AustralieFrV1, PascalFrancis, Checkpoint, bibRecord, 001076

Growth and condition indices of juvenile turbot, Scophthalmus maximus, exposed to contaminated sediments: Effects of metallic and organic compounds

Identifieur interne : 001076 ( PascalFrancis/Checkpoint ); précédent : 001075; suivant : 001077

Growth and condition indices of juvenile turbot, Scophthalmus maximus, exposed to contaminated sediments: Effects of metallic and organic compounds

Auteurs : E. Kerambrun [France] ; F. Henry [France] ; P. Perrichon [France] ; L. Courcot [France] ; T. Meziane [France] ; N. Spilmont [France, Australie] ; R. Amara [France]

Source :

Aquatic toxicology [ 0166-445X ] ; 2012.

RBID : Pascal:12-0142709

Descripteurs français

Pascal (Inist)
- Croissance, Indice condition, Sédiment, Composé organique, Essai biologique, Contamination chimique, DNA, Lipide, Milieu aquatique, Ecotoxicologie, Milieu marin, Toxicité, Scophthalmus maximus.
Wicri :
- topic : Milieu aquatique, Milieu marin.

English descriptors

KwdEn :
- Aquatic environment, Bioassay, Chemical contamination, Condition index, DNA, Ecotoxicology, Growth, Lipids, Marine environment, Organic compounds, Scophthalmus maximus, Sediments, Toxicity.

Abstract

Since sediments have the potential to form associations with several classes of pollutants, they have been recognized as a possible and significant source of contamination for the benthic environment. Flat-fish maintain a close association with sediments for food and cover, and are therefore more likely to be exposed to contaminated sediments, especially in coastal areas (e.g. nursery grounds). The assessment of these potential biological effects involves the use of adapted biomonitoring tools. The main objective of this study was to assess and compare the response of several physiological biomarkers measured on juvenile turbot (Scophthalmus maximus) exposed to contaminated sediments. Sediments were collected from three stations in a harbour in northern France (Boulogne-sur-Mer), in an anthropogenic French estuary (the Seine), and in a reference site (exposed sandy beach of Wimereux). Unexposed lab-reared juvenile turbots were exposed to sediments for 7 and 21 days in laboratory conditions. Sediments were analysed for metals, PAH and PCB contamination. Several fish growth and condition indices were individually analysed in fish according to the chemical contaminant availability in sediment, the metal concentrations in gills and the estimation of PAH metabolites in their bile. Significant decreases in growth rates, morphometric index, RNA:DNA ratio and the lipid storage index, based on the ratio of the quantity of triacylglycerols on sterols (TAG:ST), were observed with increasing level of chemical contamination. This decrease in the fish's physiological status could be related to the significant increase of several metal concentrations in contaminated fish gills and the significant increase of PAH metabolites in bile. In a field situation, such a reduction in growth and energetic status of juvenile fish could dramatically decrease their over-winter survival in contaminated nursery grounds.

Affiliations:

