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Multi-species comparison of the mechanism of biotransformation of MeO-BDEs to OH-BDEs in fish

Identifieur interne : 000058 ( PascalFrancis/Checkpoint ); précédent : 000057; suivant : 000059

Multi-species comparison of the mechanism of biotransformation of MeO-BDEs to OH-BDEs in fish

Auteurs : FENGYAN LIU [Canada] ; Steve Wiseman [Canada] ; YI WAN [République populaire de Chine] ; Jonathan A. Doering [Canada] ; Markus Hecker [Canada] ; Michael H. W. Lam [Canada] ; John P. Giesy [Canada, Hong Kong, Arabie saoudite, États-Unis]

Source :

RBID : Pascal:12-0200614

Descripteurs français

English descriptors

Abstract

Polybrominated diphenyl ethers (PBDEs) and their methoxylated- (MeO-) and hydroxylated- (OH-) analogs are ubiquitously distributed in the environment worldwide. The OH-BDEs have greater potency than PBDEs and can be produced from the transformation of MeO-BDEs. The objectives of the current study were to (1) identify the enzyme(s) that catalyze biotransformation of 6-MeO-BDE-47 to 6-OH-BDE-47 in livers from rainbow trout, and (2) compare biotransformation of 6-MeO-BDE-47 to 6-OH-BDE-47 among rainbow trout, white sturgeon and goldfish. Cytochrome P450 1A (CYP1A) enzymes did not catalyze the biotransformation reaction. However, biotransformation was significantly inhibited by the CYP inhibitors clotrimazole and 1-benzylimidazole but not gestodene. Therefore, the reaction is likely catalyzed by CYP2 enzymes. When biotransformation was compared among species, concentrations of 6-OH-BDE-47 were significantly 3.4- and 9.1-fold greater in microsomes from rainbow trout compared to goldfish or white sturgeon, respectively. Concentrations of 6-OH-BDE-47 in microsomes from goldfish were non-significantly 2.7-fold greater than in sturgeon. The initial rate of biotransformation in microsomes from livers of rainbow trout was significantly 2.0- and 6.2-fold greater than the initial rate of biotransformation in microsomes from livers of goldfish or sturgeon, respectively, while the initial rate in goldfish was significantly 3.1-fold greater than in sturgeon. It is hypothesized that differences in CYP-mediated biotransformation of MeO-BDEs to OH-BDEs could influence concentrations of OH-BDEs in different species of fish.


