EsturgeonV1, PascalFrancis, Curation, bibRecord, 000339

Distribution is a Major Factor Affecting Bioaccumulation of Decabrominated Diphenyl Ether: Chinese Sturgeon (Acipenser sinensis) as an Example

Identifieur interne : 000339 ( PascalFrancis/Curation ); précédent : 000338; suivant : 000340

Distribution is a Major Factor Affecting Bioaccumulation of Decabrominated Diphenyl Ether: Chinese Sturgeon (Acipenser sinensis) as an Example

Auteurs : YI WAN [République populaire de Chine] ; KUN ZHANG [République populaire de Chine] ; ZHAOMIN DONG [République populaire de Chine] ; JIANYING HU [République populaire de Chine]

Source :

Environmental science & technology [ 0013-936X ] ; 2013.

RBID : Pascal:13-0247493

Descripteurs français

Pascal (Inist)
- Polluant, Retardateur flamme, Accumulation biologique, Toxicocinétique, Biocénose, Modèle animal, Composition corporelle, Métabolisme, In vitro, Microsome, Acipenser sinensis, Phényle éther(polybromo).
Wicri :
- topic : Polluant.

English descriptors

KwdEn :
- Animal model, Biocenosis, Biological accumulation, Body composition, Flame retardant, In vitro, Metabolism, Microsome, Pollutant, Toxicokinetics.

Abstract

While decabromodiphenyl ether (BDE-209) has very low bioavailability and a rapid biotransformation rate, it exhibits high bioaccumulation in wildlife. To explore the bioaccumulation mechanism of BDE-209 in organisms, its toxicokinetic processes were investigated in Chinese sturgeons from the Yangtze River. Different from less brominated BDEs, lipids did not play an important role in the distribution of BDE-209 with relatively high concentrations detected in liver (54.5 ± 3.3 ng/g wet weight (ww)), gills (47.4 _± 2.9 ng/g ww), and intestine (41.9 ± 3.0 ng/g ww), followed by stomach (21.9 ± 9.0 ng/g ww), muscle (19.1 ± 5.6 ng/g ww), heart (7.5 ± 5.2 ng/g ww), gonad (6.8 ± 4.9 ng/g ww), adipose (4.9 ± 1.2 ng/g ww), and egg (2.8 ± 2.3 ng/g ww). In vitro metabolism of BDE-209 by microsomal fractions of Chinese sturgeon found that BDE-209 was biotransformed rapidly with the rate constant (K) of 0.039 h^-1 in liver. BDE-126, BDE-154, BDE-188, BDE-184, BDE-183, BDE-202, BDE-201, and BDE-204/ 197 were observed as debrominated products of BDE-209 after incubation, and their formation rates were 0.026, 0.016, and 0.006 h^-1 for BDE-126 BDE-184, and BDE-154, respectively. The concentration ratios between heart and intestine for individual PBDEs suggested slow delivery of BDE-209 among tissues after absorption. A Bayesian hierarchical model was further developed to estimate partition coefficients in a physiologically based pharmacokinetic model of BDE-209 in Chinese sturgeon. The estimated partition coefficients between tissues and blood were higher than those of less brominated BDE or PCBs in various animals, suggesting that the low partition ratios from blood to tissues would lead to high bioaccumulation of BDE-209, especially in absorbing organs.