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Le document en format XML

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<sZ>6 aut.</sZ>
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<country>Australie</country>
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</affiliation>
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<author><name sortKey="Amara, R" sort="Amara, R" uniqKey="Amara R" first="R." last="Amara">R. Amara</name>
<affiliation wicri:level="1"><inist:fA14 i1="01"><s1>Univ Lille Nord de France</s1>
<s3>FRA</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
<sZ>4 aut.</sZ>
<sZ>6 aut.</sZ>
<sZ>7 aut.</sZ>
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<country>France</country>
<wicri:noRegion>Univ Lille Nord de France</wicri:noRegion>
<wicri:noRegion>Univ Lille Nord de France</wicri:noRegion>
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<affiliation wicri:level="1"><inist:fA14 i1="02"><s1>ULCO, LOG</s1>
<s2>62930 Wimereux</s2>
<s3>FRA</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
<sZ>4 aut.</sZ>
<sZ>7 aut.</sZ>
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<country>France</country>
<wicri:noRegion>62930 Wimereux</wicri:noRegion>
<wicri:noRegion>LOG</wicri:noRegion>
<wicri:noRegion>62930 Wimereux</wicri:noRegion>
</affiliation>
<affiliation wicri:level="1"><inist:fA14 i1="03"><s1>CNRS, UMR 8187</s1>
<s2>62930 Wimereux</s2>
<s3>FRA</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
<sZ>4 aut.</sZ>
<sZ>6 aut.</sZ>
<sZ>7 aut.</sZ>
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<country>France</country>
<wicri:noRegion>62930 Wimereux</wicri:noRegion>
<wicri:noRegion>UMR 8187</wicri:noRegion>
<wicri:noRegion>62930 Wimereux</wicri:noRegion>
</affiliation>
</author>
</analytic>
<series><title level="j" type="main">Aquatic toxicology</title>
<title level="j" type="abbreviated">Aquat. toxicol.</title>
<idno type="ISSN">0166-445X</idno>
<imprint><date when="2012">2012</date>
</imprint>
</series>
</biblStruct>
</sourceDesc>
<seriesStmt><title level="j" type="main">Aquatic toxicology</title>
<title level="j" type="abbreviated">Aquat. toxicol.</title>
<idno type="ISSN">0166-445X</idno>
</seriesStmt>
</fileDesc>
<profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Aquatic environment</term>
<term>Bioassay</term>
<term>Chemical contamination</term>
<term>Condition index</term>
<term>DNA</term>
<term>Ecotoxicology</term>
<term>Growth</term>
<term>Lipids</term>
<term>Marine environment</term>
<term>Organic compounds</term>
<term>Scophthalmus maximus</term>
<term>Sediments</term>
<term>Toxicity</term>
</keywords>
<keywords scheme="Pascal" xml:lang="fr"><term>Croissance</term>
<term>Indice condition</term>
<term>Sédiment</term>
<term>Composé organique</term>
<term>Essai biologique</term>
<term>Contamination chimique</term>
<term>DNA</term>
<term>Lipide</term>
<term>Milieu aquatique</term>
<term>Ecotoxicologie</term>
<term>Milieu marin</term>
<term>Toxicité</term>
<term>Scophthalmus maximus</term>
</keywords>
<keywords scheme="Wicri" type="topic" xml:lang="fr"><term>Milieu aquatique</term>
<term>Milieu marin</term>
</keywords>
</textClass>
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</teiHeader>
<front><div type="abstract" xml:lang="en">Since sediments have the potential to form associations with several classes of pollutants, they have been recognized as a possible and significant source of contamination for the benthic environment. Flat-fish maintain a close association with sediments for food and cover, and are therefore more likely to be exposed to contaminated sediments, especially in coastal areas (e.g. nursery grounds). The assessment of these potential biological effects involves the use of adapted biomonitoring tools. The main objective of this study was to assess and compare the response of several physiological biomarkers measured on juvenile turbot (Scophthalmus maximus) exposed to contaminated sediments. Sediments were collected from three