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Le document en format XML

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<div type="abstract" xml:lang="en">Polybrominated diphenyl ethers (PBDEs) and their methoxylated- (MeO-) and hydroxylated- (OH-) analogs are ubiquitously distributed in the environment worldwide. The OH-BDEs have greater potency than PBDEs and can be produced from the transformation of MeO-BDEs. The objectives of the current study were to (1) identify the enzyme(s) that catalyze biotransformation of 6-MeO-BDE-47 to 6-OH-BDE-47 in livers from rainbow trout, and (2) compare biotransformation of 6-MeO-BDE-47 to 6-OH-BDE-47 among rainbow trout, white sturgeon and goldfish. Cytochrome P450 1A (CYP1A) enzymes did not catalyze the biotransformation reaction. However, biotransformation was significantly inhibited by the CYP inhibitors clotrimazole and 1-benzylimidazole but not gestodene. Therefore, the reaction is likely catalyzed by CYP2 enzymes. When biotransformation was compared among species, concentrations of 6-OH-BDE-47 were significantly 3.4- and 9.1-fold greater in microsomes from rainbow trout compared to goldfish or white sturgeon, respectively. Concentrations of 6-OH-BDE-47 in microsomes from goldfish were non-significantly 2.7-fold greater than in sturgeon. The initial rate of biotransformation in microsomes from livers of rainbow trout was significantly 2.0- and 6.2-fold greater than the initial rate of biotransformation in microsomes from livers of goldfish or sturgeon, respectively, while the initial rate in goldfish was significantly 3.1-fold greater than in sturgeon. It is hypothesized that differences in CYP-mediated biotransformation of MeO-BDEs to OH-BDEs could influence concentrations of OH-BDEs in different species of fish.</div>
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<s1>GIESY (John P.)</s1>
</fA11>
<fA14 i1="01">
<s1>Toxicology Centre, University of Saskatchewan</s1>
<s2>Saskatoon, SK S7N 5B3</s2>
<s3>CAN</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
<sZ>4 aut.</sZ>
<sZ>5 aut.</sZ>
<sZ>7 aut.</sZ>
</fA14>
<fA14 i1="02">
<s1>College of Urban and Environmental Sciences, Peking University</s1>
<s2>Beijing 100871</s2>
<s3>CHN</s3>
<sZ>3 aut.</sZ>
</fA14>
<fA14 i1="03">
<s1>School of Environment and Sustainability, University of Saskatchewan</s1>
<s2>Saskatoon, SK S7N 5C8</s2>
<s3>CAN</s3>
<sZ>4 aut.</sZ>
<sZ>5 aut.</sZ>
</fA14>
<fA14 i1="04">
<s1>Depamment of Veterinary Biomedical Sciences, University of Saskatchewan</s1>
<s2>Saskatoon, SK S7N 5C8</s2>
<s3>CAN</s3>
<sZ>6 aut.</sZ>
<sZ>7 aut.</sZ>
</fA14>
<fA14 i1="05">
<s1>Department of Biology and Chemistry, and State Key Laboratory for Marine Pollution, City University of Hong Kong</s1>
<s2>Kowloon</s2>
<s3>HKG</s3>
<sZ>7 aut.</sZ>
</fA14>
<fA14 i1="06">
<s1>Department of Zoology, College of Science, King Saud University, P.O. Box 2455</s1>
<s2>Riyadh 11451</s2>
<s3>SAU</s3>
<sZ>7 aut.</sZ>
</fA14>
<fA14 i1="07">
<s1>School of Biological Sciences, The University of Hong Kong, Hong Kong Special Administrative Region</s1>
<s3>HKG</s3>
<sZ>7 aut.</sZ>
</fA14>
<fA14 i1="08">
<s1>Department of Zoology, Center for Integrative Toxicology, Michigan State University</s1>
<s2>East Lansing, MI 48824</s2>
<s3>USA</s3>
<sZ>7 aut.</sZ>
</fA14>
<fA20>
<s1>182-188</s1>
</fA20>
<fA21>
<s1>2012</s1>
</fA21>
<fA23 i1="01">
<s0>ENG</s0>
</fA23>
<fA43 i1="01">
<s1>INIST</s1>
<s2>18841</s2>
<s5>354000506905600210</s5>
</fA43>
<fA44>
<s0>0000</s0>
<s1>© 2012 INIST-CNRS. All rights reserved.</s1>
</fA44>
<fA45>
<s0>3/4 p.</s0>
</fA45>
<fA47 i1="01" i2="1">
<s0>12-0200614</s0>
</fA47>
<fA60>
<s1>P</s1>
</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>Polybrominated diphenyl ethers (PBDEs) and their methoxylated- (MeO-) and hydroxylated- (OH-) analogs are ubiquitously distributed in the environment worldwide. The OH-BDEs have greater potency than PBDEs and can be produced from the transformation of MeO-BDEs. The objectives of the current study were to (1) identify the enzyme(s) that catalyze biotransformation of 6-MeO-BDE-47 to 6-OH-BDE-47 in livers from rainbow trout, and (2) compare biotransformation of 6-MeO-BDE-47 to 6-OH-BDE-47 among rainbow trout, white sturgeon and goldfish. Cytochrome P450 1A (CYP1A) enzymes did not catalyze the biotransformation reaction. However, biotransformation was significantly inhibited by the CYP inhibitors clotrimazole and 1-benzylimidazole but not gestodene. Therefore, the reaction is likely catalyzed by CYP2 enzymes. When biotransformation was compared among species, concentrations of 6-OH-BDE-47 were significantly 3.4- and 9.1-fold greater in microsomes from rainbow trout compared to goldfish or white sturgeon, respectively. Concentrations of 6-OH-BDE-47 in microsomes from goldfish were non-significantly 2.7-fold greater than in sturgeon. The initial rate of biotransformation in microsomes from livers of rainbow trout was significantly 2.0- and 6.2-fold greater than the initial rate of biotransformation in microsomes from livers of goldfish or sturgeon, respectively, while the initial rate in goldfish was significantly 3.1-fold greater than in sturgeon. It is hypothesized that differences in CYP-mediated biotransformation of MeO-BDEs to OH-BDEs could influence concentrations of OH-BDEs in different species of fish.</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>Biotransformation</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG">