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A03		`1`		`@0 Environ. sci. technol.`
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A08	`01`	`1`	`ENG`	`@1 Distribution is a Major Factor Affecting Bioaccumulation of Decabrominated Diphenyl Ether: Chinese Sturgeon (Acipenser sinensis) as an Example`
A11	`01`	`1`		`@1 YI WAN`
A11	`02`	`1`		`@1 KUN ZHANG`
A11	`03`	`1`		`@1 ZHAOMIN DONG`
A11	`04`	`1`		`@1 JIANYING HU`
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C01	`01`		`ENG`	@0 While decabromodiphenyl ether (BDE-209) has very low bioavailability and a rapid biotransformation rate, it exhibits high bioaccumulation in wildlife. To explore the bioaccumulation mechanism of BDE-209 in organisms, its toxicokinetic processes were investigated in Chinese sturgeons from the Yangtze River. Different from less brominated BDEs, lipids did not play an important role in the distribution of BDE-209 with relatively high concentrations detected in liver (54.5 ± 3.3 ng/g wet weight (ww)), gills (47.4 _± 2.9 ng/g ww), and intestine (41.9 ± 3.0 ng/g ww), followed by stomach (21.9 ± 9.0 ng/g ww), muscle (19.1 ± 5.6 ng/g ww), heart (7.5 ± 5.2 ng/g ww), gonad (6.8 ± 4.9 ng/g ww), adipose (4.9 ± 1.2 ng/g ww), and egg (2.8 ± 2.3 ng/g ww). In vitro metabolism of BDE-209 by microsomal fractions of Chinese sturgeon found that BDE-209 was biotransformed rapidly with the rate constant (K) of 0.039 h^-1 in liver. BDE-126, BDE-154, BDE-188, BDE-184, BDE-183, BDE-202, BDE-201, and BDE-204/ 197 were observed as debrominated products of BDE-209 after incubation, and their formation rates were 0.026, 0.016, and 0.006 h^-1 for BDE-126 BDE-184, and BDE-154, respectively. The concentration ratios between heart and intestine for individual PBDEs suggested slow delivery of BDE-209 among tissues after absorption. A Bayesian hierarchical model was further developed to estimate partition coefficients in a physiologically based pharmacokinetic model of BDE-209 in Chinese sturgeon. The estimated partition coefficients between tissues and blood were higher than those of less brominated BDE or PCBs in various animals, suggesting that the low partition ratios from blood to tissues would lead to high bioaccumulation of BDE-209, especially in absorbing organs.
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C03	`01`	`X`	`SPA`	`@0 Contaminante @5 01`
C03	`02`	`X`	`FRE`	`@0 Retardateur flamme @5 02`
C03	`02`	`X`	`ENG`	`@0 Flame retardant @5 02`
C03	`02`	`X`	`SPA`	`@0 Retardador llama @5 02`
C03	`03`	`X`	`FRE`	`@0 Accumulation biologique @5 03`
C03	`03`	`X`	`ENG`	`@0 Biological accumulation @5 03`
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C03	`04`	`X`	`FRE`	`@0 Toxicocinétique @5 04`
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C03	`04`	`X`	`SPA`	`@0 Toxicocinética @5 04`
C03	`05`	`X`	`FRE`	`@0 Biocénose @5 05`
C03	`05`	`X`	`ENG`	`@0 Biocenosis @5 05`
C03	`05`	`X`	`SPA`	`@0 Biocenosis @5 05`
C03	`06`	`X`	`FRE`	`@0 Modèle animal @5 06`
C03	`06`	`X`	`ENG`	`@0 Animal model @5 06`
C03	`06`	`X`	`SPA`	`@0 Modelo animal @5 06`
C03	`07`	`X`	`FRE`	`@0 Composition corporelle @5 07`
C03	`07`	`X`	`ENG`	`@0 Body composition @5 07`
C03	`07`	`X`	`SPA`	`@0 Composicíon corporal @5 07`
C03	`08`	`X`	`FRE`	`@0 Métabolisme @5 08`
C03	`08`	`X`	`ENG`	`@0 Metabolism @5 08`
C03	`08`	`X`	`SPA`	`@0 Metabolismo @5 08`
C03	`09`	`X`	`FRE`	`@0 In vitro @5 09`
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C03	`09`	`X`	`SPA`	`@0 In vitro @5 09`
C03	`10`	`X`	`FRE`	`@0 Microsome @5 10`
C03	`10`	`X`	`ENG`	`@0 Microsome @5 10`
C03	`10`	`X`	`SPA`	`@0 Microsoma @5 10`
C03	`11`	`X`	`FRE`	`@0 Acipenser sinensis @4 INC @5 87`
C03	`12`	`X`	`FRE`	`@0 Phényle éther(polybromo) @4 INC @5 88`
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N21				`@1 238`