stations in a harbour in northern France (Boulogne-sur-Mer), in an anthropogenic French estuary (the Seine), and in a reference site (exposed sandy beach of Wimereux). Unexposed lab-reared juvenile turbots were exposed to sediments for 7 and 21 days in laboratory conditions. Sediments were analysed for metals, PAH and PCB contamination. Several fish growth and condition indices were individually analysed in fish according to the chemical contaminant availability in sediment, the metal concentrations in gills and the estimation of PAH metabolites in their bile. Significant decreases in growth rates, morphometric index, RNA:DNA ratio and the lipid storage index, based on the ratio of the quantity of triacylglycerols on sterols (TAG:ST), were observed with increasing level of chemical contamination. This decrease in the fish's physiological status could be related to the significant increase of several metal concentrations in contaminated fish gills and the significant increase of PAH metabolites in bile. In a field situation, such a reduction in growth and energetic status of juvenile fish could dramatically decrease their over-winter survival in contaminated nursery grounds.</div>
</front>
</TEI>
<inist><standard h6="B"><pA><fA01 i1="01" i2="1"><s0>0166-445X</s0>
</fA01>
<fA02 i1="01"><s0>AQTODG</s0>
</fA02>
<fA03 i2="1"><s0>Aquat. toxicol.</s0>
</fA03>
<fA05><s2>108</s2>
</fA05>
<fA08 i1="01" i2="1" l="ENG"><s1>Growth and condition indices of juvenile turbot, Scophthalmus maximus, exposed to contaminated sediments: Effects of metallic and organic compounds</s1>
</fA08>
<fA09 i1="01" i2="1" l="ENG"><s1>Proceedings from the 16th International Symposium on Pollutant Responses in Marine Organisms (PRIMO 16)</s1>
</fA09>
<fA11 i1="01" i2="1"><s1>KERAMBRUN (E.)</s1>
</fA11>
<fA11 i1="02" i2="1"><s1>HENRY (F.)</s1>
</fA11>
<fA11 i1="03" i2="1"><s1>PERRICHON (P.)</s1>
</fA11>
<fA11 i1="04" i2="1"><s1>COURCOT (L.)</s1>
</fA11>
<fA11 i1="05" i2="1"><s1>MEZIANE (T.)</s1>
</fA11>
<fA11 i1="06" i2="1"><s1>SPILMONT (N.)</s1>
</fA11>
<fA11 i1="07" i2="1"><s1>AMARA (R.)</s1>
</fA11>
<fA12 i1="01" i2="1"><s1>BAINY (Afonso)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="02" i2="1"><s1>AKCHA (Farida)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="03" i2="1"><s1>ARWKWE (Augustine)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="04" i2="1"><s1>BAIN (Lisa)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="05" i2="1"><s1>JOAO BEBIANNO (Maria)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="06" i2="1"><s1>CELANDER (Malin)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="07" i2="1"><s1>KING MING CHAN</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="08" i2="1"><s1>CHIPMAN (Kevin)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="09" i2="1"><s1>DENSLOW (Nancy)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="10" i2="1"><s1>DI GIULIO (Richard)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="11" i2="1"><s1>FENT (Karl)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="12" i2="1"><s1>FÖRLIN (Lars)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="13" i2="1"><s1>GALLAGHER (Evan)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="14" i2="1"><s1>GOLD-BOUCHOT (Gerardo)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="15" i2="1"><s1>GOKSOYR (Anders)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="16" i2="1"><s1>HINTON (David)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="17" i2="1"><s1>HOOK (Sharon)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="18" i2="1"><s1>IWATA (Hisato)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="19" i2="1"><s1>O.JAMES (Margaret)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="20" i2="1"><s1>LEBLANC (Gerald)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="21" i2="1"><s1>LEE (Jae-Seong)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="22" i2="1"><s1>MINIER (Christophe)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="23" i2="1"><s1>NICHOLS (John)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="24" i2="1"><s1>PORTE (Cinta)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="25" i2="1"><s1>REGOLI (Francesco)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="26" i2="1"><s1>RINGWOOD (Amy H.)