<s0>Biotransformation</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="SPA">
<s0>Biotransformación</s0>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE">
<s0>Pisces</s0>
<s2>NS</s2>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="ENG">
<s0>Pisces</s0>
<s2>NS</s2>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="SPA">
<s0>Pisces</s0>
<s2>NS</s2>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE">
<s0>Cytochrome P450</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG">
<s0>Cytochrome P450</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA">
<s0>Citocromo P450</s0>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE">
<s0>Microsome</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG">
<s0>Microsome</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA">
<s0>Microsoma</s0>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE">
<s0>Hydroxylation</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG">
<s0>Hydroxylation</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA">
<s0>Hidroxilación</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE">
<s0>Inhibiteur</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG">
<s0>Inhibitor</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA">
<s0>Inhibidor</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>Marqueur biologique</s0>
<s5>23</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG">
<s0>Biological marker</s0>
<s5>23</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA">
<s0>Marcador biológico</s0>
<s5>23</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE">
<s0>Toxicité</s0>
<s5>24</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG">
<s0>Toxicity</s0>
<s5>24</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA">
<s0>Toxicidad</s0>
<s5>24</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE">
<s0>Acipenser</s0>
<s4>INC</s4>
<s5>64</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="01" i2="X" l="ENG">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="01" i2="X" l="SPA">
<s0>Vertebrata</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="FRE">
<s0>Acipenseridae</s0>
<s4>INC</s4>
<s5>70</s5>
</fC07>
<fN21>
<s1>156</s1>
</fN21>
<fN44 i1="01">
<s1>OTO</s1>
</fN44>
<fN82>
<s1>OTO</s1>
</fN82>
</pA>
</standard>
</inist>
<affiliations>
<list>
<country>
<li>Arabie saoudite</li>
<li>Canada</li>
<li>Hong Kong</li>
<li>République populaire de Chine</li>
<li>États-Unis</li>
</country>
<region>
<li>Michigan</li>
<li>Pékin</li>
</region>
<settlement>
<li>East Lansing</li>
<li>Pékin</li>
</settlement>
<orgName>
<li>Université d'État du Michigan</li>
<li>Université de Pékin</li>
</orgName>
</list>
<tree>
<country name="Canada">
<noRegion>
<name sortKey="Fengyan Liu" sort="Fengyan Liu" uniqKey="Fengyan Liu" last="Fengyan Liu">FENGYAN LIU</name>
</noRegion>
<name sortKey="Doering, Jonathan A" sort="Doering, Jonathan A" uniqKey="Doering J" first="Jonathan A." last="Doering">Jonathan A. Doering</name>
<name sortKey="Doering, Jonathan A" sort="Doering, Jonathan A" uniqKey="Doering J" first="Jonathan A." last="Doering">Jonathan A. Doering</name>
<name sortKey="Giesy, John P" sort="Giesy, John P" uniqKey="Giesy J" first="John P." last="Giesy">John P. Giesy</name>
<name sortKey="Giesy, John P" sort="Giesy, John P" uniqKey="Giesy J" first="John P." last="Giesy">John P. Giesy</name>
<name sortKey="Hecker, Markus" sort="Hecker, Markus" uniqKey="Hecker M" first="Markus" last="Hecker">Markus Hecker</name>
<name sortKey="Hecker, Markus" sort="Hecker, Markus" uniqKey="Hecker M" first="Markus" last="Hecker">Markus Hecker</name>
<name sortKey="Lam, Michael H W" sort="Lam, Michael H W" uniqKey="Lam M" first="Michael H. W." last="Lam">Michael H. W. Lam</name>
<name sortKey="Wiseman, Steve" sort="Wiseman, Steve" uniqKey="Wiseman S" first="Steve" last="Wiseman">Steve Wiseman</name>
</country>
<country name="République populaire de Chine">
<noRegion>
<name sortKey="Yi Wan" sort="Yi Wan" uniqKey="Yi Wan" last="Yi Wan">YI WAN</name>
</noRegion>
</country>
<country name="Hong Kong">
<noRegion>
<name sortKey="Giesy, John P" sort="Giesy, John P" uniqKey="Giesy J" first="John P." last="Giesy">John P. Giesy</name>
</noRegion>
<name sortKey="Giesy, John P" sort="Giesy, John P" uniqKey="Giesy J" first="John P." last="Giesy">John P. Giesy</name>
</country>
<country name="Arabie saoudite">
<noRegion>
<name sortKey="Giesy, John P" sort="Giesy, John P" uniqKey="Giesy J" first="John P." last="Giesy">John P. Giesy</name>
</noRegion>
</country>
<country name="États-Unis">
<region name="Michigan">
<name sortKey="Giesy, John P" sort="Giesy, John P" uniqKey="Giesy J" first="John P." last="Giesy">John P. Giesy</name>
</region>
</country>
</tree>
</affiliations>
</record>

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