5 was higher in the Kymijoki River downstream the Ky-5 manufacturing place compared to the up-stream locations. The PCDD/F concentrations in fish liver and spawn were 10-100 times higher than the concentration in muscle, because of the much higher lipid concentrations of these organes. Consequently, the tolerable daily intake values could be as much as 100 times smaller (M. Korhonen, M. Verta, T. Vartiainen, Organohalog. Comp. 32 (1997) 305-310; P. Mikkelson, J. Paasivirta, H. Kiviranta, Organohalog. Comp. 39 (1998) 59-62).
PubMed: 11372842
Affiliations:
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Korhonen</name><affiliation wicri:level="1"><nlm:affiliation>Finnish Environment Institute, Impacts Research Division, Helsinki. markku.korhonen@vyh.edu</nlm:affiliation><country wicri:rule="url">États-Unis</country></affiliation></author><author><name sortKey="Verta, M" sort="Verta, M" uniqKey="Verta M" first="M" last="Verta">M. Verta</name></author><author><name sortKey="Lehtoranta, J" sort="Lehtoranta, J" uniqKey="Lehtoranta J" first="J" last="Lehtoranta">J. Lehtoranta</name></author><author><name sortKey="Kiviranta, H" sort="Kiviranta, H" uniqKey="Kiviranta H" first="H" last="Kiviranta">H. Kiviranta</name></author><author><name sortKey="Vartiainen, T" sort="Vartiainen, T" uniqKey="Vartiainen T" first="T" last="Vartiainen">T. 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The fish were caught at 14 localities along the river and its estuary. The selected species represent different trophic levels and/or inhabit different environments. The concentrations of PCDD/Fs were low, in most samples below 1 pg g(-1) ITEQ (NATO/CCMS 1988) fresh weight (fw) in muscle, except salmon and Baltic herring. These two species graze at the open sea and consequently accumulate contaminants at a large area in the Baltic Sea. The lipid content in salmon and Baltic herring was an order of magnitude higher than in other species. PCDD/Fs in fish muscle showed only slightly elevated levels in the Kymijoki area and its estuary as compared to the levels in the same species in Finnish freshwaters and sea areas. The concentration of the main impurities of the fungicide Ky-5 was higher in the Kymijoki River downstream the Ky-5 manufacturing place compared to the up-stream locations. The PCDD/F concentrations in fish liver and spawn were 10-100 times higher than the concentration in muscle, because of the much higher lipid concentrations of these organes. Consequently, the tolerable daily intake values could be as much as 100 times smaller (M. Korhonen, M. Verta, T. Vartiainen, Organohalog. Comp. 32 (1997) 305-310; P. Mikkelson, J. Paasivirta, H. Kiviranta, Organohalog. 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The fish were caught at 14 localities along the river and its estuary. The selected species represent different trophic levels and/or inhabit different environments. The concentrations of PCDD/Fs were low, in most samples below 1 pg g(-1) ITEQ (NATO/CCMS 1988) fresh weight (fw) in muscle, except salmon and Baltic herring. These two species graze at the open sea and consequently accumulate contaminants at a large area in the Baltic Sea. The lipid content in salmon and Baltic herring was an order of magnitude higher than in other species. PCDD/Fs in fish muscle showed only slightly elevated levels in the Kymijoki area and its estuary as compared to the levels in the same species in Finnish freshwaters and sea areas. The concentration of the main impurities of the fungicide Ky-5 was higher in the Kymijoki River downstream the Ky-5 manufacturing place compared to the up-stream locations. The PCDD/F concentrations in fish liver and spawn were 10-100 times higher than the concentration in muscle, because of the much higher lipid concentrations of these organes. Consequently, the tolerable daily intake values could be as much as 100 times smaller (M. Korhonen, M. Verta, T. Vartiainen, Organohalog. Comp. 32 (1997) 305-310; P. Mikkelson, J. Paasivirta, H. Kiviranta, Organohalog. 