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="27" i2="1"><s1>RONIS (Martin)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="28" i2="1"><s1>SEGNER (Helmut)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="29" i2="1"><s1>SCHULTZ (Irv)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="30" i2="1"><s1>STEGEMAN (John)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="31" i2="1"><s1>THOMAS (Peter)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="32" i2="1"><s1>TILLET (Don)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="33" i2="1"><s1>TOLLEFSON (Knut-Erik)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="34" i2="1"><s1>VAN BENEDEN (Rebecca)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="35" i2="1"><s1>VAN DER KRAAK (Glen)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="36" i2="1"><s1>VAN DER OOST (Ron)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="37" i2="1"><s1>WALDOCK (Mic)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="38" i2="1"><s1>SCHLENK (Daniel)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="39" i2="1"><s1>MASON (Zed)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="40" i2="1"><s1>KELLEY (Kevin)</s1>
<s9>ed.</s9>
</fA12>
<fA14 i1="01"><s1>Univ Lille Nord de France</s1>
<s3>FRA</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
<sZ>4 aut.</sZ>
<sZ>6 aut.</sZ>
<sZ>7 aut.</sZ>
</fA14>
<fA14 i1="02"><s1>ULCO, LOG</s1>
<s2>62930 Wimereux</s2>
<s3>FRA</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
<sZ>4 aut.</sZ>
<sZ>7 aut.</sZ>
</fA14>
<fA14 i1="03"><s1>CNRS, UMR 8187</s1>
<s2>62930 Wimereux</s2>
<s3>FRA</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
<sZ>4 aut.</sZ>
<sZ>6 aut.</sZ>
<sZ>7 aut.</sZ>
</fA14>
<fA14 i1="04"><s1>IFREMER</s1>
<s2>17137 L'Houmeau</s2>
<s3>FRA</s3>
<sZ>3 aut.</sZ>
</fA14>
<fA14 i1="05"><s1>UMR-CNRS 5178, Biologie des Organismes Marins et Ecosystemes Departement Milieux et Peuplements Aquatiques, MNHN</s1>
<s2>75231 Paris</s2>
<s3>FRA</s3>
<sZ>5 aut.</sZ>
</fA14>
<fA14 i1="06"><s1>USTL, LOG</s1>
<s2>62930 Wimereux</s2>
<s3>FRA</s3>
<sZ>6 aut.</sZ>
</fA14>
<fA14 i1="07"><s1>Environmental Futures Centre, Griffith University, Gold Coast Campus</s1>
<s2>QLD 4222</s2>
<s3>AUS</s3>
<sZ>6 aut.</sZ>
</fA14>
<fA15 i1="01"><s1>University of California</s1>
<s2>Riverside</s2>
<s3>USA</s3>
<sZ>38 aut.</sZ>
</fA15>
<fA15 i1="02"><s1>California State University of Long Beach</s1>
<s3>USA</s3>
<sZ>39 aut.</sZ>
<sZ>40 aut.</sZ>
</fA15>
<fA20><s1>130-140</s1>
</fA20>
<fA21><s1>2012</s1>
</fA21>
<fA23 i1="01"><s0>ENG</s0>
</fA23>
<fA43 i1="01"><s1>INIST</s1>
<s2>18841</s2>
<s5>354000502842400160</s5>
</fA43>
<fA44><s0>0000</s0>
<s1>© 2012 INIST-CNRS. All rights reserved.</s1>
</fA44>
<fA45><s0>1 p.1/4</s0>
</fA45>
<fA47 i1="01" i2="1"><s0>12-0142709</s0>
</fA47>
<fA60><s1>P</s1>
<s2>C</s2>
</fA60>
<fA61><s0>A</s0>
</fA61>
<fA64 i1="01" i2="1"><s0>Aquatic toxicology</s0>
</fA64>
<fA66 i1="01"><s0>NLD</s0>
</fA66>
<fC01 i1="01" l="ENG"><s0>Since sediments have the potential to form associations with several classes of pollutants, they have been recognized as a possible and significant source of contamination for the benthic environment. Flat-fish maintain a close association with sediments for food and cover, and are therefore more likely to be exposed to contaminated sediments, especially in coastal areas (e.g. nursery grounds). The assessment of these potential biological effects involves the use of adapted biomonitoring tools. The main objective of this study was to assess and compare the response of several physiological biomarkers measured on juvenile turbot (Scophthalmus maximus) exposed to contaminated sediments. Sediments were