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Le document en format XML

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<front><div type="abstract" xml:lang="en">While decabromodiphenyl ether (BDE-209) has very low bioavailability and a rapid biotransformation rate, it exhibits high bioaccumulation in wildlife. To explore the bioaccumulation mechanism of BDE-209 in organisms, its toxicokinetic processes were investigated in Chinese sturgeons from the Yangtze River. Different from less brominated BDEs, lipids did not play an important role in the distribution of BDE-209 with relatively high concentrations detected in liver (54.5 ± 3.3 ng/g wet weight (ww)), gills (47.4 <sub>±</sub>
 2.9 ng/g ww), and intestine (41.9 ± 3.0 ng/g ww), followed by stomach (21.9 ± 9.0 ng/g ww), muscle (19.1 ± 5.6 ng/g ww), heart (7.5 ± 5.2 ng/g ww), gonad (6.8 ± 4.9 ng/g ww), adipose (4.9 ± 1.2 ng/g ww), and egg (2.8 ± 2.3 ng/g ww). In vitro metabolism of BDE-209 by microsomal fractions of Chinese sturgeon found that BDE-209 was biotransformed rapidly with the rate constant (K) of 0.039 h<sup>-1</sup>
 in liver. BDE-126, BDE-154, BDE-188, BDE-184, BDE-183, BDE-202, BDE-201, and BDE-204/ 197 were observed as debrominated products of BDE-209 after incubation, and their formation rates were 0.026, 0.016, and 0.006 h<sup>-1</sup>
 for BDE-126 BDE-184, and BDE-154, respectively. The concentration ratios between heart and intestine for individual PBDEs suggested slow delivery of BDE-209 among tissues after absorption. A Bayesian hierarchical model was further developed to estimate partition coefficients in a physiologically based pharmacokinetic model of BDE-209 in Chinese sturgeon. The estimated partition coefficients between tissues and blood were higher than those of less brominated BDE or PCBs in various animals, suggesting that the low partition ratios from blood to tissues would lead to high bioaccumulation of BDE-209, especially in absorbing organs.</div>
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<fC01 i1="01" l="ENG"><s0>While decabromodiphenyl ether (BDE-209) has very low bioavailability and a rapid biotransformation rate, it exhibits high bioaccumulation in wildlife. To explore the bioaccumulation mechanism of BDE-209 in organisms, its toxicokinetic processes were investigated in Chinese sturgeons from the Yangtze River. Different from less brominated BDEs, lipids did not play an important role in the distribution of BDE-209 with relatively high concentrations detected in liver (54.5 ± 3.3 ng/g wet weight (ww)), gills (47.4 <sub>±</sub>
 2.9 ng/g ww), and intestine (41.9 ± 3.0 ng/g ww), followed by stomach (21.9 ± 9.0 ng/g ww), muscle (19.1 ± 5.6 ng/g ww), heart (7.5 ± 5.2 ng/g ww), gonad (6.8 ± 4.9 ng/g ww), adipose (4.9 ± 1.2 ng/g ww), and egg (2.8 ± 2.3 ng/g ww). In vitro metabolism of BDE-209 by microsomal fractions of Chinese sturgeon found that BDE-209 was biotransformed rapidly with the rate constant (K) of 0.039 h<sup>-1</sup>
 in liver. BDE-126, BDE-154, BDE-188, BDE-184, BDE-183, BDE-202, BDE-201, and BDE-204/ 197 were observed as debrominated products of BDE-209 after incubation, and their formation rates were 0.026, 0.016, and 0.006 h<sup>-1</sup>
 for BDE-126 BDE-184, and BDE-154, respectively. The concentration ratios between heart and intestine for individual PBDEs suggested slow delivery of BDE-209 among tissues after absorption. A Bayesian hierarchical model was further developed to estimate partition coefficients in a physiologically based pharmacokinetic model of BDE-209 in Chinese sturgeon. The estimated partition coefficients between tissues and blood were higher than those of less brominated BDE or PCBs in various animals, suggesting that the low partition ratios from blood to tissues would lead to high bioaccumulation of BDE-209, especially in absorbing organs.</s0>
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<fC03 i1="05" i2="X" l="FRE"><s0>Biocénose</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG"><s0>Biocenosis</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA"><s0>Biocenosis</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE"><s0>Modèle animal</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG"><s0>Animal model</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA"><s0>Modelo animal</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE"><s0>Composition corporelle</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG"><s0>Body composition</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA"><s0>Composicíon corporal</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE"><s0>Métabolisme</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG"><s0>Metabolism</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA"><s0>Metabolismo</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE"><s0>In vitro</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG"><s0>In vitro</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA"><s0>In vitro</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE"><s0>Microsome</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG"><s0>Microsome</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA"><s0>Microsoma</s0>
<s5>10</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE"><s0>Acipenser sinensis</s0>
<s4>INC</s4>
<s5>87</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE"><s0>Phényle éther(polybromo)</s0>
<s4>INC</s4>
<s5>88</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE"><s0>Pisces</s0>
<s2>NS</s2>
<s5>26</s5>
</fC07>
<fC07 i1="01" i2="X" l="ENG"><s0>Pisces</s0>
<s2>NS</s2>
<s5>26</s5>
</fC07>
<fC07 i1="01" i2="X" l="SPA"><s0>Pisces</s0>
<s2>NS</s2>
<s5>26</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>
<fN21><s1>238</s1>
</fN21>
</pA>
</standard>
</inist>
</record>

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   |wiki=    Wicri/Eau
   |area=    EsturgeonV1
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   |type=    RBID
   |clé=     Pascal:13-0247493
   |texte=   Distribution is a Major Factor Affecting Bioaccumulation of Decabrominated Diphenyl Ether: Chinese Sturgeon (Acipenser sinensis) as an Example
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Distribution is a Major Factor Affecting Bioaccumulation of Decabrominated Diphenyl Ether: Chinese Sturgeon (Acipenser sinensis) as an Example

Distribution is a Major Factor Affecting Bioaccumulation of Decabrominated Diphenyl Ether: Chinese Sturgeon (Acipenser sinensis) as an Example

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Abstract

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