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Levels of DDT and hexachlorocyclohexane in burbot (Lota lota L.) from Russian Arctic rivers

Identifieur interne : 000B53 ( Main/Exploration ); précédent : 000B52; suivant : 000B54

Levels of DDT and hexachlorocyclohexane in burbot (Lota lota L.) from Russian Arctic rivers

Auteurs : Alexander V. Zhulidov [Russie] ; Richard D. Robarts [Canada] ; John V. Headley [Canada] ; Karsten Liber [Canada] ; Daniel A. Zhulidov [Russie] ; Olga V. Zhulidova [Russie] ; Dmitry F. Pavlov [Russie]

Source :

RBID : Pascal:02-0432602

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English descriptors

Abstract

The concentrations of organochlorine pesticides (OCPs=p,p'DDT, p,p'DDD, p,p'DDE, α-HCH and γ-HCH) were measured in the sediments, water and burbot (whole liver and liver lipids) of eight Russian Arctic rivers near their outflows to the Arctic Ocean between 1988 and 1994. DDT was not detected in any river sediments above the limit of quantification (LOQ) of 2.5 ng g-1 dry wt. Concentrations of DDD and DDE were only found in three of the river sediments above the LOQ of 0.75 ng g-1 dry wt. DDT and DDE were present in only North Dvina and Pechora river water above the LOQ of 5 ng l-1, while DDD was not found in any river above this limit. Both α- and γ-HCH were found in all river sediments except for the Kolyma River at concentrations up to 2.4 and 3.5 ng g-1 dry wt., respectively. In river water, α-HCH was as high as 8.6 ng l-1 in the Ob River and γ-HCH as high as 7.6 ng l-1 in the Pechora River. The concentration of both ΣDDT and ΣHCH decreased to LOQ levels by about 1992 in both water and sediments. EDDT (up to 70 ng g-1 wet wt.) and ΣHCH (maximum 18 ng g-1 wet wt.) in burbot livers followed a similar temporal trend as in water and sediments. There is a scarcity of OCP data for Russia, but from what is available, we conclude that: (1) contamination of Russian rivers and burbot by OCPs is less severe in the Arctic than at lower latitudes; (2) contamination of Russian Arctic burbot is comparable to, or lower than, similar OCP contamination measured in burbot and other fish in other countries; and (3) the OCP concentrations in Russian burbot pose a negligible health risk to either humans or wildlife.