collected from three stations in a harbour in northern France (Boulogne-sur-Mer), in an anthropogenic French estuary (the Seine), and in a reference site (exposed sandy beach of Wimereux). Unexposed lab-reared juvenile turbots were exposed to sediments for 7 and 21 days in laboratory conditions. Sediments were analysed for metals, PAH and PCB contamination. Several fish growth and condition indices were individually analysed in fish according to the chemical contaminant availability in sediment, the metal concentrations in gills and the estimation of PAH metabolites in their bile. Significant decreases in growth rates, morphometric index, RNA:DNA ratio and the lipid storage index, based on the ratio of the quantity of triacylglycerols on sterols (TAG:ST), were observed with increasing level of chemical contamination. This decrease in the fish's physiological status could be related to the significant increase of several metal concentrations in contaminated fish gills and the significant increase of PAH metabolites in bile. In a field situation, such a reduction in growth and energetic status of juvenile fish could dramatically decrease their over-winter survival in contaminated nursery grounds.</s0>
</fC01>
<fC02 i1="01" i2="X"><s0>002A14D05A</s0>
</fC02>
<fC02 i1="02" i2="X"><s0>002A14B04E</s0>
</fC02>
<fC03 i1="01" i2="X" l="FRE"><s0>Croissance</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG"><s0>Growth</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="SPA"><s0>Crecimiento</s0>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE"><s0>Indice condition</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="ENG"><s0>Condition index</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="SPA"><s0>Indice condición</s0>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE"><s0>Sédiment</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG"><s0>Sediments</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA"><s0>Sedimento</s0>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE"><s0>Composé organique</s0>
<s2>NA</s2>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG"><s0>Organic compounds</s0>
<s2>NA</s2>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA"><s0>Compuesto orgánico</s0>
<s2>NA</s2>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE"><s0>Essai biologique</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG"><s0>Bioassay</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA"><s0>Prueba biológica</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE"><s0>Contamination chimique</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG"><s0>Chemical contamination</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA"><s0>Contaminación química</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE"><s0>DNA</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG"><s0>DNA</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA"><s0>DNA</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE"><s0>Lipide</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG"><s0>Lipids</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA"><s0>Lípido</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE"><s0>Milieu aquatique</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG"><s0>Aquatic environment</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA"><s0>Medio acuático</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE"><s0>Ecotoxicologie</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG"><s0>Ecotoxicology</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA"><s0>Ecotoxicología</s0>
<s5>10</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE"><s0>Milieu marin</s0>
<s5>23</s5>
</fC03>
<fC03 i1="11" i2="X" l="ENG"><s0>Marine environment</s0>
<s5>23</s5>
</fC03>
<fC03 i1="11" i2="X" l="SPA"><s0>Medio marino</s0>
<s5>23</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE"><s0>Toxicité</s0>
<s5>24</s5>
</fC03>
<fC03 i1="12" i2="X" l="ENG"><s0>Toxicity</s0>
<s5>24</s5>
</fC03>
