Serveur d'exploration sur l'esturgeon

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Effects of dietary methylmercury on growth performance and tissue burden in juvenile green (Acipenser medirostris) and white sturgeon (A. transmontanus)

Identifieur interne : 000301 ( PascalFrancis/Curation ); précédent : 000300; suivant : 000302

Effects of dietary methylmercury on growth performance and tissue burden in juvenile green (Acipenser medirostris) and white sturgeon (A. transmontanus)

Auteurs : Jang-Won Lee [États-Unis] ; Nicola De Riu [États-Unis, Italie] ; Seunghyung Lee [États-Unis] ; Sungchul C. Bai [Corée du Sud] ; Giuseppe Moniello [Italie] ; Silas S. O. Hung [États-Unis]

Source :

RBID : Pascal:12-0016619

Descripteurs français

English descriptors

Abstract

Triplicate groups of juvenile green and white sturgeon (30 ± 2 g) were exposed to one of the four nominal concentrations of dietary methylmercury (MeHg, 0 (control), 25, 50, and 100 mg MeHg/kg diet) for 8 weeks to determine and compare the effects on growth performance and mercury (Hg) tissue burden in the two sturgeon species. Mortality, growth performance as measured by percent body weight increase per day, hepatosomatic index, proximate composition of whole body, and Hg burden in the whole body, gill, heart, liver, kidney, and white muscle were determined to assess the adverse growth effects and bioaccumulation of dietary MeHg in sturgeon. Significantly higher mortality and lower growth rate (p < 0.05) were noted in green and white sturgeon fed the MeHg diets compared to the controls. Green sturgeon fed the MeHg diets exhibited earlier and more severe adverse effects compared to white sturgeon. Mercury accumulated in all tissues in a dose-dependent manner regardless of species, and the highest Hg concentrations were found in the kidneys of both species. Dietary MeHg had no significant effect (p > 0.05) on the whole body proximate compositions of either sturgeon species. In conclusion, green sturgeon was more susceptible to dietary MeHg toxicity than white sturgeon in our 8-week growth experiment based on the higher mortality and lower growth rate and body energy contents.
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A11 01  1    @1 LEE (Jang-Won)
A11 02  1    @1 DE RIU (Nicola)
A11 03  1    @1 LEE (Seunghyung)
A11 04  1    @1 BAI (Sungchul C.)
A11 05  1    @1 MONIELLO (Giuseppe)
A11 06  1    @1 HUNG (Silas S. O.)
A14 01      @1 Department of Animal Science, University of California, One Shields Avenue @2 Davis, CA 95616-8521 @3 USA @Z 1 aut. @Z 2 aut. @Z 3 aut. @Z 6 aut.
A14 02      @1 Department of Animal Biology, University ofSassari, Via Vienna 2 @2 07100 Sassari @3 ITA @Z 2 aut. @Z 5 aut.
A14 03      @1 Feeds and Foods Nutrition Research Center/Department of Marine Bio-materials and Aquaculture, Pukyong National University, 599-1 @2 Daeyeon 3-Dong, Busan 608-737 @3 KOR @Z 4 aut.
A20       @1 227-234
A21       @1 2011
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A44       @0 0000 @1 © 2012 INIST-CNRS. All rights reserved.
