Concentrations of polychlorinated dibenzo- p -dioxins and furans in fish downstream from a Ky-5 manufacturing
Identifieur interne : 000B73 ( Main/Exploration ); précédent : 000B72; suivant : 000B74Concentrations of polychlorinated dibenzo- p -dioxins and furans in fish downstream from a Ky-5 manufacturing
Auteurs : Markku Korhonen [États-Unis, Finlande] ; Matti Verta [Finlande] ; Jouni Lehtoranta [Finlande] ; Hannu Kiviranta [Finlande] ; Terttu Vartiainen [Finlande]Source :
- Chemosphere [ 0045-6535 ] ; 2001.
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.
- Pascal (Inist)
- Accumulation biologique, Agent préservation bois, Animaux, Biodisponibilité, Chaine alimentaire, Contamination des aliments, Cours eau, Dibenzofurane(polychloro), Dioxine dérivé, Distribution tissulaire, Effluent, Faune, Humains, Industrie, Pisces, Poissons, Polluant, Pollution eau, Santé publique, Usine chimique, Écosystème.
- Wicri :
English descriptors
- KwdEn :
- Animals (MeSH), Benzofurans (analysis), Benzofurans (pharmacokinetics), Biological Availability (MeSH), Biological accumulation, Chemical plant, Dioxin derivatives, Ecosystem (MeSH), Effluent, Fauna, Fishes (MeSH), Food Chain (MeSH), Food Contamination (MeSH), Humans (MeSH), Industry (MeSH), Liver (chemistry), Pisces, Pollutant, Public Health (MeSH), Soil Pollutants (analysis), Soil Pollutants (pharmacokinetics), Stream, Tetrachlorodibenzodioxin (administration & dosage), Tetrachlorodibenzodioxin (analogs & derivatives), Tetrachlorodibenzodioxin (pharmacokinetics), Tissue Distribution (MeSH), Water Pollutants, Chemical (analysis), Water Pollutants, Chemical (pharmacokinetics), Water pollution, Wood preservative.
- 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 upstream 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).
Url:
DOI: 10.1016/S0045-6535(00)00410-0
Affiliations:
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Box 140, FIN-00251 Helsinki</wicri:regionArea><wicri:noRegion>FIN-00251 Helsinki</wicri:noRegion></affiliation></author><author><name sortKey="Verta, Matti" sort="Verta, Matti" uniqKey="Verta M" first="Matti" last="Verta">Matti Verta</name><affiliation wicri:level="1"><country xml:lang="fr">Finlande</country><wicri:regionArea>Finnish Environment Institute, Impacts Research Division, P.O. Box 140, FIN-00251 Helsinki</wicri:regionArea><wicri:noRegion>FIN-00251 Helsinki</wicri:noRegion></affiliation></author><author><name sortKey="Lehtoranta, Jouni" sort="Lehtoranta, Jouni" uniqKey="Lehtoranta J" first="Jouni" last="Lehtoranta">Jouni Lehtoranta</name><affiliation wicri:level="1"><country xml:lang="fr">Finlande</country><wicri:regionArea>Finnish Environment Institute, Impacts Research Division, P.O. Box 140, FIN-00251 Helsinki</wicri:regionArea><wicri:noRegion>FIN-00251 Helsinki</wicri:noRegion></affiliation></author><author><name sortKey="Kiviranta, Hannu" sort="Kiviranta, Hannu" uniqKey="Kiviranta H" first="Hannu" last="Kiviranta">Hannu Kiviranta</name><affiliation wicri:level="1"><country xml:lang="fr">Finlande</country><wicri:regionArea>National Public Health Institute, P.O. Box 95, FIN-70701 Kuopio</wicri:regionArea><wicri:noRegion>FIN-70701 Kuopio</wicri:noRegion></affiliation></author><author><name sortKey="Vartiainen, Terttu" sort="Vartiainen, Terttu" uniqKey="Vartiainen T" first="Terttu" last="Vartiainen">Terttu Vartiainen</name><affiliation wicri:level="1"><country xml:lang="fr">Finlande</country><wicri:regionArea>National Public Health Institute, P.O. 