<fC03 i1="12" i2="X" l="SPA"><s0>Toxicidad</s0>
<s5>24</s5>
</fC03>
<fC03 i1="13" i2="X" l="FRE"><s0>Scophthalmus maximus</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03>
<fC03 i1="13" i2="X" l="ENG"><s0>Scophthalmus maximus</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03>
<fC03 i1="13" i2="X" l="SPA"><s0>Scophthalmus maximus</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE"><s0>Pisces</s0>
<s2>NS</s2>
<s5>29</s5>
</fC07>
<fC07 i1="01" i2="X" l="ENG"><s0>Pisces</s0>
<s2>NS</s2>
<s5>29</s5>
</fC07>
<fC07 i1="01" i2="X" l="SPA"><s0>Pisces</s0>
<s2>NS</s2>
<s5>29</s5>
</fC07>
<fC07 i1="02" i2="X" l="FRE"><s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="ENG"><s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="SPA"><s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="FRE"><s0>Scophthalmidae</s0>
<s4>INC</s4>
<s5>70</s5>
</fC07>
<fN21><s1>107</s1>
</fN21>
<fN44 i1="01"><s1>OTO</s1>
</fN44>
<fN82><s1>OTO</s1>
</fN82>
</pA>
<pR><fA30 i1="01" i2="1" l="ENG"><s1>PRIMO 16 International Symposium on Pollutant Responses in Marine Organisms</s1>
<s2>16</s2>
<s3>Long Beach, CA USA</s3>
<s4>2011-05-15</s4>
</fA30>
</pR>
</standard>
</inist>
<affiliations><list><country><li>Australie</li>
<li>France</li>
</country>
<region><li>Île-de-France</li>
</region>
<settlement><li>Paris</li>
</settlement>
</list>
<tree><country name="France"><noRegion><name sortKey="Kerambrun, E" sort="Kerambrun, E" uniqKey="Kerambrun E" first="E." last="Kerambrun">E. Kerambrun</name>
</noRegion>
<name sortKey="Amara, R" sort="Amara, R" uniqKey="Amara R" first="R." last="Amara">R. Amara</name>
<name sortKey="Amara, R" sort="Amara, R" uniqKey="Amara R" first="R." last="Amara">R. Amara</name>
<name sortKey="Amara, R" sort="Amara, R" uniqKey="Amara R" first="R." last="Amara">R. Amara</name>
<name sortKey="Courcot, L" sort="Courcot, L" uniqKey="Courcot L" first="L." last="Courcot">L. Courcot</name>
<name sortKey="Courcot, L" sort="Courcot, L" uniqKey="Courcot L" first="L." last="Courcot">L. Courcot</name>
<name sortKey="Courcot, L" sort="Courcot, L" uniqKey="Courcot L" first="L." last="Courcot">L. Courcot</name>
<name sortKey="Henry, F" sort="Henry, F" uniqKey="Henry F" first="F." last="Henry">F. Henry</name>
<name sortKey="Henry, F" sort="Henry, F" uniqKey="Henry F" first="F." last="Henry">F. Henry</name>
<name sortKey="Henry, F" sort="Henry, F" uniqKey="Henry F" first="F." last="Henry">F. Henry</name>
<name sortKey="Kerambrun, E" sort="Kerambrun, E" uniqKey="Kerambrun E" first="E." last="Kerambrun">E. Kerambrun</name>
<name sortKey="Kerambrun, E" sort="Kerambrun, E" uniqKey="Kerambrun E" first="E." last="Kerambrun">E. Kerambrun</name>
<name sortKey="Meziane, T" sort="Meziane, T" uniqKey="Meziane T" first="T." last="Meziane">T. Meziane</name>
<name sortKey="Perrichon, P" sort="Perrichon, P" uniqKey="Perrichon P" first="P." last="Perrichon">P. Perrichon</name>
<name sortKey="Spilmont, N" sort="Spilmont, N" uniqKey="Spilmont N" first="N." last="Spilmont">N. Spilmont</name>
<name sortKey="Spilmont, N" sort="Spilmont, N" uniqKey="Spilmont N" first="N." last="Spilmont">N. Spilmont</name>
<name sortKey="Spilmont, N" sort="Spilmont, N" uniqKey="Spilmont N" first="N." last="Spilmont">N. Spilmont</name>
</country>
<country name="Australie"><noRegion><name sortKey="Spilmont, N" sort="Spilmont, N" uniqKey="Spilmont N" first="N." last="Spilmont">N. Spilmont</name>
</noRegion>
</country>
</tree>
</affiliations>
</record>

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	Serveur d'exploration sur les relations entre la France et l'Australie
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Growth and condition indices of juvenile turbot, Scophthalmus maximus, exposed to contaminated sediments: Effects of metallic and organic compounds

Growth and condition indices of juvenile turbot, Scophthalmus maximus, exposed to contaminated sediments: Effects of metallic and organic compounds

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