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C01 01    ENG  @0 Triplicate groups of juvenile green and white sturgeon (30 ± 2 g) were exposed to one of the four nominal concentrations of dietary methylmercury (MeHg, 0 (control), 25, 50, and 100 mg MeHg/kg diet) for 8 weeks to determine and compare the effects on growth performance and mercury (Hg) tissue burden in the two sturgeon species. Mortality, growth performance as measured by percent body weight increase per day, hepatosomatic index, proximate composition of whole body, and Hg burden in the whole body, gill, heart, liver, kidney, and white muscle were determined to assess the adverse growth effects and bioaccumulation of dietary MeHg in sturgeon. Significantly higher mortality and lower growth rate (p < 0.05) were noted in green and white sturgeon fed the MeHg diets compared to the controls. Green sturgeon fed the MeHg diets exhibited earlier and more severe adverse effects compared to white sturgeon. Mercury accumulated in all tissues in a dose-dependent manner regardless of species, and the highest Hg concentrations were found in the kidneys of both species. Dietary MeHg had no significant effect (p > 0.05) on the whole body proximate compositions of either sturgeon species. In conclusion, green sturgeon was more susceptible to dietary MeHg toxicity than white sturgeon in our 8-week growth experiment based on the higher mortality and lower growth rate and body energy contents.
C02 01  X    @0 002A14D05A
C02 02  X    @0 002A15B
C03 01  X  FRE  @0 Régime alimentaire @5 01
C03 01  X  ENG  @0 Diet @5 01
C03 01  X  SPA  @0 Régimen alimentario @5 01
C03 02  X  FRE  @0 Croissance @5 02
C03 02  X  ENG  @0 Growth @5 02
C03 02  X  SPA  @0 Crecimiento @5 02
C03 03  X  FRE  @0 Performance @5 03
C03 03  X  ENG  @0 Performance @5 03
C03 03  X  SPA  @0 Rendimiento @5 03
C03 04  X  FRE  @0 Animal jeune @5 04
C03 04  X  ENG  @0 Young animal @5 04
C03 04  X  SPA  @0 Animal joven @5 04
C03 05  X  FRE  @0 Mercure @2 NC @2 FX @5 05
C03 05  X  ENG  @0 Mercury @2 NC @2 FX @5 05
C03 05  X  SPA  @0 Mercurio @2 NC @2 FX @5 05
C03 06  X  FRE  @0 Toxicité @5 06
C03 06  X  ENG  @0 Toxicity @5 06
C03 06  X  SPA  @0 Toxicidad @5 06
C03 07  X  FRE  @0 Milieu aquatique @5 07
C03 07  X  ENG  @0 Aquatic environment @5 07
C03 07  X  SPA  @0 Medio acuático @5 07
C03 08  X  FRE  @0 Ecotoxicologie @5 08
C03 08  X  ENG  @0 Ecotoxicology @5 08
C03 08  X  SPA  @0 Ecotoxicología @5 08
C03 09  X  FRE  @0 Polluant @5 23
C03 09  X  ENG  @0 Pollutant @5 23
C03 09  X  SPA  @0 Contaminante @5 23
C03 10  X  FRE  @0 Acipenser transmontanus @2 NS @5 49
C03 10  X  ENG  @0 Acipenser transmontanus @2 NS @5 49
C03 10  X  SPA  @0 Acipenser transmontanus @2 NS @5 49
C03 11  X  FRE  @0 Mercure(méthyl) @4 INC @5 87
C07 01  X  FRE  @0 Alimentation @5 17
C07 01  X  ENG  @0 Feeding @5 17
C07 01  X  SPA  @0 Alimentación @5 17
C07 02  X  FRE  @0 Composé organique @2 NA @5 18
C07 02  X  ENG  @0 Organic compounds @2 NA @5 18
C07 02  X  SPA  @0 Compuesto orgánico @2 NA @5 18
C07 03  X  FRE  @0 Métal lourd @5 19
C07 03  X  ENG  @0 Heavy metal @5 19
C07 03  X  SPA  @0 Metal pesado @5 19
C07 04  X  FRE  @0 Pisces @2 NS @5 29
C07 04  X  ENG  @0 Pisces @2 NS @5 29
C07 04  X  SPA  @0 Pisces @2 NS @5 29
C07 05  X  FRE  @0 Vertebrata @2 NS
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C07 06  X  FRE  @0 Acipenseridae @4 INC @5 70
N21       @1 002
N44 01      @1 OTO
N82       @1 OTO