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<term>Animals (MeSH)</term>
<term>Arctic Region</term>
<term>Arctic Regions (MeSH)</term>
<term>Biological accumulation</term>
<term>DDE</term>
<term>DDT</term>
<term>DDT (analysis)</term>
<term>Degradation product</term>
<term>Environmental Monitoring (MeSH)</term>
<term>Fishes (metabolism)</term>
<term>Fresh Water (analysis)</term>
<term>Geologic Sediments (analysis)</term>
<term>HCH</term>
<term>Humans (MeSH)</term>
<term>Insecticide</term>
<term>Insecticides (analysis)</term>
<term>Lindane (analysis)</term>
<term>Lipids (analysis)</term>
<term>Liver (chemistry)</term>
<term>Lota lota</term>
<term>Persistent organic pollutant</term>
<term>Public health</term>
<term>Risk Assessment (MeSH)</term>
<term>Risk analysis</term>
<term>Russia</term>
<term>Russia (MeSH)</term>
<term>Stream</term>
<term>Water Pollutants, Chemical (analysis)</term>
<term>Water pollution</term>
<term>Xenobiotic</term>
</keywords>
<keywords scheme="KwdFr" xml:lang="fr">
<term>Animaux (MeSH)</term>
<term>Appréciation des risques (MeSH)</term>
<term>DDT (analyse)</term>
<term>Eau douce (analyse)</term>
<term>Foie (composition chimique)</term>
<term>Humains (MeSH)</term>
<term>Insecticides (analyse)</term>
<term>Lipides (analyse)</term>
<term>Poissons (métabolisme)</term>
<term>Polluants chimiques de l'eau (analyse)</term>
<term>Russie (MeSH)</term>
<term>Régions arctiques (MeSH)</term>
<term>Surveillance de l'environnement (MeSH)</term>
<term>Sédiments géologiques (analyse)</term>
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<term>DDT</term>
<term>Insecticides</term>
<term>Lindane</term>
<term>Lipids</term>
<term>Water Pollutants, Chemical</term>
</keywords>
<keywords scheme="MESH" type="geographic" xml:lang="en">
<term>Arctic Regions</term>
<term>Russia</term>
</keywords>
<keywords scheme="MESH" qualifier="analyse" xml:lang="fr">
<term>DDT</term>
<term>Eau douce</term>
<term>Insecticides</term>
<term>Lipides</term>
<term>Polluants chimiques de l'eau</term>
<term>Sédiments géologiques</term>
</keywords>
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<term>Fresh Water</term>
<term>Geologic Sediments</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="metabolism" xml:lang="en">
<term>Fishes</term>
</keywords>
<keywords scheme="MESH" qualifier="métabolisme" xml:lang="fr">
<term>Poissons</term>
</keywords>
<keywords scheme="MESH" xml:lang="en">
<term>Animals</term>
<term>Environmental Monitoring</term>
<term>Humans</term>
<term>Risk Assessment</term>
</keywords>
<keywords scheme="Pascal" xml:lang="fr">
<term>Animaux</term>
<term>Appréciation des risques</term>
<term>Humains</term>
<term>Pollution eau</term>
<term>Russie</term>
<term>Régions arctiques</term>
<term>Surveillance de l'environnement</term>
<term>Xénobiotique</term>
<term>Accumulation biologique</term>
<term>Analyse risque</term>
<term>Santé publique</term>
<term>Cours eau</term>
<term>Arctique</term>
<term>Russie</term>
<term>Produit dégradation</term>
<term>Insecticide</term>
<term>DDT</term>
<term>HCH</term>
<term>DDE</term>
<term>Lota lota</term>
<term>Polluant organique persistant</term>
</keywords>
<keywords scheme="Wicri" type="geographic" xml:lang="fr">
<term>Russie</term>
</keywords>
<keywords scheme="Wicri" type="topic" xml:lang="fr">
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<front>
<div type="abstract" xml:lang="en">The concentrations of organochlorine pesticides (OCPs=p,p'DDT, p,p'DDD, p,p'DDE, α-HCH and γ-HCH) were measured in the sediments, water and burbot (whole liver and liver lipids) of eight Russian Arctic rivers near their outflows to the Arctic Ocean between 1988 and 1994. DDT was not detected in any river sediments above the limit of quantification (LOQ) of 2.5 ng g
<sup>-1</sup>
dry wt. Concentrations of DDD and DDE were only found in three of the river sediments above the LOQ of 0.75 ng g
<sup>-1</sup>
dry wt. DDT and DDE were present in only North Dvina and Pechora river water above the LOQ of 5 ng l
<sup>-1</sup>
, while DDD was not found in any river above this limit. Both α- and γ-HCH were found in all river sediments except for the Kolyma River at concentrations up to 2.4 and 3.5 ng g
<sup>-1</sup>
dry wt., respectively. In river water, α-HCH was as high as 8.6 ng l
<sup>-1</sup>
in the Ob River and γ-HCH as high as 7.6 ng l
<sup>-1</sup>
in the Pechora River. The concentration of both ΣDDT and ΣHCH decreased to LOQ levels by about 1992 in both water and sediments. EDDT (up to 70 ng g
<sup>-1</sup>
wet wt.) and ΣHCH (maximum 18 ng g
<sup>-1</sup>
wet wt.) in burbot livers followed a similar temporal trend as in water and sediments. There is a scarcity of OCP data for Russia, but from what is available, we conclude that: (1) contamination of Russian rivers and burbot by OCPs is less severe in the Arctic than at lower latitudes; (2) contamination of Russian Arctic burbot is comparable to, or lower than, similar OCP contamination measured in burbot and other fish in other countries; and (3) the OCP concentrations in Russian burbot pose a negligible health risk to either humans or wildlife.</div>
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