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Gov't</PublicationType></PublicationTypeList></Article><MedlineJournalInfo><Country>England</Country><MedlineTA>Chemosphere</MedlineTA><NlmUniqueID>0320657</NlmUniqueID><ISSNLinking>0045-6535</ISSNLinking></MedlineJournalInfo><ChemicalList><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D001572">Benzofurans</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D012989">Soil Pollutants</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D014874">Water Pollutants, Chemical</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="C023386">chlorinated dibenzofurans</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="C008954">polychlorodibenzo-4-dioxin</NameOfSubstance></Chemical><Chemical><RegistryNumber>DO80M48B6O</RegistryNumber><NameOfSubstance UI="D013749">Tetrachlorodibenzodioxin</NameOfSubstance></Chemical></ChemicalList><CitationSubset>IM</CitationSubset><MeshHeadingList><MeshHeading><DescriptorName MajorTopicYN="N" UI="D000818">Animals</DescriptorName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D001572">Benzofurans</DescriptorName><QualifierName MajorTopicYN="N" UI="Q000032">analysis</QualifierName><QualifierName MajorTopicYN="Y" UI="Q000493">pharmacokinetics</QualifierName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D001682">Biological Availability</DescriptorName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D017753">Ecosystem</DescriptorName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="Y" UI="D005399">Fishes</DescriptorName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D020387">Food Chain</DescriptorName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="Y" UI="D005506">Food Contamination</DescriptorName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D006801">Humans</DescriptorName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D007221">Industry</DescriptorName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D008099">Liver</DescriptorName><QualifierName MajorTopicYN="N" UI="Q000737">chemistry</QualifierName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D011634">Public Health</DescriptorName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D012989">Soil Pollutants</DescriptorName><QualifierName MajorTopicYN="N" UI="Q000032">analysis</QualifierName><QualifierName MajorTopicYN="Y" UI="Q000493">pharmacokinetics</QualifierName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D013749">Tetrachlorodibenzodioxin</DescriptorName><QualifierName MajorTopicYN="N" UI="Q000008">administration & dosage</QualifierName><QualifierName MajorTopicYN="N" UI="Q000031">analogs & derivatives</QualifierName><QualifierName MajorTopicYN="Y" UI="Q000493">pharmacokinetics</QualifierName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D014018">Tissue Distribution</DescriptorName></MeshHeading><MeshHeading><DescriptorName MajorTopicYN="N" UI="D014874">Water Pollutants, Chemical</DescriptorName><QualifierName MajorTopicYN="N" UI="Q000032">analysis</QualifierName><QualifierName MajorTopicYN="Y" UI="Q000493">pharmacokinetics</QualifierName></MeshHeading></MeshHeadingList></MedlineCitation><PubmedData><History><PubMedPubDate PubStatus="pubmed"><Year>2001</Year><Month>5</Month><Day>25</Day><Hour>10</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="medline"><Year>2001</Year><Month>9</Month><Day>28</Day><Hour>10</Hour><Minute>1</Minute></PubMedPubDate><PubMedPubDate PubStatus="entrez"><Year>2001</Year><Month>5</Month><Day>25</Day><Hour>10</Hour><Minute>0</Minute></PubMedPubDate></History><PublicationStatus>ppublish</PublicationStatus><ArticleIdList><ArticleId IdType="pubmed">11372842</ArticleId><ArticleId IdType="pii">S0045-6535(00)00410-0</ArticleId></ArticleIdList></PubmedData></pubmed><affiliations><list><country><li>États-Unis</li></country></list><tree><noCountry><name sortKey="Kiviranta, H" sort="Kiviranta, H" uniqKey="Kiviranta H" first="H" last="Kiviranta">H. Kiviranta</name><name sortKey="Lehtoranta, J" sort="Lehtoranta, J" uniqKey="Lehtoranta J" first="J" last="Lehtoranta">J. Lehtoranta</name><name sortKey="Vartiainen, T" sort="Vartiainen, T" uniqKey="Vartiainen T" first="T" last="Vartiainen">T. Vartiainen</name><name sortKey="Verta, M" sort="Verta, M" uniqKey="Verta M" first="M" last="Verta">M. Verta</name></noCountry><country name="États-Unis"><noRegion><name sortKey="Korhonen, M" sort="Korhonen, M" uniqKey="Korhonen M" first="M" last="Korhonen">M. Korhonen</name></noRegion></country></tree></affiliations></record>Pour manipuler ce document sous Unix (Dilib)
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