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Pascal:12-0016619

Le document en format XML

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<title xml:lang="en" level="a">Effects of dietary methylmercury on growth performance and tissue burden in juvenile green (Acipenser medirostris) and white sturgeon (A. transmontanus)</title>
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<name sortKey="Moniello, Giuseppe" sort="Moniello, Giuseppe" uniqKey="Moniello G" first="Giuseppe" last="Moniello">Giuseppe Moniello</name>
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<term>Acipenser transmontanus</term>
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<term>Diet</term>
<term>Ecotoxicology</term>
<term>Growth</term>
<term>Mercury</term>
<term>Performance</term>
<term>Pollutant</term>
<term>Toxicity</term>
<term>Young animal</term>
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<term>Régime alimentaire</term>
<term>Croissance</term>
<term>Performance</term>
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<term>Milieu aquatique</term>
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<term>Acipenser transmontanus</term>
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<div type="abstract" xml:lang="en">Triplicate groups of juvenile green and white sturgeon (30 ± 2 g) were exposed to one of the four nominal concentrations of dietary methylmercury (MeHg, 0 (control), 25, 50, and 100 mg MeHg/kg diet) for 8 weeks to determine and compare the effects on growth performance and mercury (Hg) tissue burden in the two sturgeon species. Mortality, growth performance as measured by percent body weight increase per day, hepatosomatic index, proximate composition of whole body, and Hg burden in the whole body, gill, heart, liver, kidney, and white muscle were determined to assess the adverse growth effects and bioaccumulation of dietary MeHg in sturgeon. Significantly higher mortality and lower growth rate (p < 0.05) were noted in green and white sturgeon fed the MeHg diets compared to the controls. Green sturgeon fed the MeHg diets exhibited earlier and more severe adverse effects compared to white sturgeon. Mercury accumulated in all tissues in a dose-dependent manner regardless of species, and the highest Hg concentrations were found in the kidneys of both species. Dietary MeHg had no significant effect (p > 0.05) on the whole body proximate compositions of either sturgeon species. In conclusion, green sturgeon was more susceptible to dietary MeHg toxicity than white sturgeon in our 8-week growth experiment based on the higher mortality and lower growth rate and body energy contents.</div>
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<fC01 i1="01" l="ENG">
<s0>Triplicate groups of juvenile green and white sturgeon (30 ± 2 g) were exposed to one of the four nominal concentrations of dietary methylmercury (MeHg, 0 (control), 25, 50, and 100 mg MeHg/kg diet) for 8 weeks to determine and compare the effects on growth performance and mercury (Hg) tissue burden in the two sturgeon species. Mortality, growth performance as measured by percent body weight increase per day, hepatosomatic index, proximate composition of whole body, and Hg burden in the whole body, gill, heart, liver, kidney, and white muscle were determined to assess the adverse growth effects and bioaccumulation of dietary MeHg in sturgeon. Significantly higher mortality and lower growth rate (p < 0.05) were noted in green and white sturgeon fed the MeHg diets compared to the controls. Green sturgeon fed the MeHg diets exhibited earlier and more severe adverse effects compared to white sturgeon. Mercury accumulated in all tissues in a dose-dependent manner regardless of species, and the highest Hg concentrations were found in the kidneys of both species. Dietary MeHg had no significant effect (p > 0.05) on the whole body proximate compositions of either sturgeon species. In conclusion, green sturgeon was more susceptible to dietary MeHg toxicity than white sturgeon in our 8-week growth experiment based on the higher mortality and lower growth rate and body energy contents.</s0>
</fC01>
<fC02 i1="01" i2="X">
<s0>002A14D05A</s0>
</fC02>
<fC02 i1="02" i2="X">
<s0>002A15B</s0>
</fC02>
<fC03 i1="01" i2="X" l="FRE">
<s0>Régime alimentaire</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG">
<s0>Diet</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="SPA">
<s0>Régimen alimentario</s0>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE">
<s0>Croissance</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="ENG">
<s0>Growth</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="SPA">
<s0>Crecimiento</s0>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE">
<s0>Performance</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG">
<s0>Performance</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA">
<s0>Rendimiento</s0>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE">
<s0>Animal jeune</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG">
<s0>Young animal</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA">
<s0>Animal joven</s0>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE">
<s0>Mercure</s0>
<s2>NC</s2>
<s2>FX</s2>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG">
<s0>Mercury</s0>
<s2>NC</s2>
<s2>FX</s2>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA">
<s0>Mercurio</s0>
<s2>NC</s2>
<s2>FX</s2>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE">
<s0>Toxicité</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG">
<s0>Toxicity</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA">
<s0>Toxicidad</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE">
<s0>Milieu aquatique</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG">
<s0>Aquatic environment</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA">
<s0>Medio acuático</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE">
<s0>Ecotoxicologie</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG">
<s0>Ecotoxicology</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA">
<s0>Ecotoxicología</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE">
<s0>Polluant</s0>
<s5>23</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG">
<s0>Pollutant</s0>
<s5>23</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA">
<s0>Contaminante</s0>
<s5>23</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE">
<s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG">
<s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA">
<s0>Acipenser transmontanus</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE">
<s0>Mercure(méthyl)</s0>
<s4>INC</s4>
<s5>87</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE">
<s0>Alimentation</s0>
<s5>17</s5>
</fC07>
<fC07 i1="01" i2="X" l="ENG">
<s0>Feeding</s0>
<s5>17</s5>
</fC07>
<fC07 i1="01" i2="X" l="SPA">
<s0>Alimentación</s0>
<s5>17</s5>
</fC07>
<fC07 i1="02" i2="X" l="FRE">
<s0>Composé organique</s0>
<s2>NA</s2>
<s5>18</s5>
</fC07>
<fC07 i1="02" i2="X" l="ENG">
<s0>Organic compounds</s0>
<s2>NA</s2>
<s5>18</s5>
</fC07>
<fC07 i1="02" i2="X" l="SPA">
<s0>Compuesto orgánico</s0>
<s2>NA</s2>
<s5>18</s5>
</fC07>
<fC07 i1="03" i2="X" l="FRE">
<s0>Métal lourd</s0>
<s5>19</s5>
</fC07>
<fC07 i1="03" i2="X" l="ENG">
<s0>Heavy metal</s0>
<s5>19</s5>
</fC07>
<fC07 i1="03" i2="X" l="SPA">
<s0>Metal pesado</s0>
<s5>19</s5>
</fC07>
<fC07 i1="04" i2="X" l="FRE">
<s0>Pisces</s0>
<s2>NS</s2>
<s5>29</s5>
</fC07>
<fC07 i1="04" i2="X" l="ENG">
<s0>Pisces</s0>
<s2>NS</s2>
<s5>29</s5>
</fC07>
<fC07 i1="04" i2="X" l="SPA">
<s0>Pisces</s0>
<s2>NS</s2>
<s5>29</s5>
</fC07>
<fC07 i1="05" i2="X" l="FRE">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="ENG">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="SPA">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="FRE">
<s0>Acipenseridae</s0>
<s4>INC</s4>
<s5>70</s5>
</fC07>
<fN21>
<s1>002</s1>
</fN21>
<fN44 i1="01">
<s1>OTO</s1>
</fN44>
<fN82>
<s1>OTO</s1>
</fN82>
</pA>
</standard>
</inist>
</record>

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   |wiki=    Wicri/Eau
   |area=    EsturgeonV1
   |flux=    PascalFrancis
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   |texte=   Effects of dietary methylmercury on growth performance and tissue burden in juvenile green (Acipenser medirostris) and white sturgeon (A. transmontanus)
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