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(pharmacokinetics)</term><term>Biological Availability (MeSH)</term><term>Biological accumulation</term><term>Chemical plant</term><term>Dioxin derivatives</term><term>Ecosystem (MeSH)</term><term>Effluent</term><term>Fauna</term><term>Fishes (MeSH)</term><term>Food Chain (MeSH)</term><term>Food Contamination (MeSH)</term><term>Humans (MeSH)</term><term>Industry (MeSH)</term><term>Liver (chemistry)</term><term>Pisces</term><term>Pollutant</term><term>Public Health (MeSH)</term><term>Soil Pollutants (analysis)</term><term>Soil Pollutants (pharmacokinetics)</term><term>Stream</term><term>Tetrachlorodibenzodioxin (administration & dosage)</term><term>Tetrachlorodibenzodioxin (analogs & derivatives)</term><term>Tetrachlorodibenzodioxin (pharmacokinetics)</term><term>Tissue Distribution (MeSH)</term><term>Water Pollutants, Chemical (analysis)</term><term>Water Pollutants, Chemical (pharmacokinetics)</term><term>Water pollution</term><term>Wood preservative</term></keywords><keywords 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type="chemical" qualifier="analysis" xml:lang="en"><term>Benzofurans</term><term>Soil Pollutants</term><term>Water Pollutants, Chemical</term></keywords><keywords scheme="MESH" type="chemical" qualifier="pharmacokinetics" xml:lang="en"><term>Benzofurans</term><term>Soil Pollutants</term><term>Tetrachlorodibenzodioxin</term><term>Water Pollutants, Chemical</term></keywords><keywords scheme="MESH" qualifier="analyse" xml:lang="fr"><term>Benzofuranes</term><term>Polluants chimiques de l'eau</term><term>Polluants du sol</term></keywords><keywords scheme="MESH" qualifier="chemistry" xml:lang="en"><term>Liver</term></keywords><keywords scheme="MESH" qualifier="composition chimique" xml:lang="fr"><term>Foie</term></keywords><keywords scheme="MESH" qualifier="pharmacocinétique" xml:lang="fr"><term>Benzofuranes</term><term>Polluants chimiques de l'eau</term><term>Polluants du sol</term></keywords><keywords scheme="MESH" xml:lang="en"><term>Animals</term><term>Biological Availability</term><term>Ecosystem</term><term>Fishes</term><term>Food Chain</term><term>Food Contamination</term><term>Humans</term><term>Industry</term><term>Public Health</term><term>Tissue Distribution</term></keywords><keywords scheme="Pascal" xml:lang="fr"><term>Accumulation biologique</term><term>Agent préservation bois</term><term>Animaux</term><term>Biodisponibilité</term><term>Chaine alimentaire</term><term>Contamination des aliments</term><term>Cours eau</term><term>Dibenzofurane(polychloro)</term><term>Dioxine dérivé</term><term>Distribution tissulaire</term><term>Effluent</term><term>Faune</term><term>Humains</term><term>Industrie</term><term>Pisces</term><term>Poissons</term><term>Polluant</term><term>Pollution eau</term><term>Santé publique</term><term>Usine chimique</term><term>Écosystème</term></keywords><keywords scheme="Wicri" type="topic" xml:lang="fr"><term>Faune</term><term>Polluant</term></keywords></textClass><langUsage><language ident="en">en</language></langUsage></profileDesc></teiHeader><front><div type="abstract" xml:lang="en">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 upstream 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).</div></front></TEI><affiliations><list><country><li>Finlande</li><li>États-Unis</li></country></list><tree><country name="États-Unis"><noRegion><name sortKey="Korhonen, Markku" sort="Korhonen, Markku" uniqKey="Korhonen M" first="Markku" last="Korhonen">Markku Korhonen</name></noRegion></country><country name="Finlande"><noRegion><name sortKey="Korhonen, Markku" sort="Korhonen, Markku" uniqKey="Korhonen M" first="Markku" last="Korhonen">Markku Korhonen</name></noRegion><name sortKey="Kiviranta, Hannu" sort="Kiviranta, Hannu" uniqKey="Kiviranta H" first="Hannu" last="Kiviranta">Hannu Kiviranta</name><name sortKey="Lehtoranta, Jouni" sort="Lehtoranta, Jouni" uniqKey="Lehtoranta J" first="Jouni" last="Lehtoranta">Jouni Lehtoranta</name><name sortKey="Vartiainen, Terttu" sort="Vartiainen, Terttu" uniqKey="Vartiainen T" first="Terttu" last="Vartiainen">Terttu Vartiainen</name><name sortKey="Verta, Matti" sort="Verta, Matti" uniqKey="Verta M" first="Matti" last="Verta">Matti Verta</name></country></tree></affiliations></record>Pour manipuler ce document sous Unix (Dilib)
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