Toxicokinetics of polybrominated diphenyl ethers across life stages in the northern leopard frog (Lithobates pipiens)
Polybrominated diphenyl ethers (PBDEs), a class of flame retardants, are bioaccumulative toxins that can biomagnify in food webs. However, little is known about the toxicokinetics of total and congener‐specific BDEs in lower vertebrates. The authors exposed northern leopard frog (Lithobates (Rana) p...
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Veröffentlicht in: | Environmental toxicology and chemistry 2013-07, Vol.32 (7), p.1631-1640 |
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description | Polybrominated diphenyl ethers (PBDEs), a class of flame retardants, are bioaccumulative toxins that can biomagnify in food webs. However, little is known about the toxicokinetics of total and congener‐specific BDEs in lower vertebrates. The authors exposed northern leopard frog (Lithobates (Rana) pipiens) tadpoles to diets containing DE‐71 (a pentabromodiphenyl ether mixture (0 ng/g as control, 71.4 ng/g, and 634 DE‐71 ng/g wet mass)) for 50 d, followed by a period of depuration during which they were fed only undosed (control) food. After 28 d, tadpoles eliminated over 94% of the ΣPBDEs from their tissues (t½ = 5.9 ± 1.9 d) with no significant differences in elimination rates for the predominant congeners. Elimination of BDE‐99 was independent of dose, indicating first‐order kinetics. It did not fit a biexponential model significantly better than a monoexponential model, indicating single‐compartment elimination. To compare developmental life‐stage kinetics following larval exposure, the authors collected individuals at the beginning and end of metamorphosis and at 70 d postmetamorphosis. During metamorphosis, total‐body residues per individual did not significantly change, implying little to no elimination. After 70 d, juvenile frogs eliminated 89.7% of the ΣPBDEs from their tissues, and BDE‐47 was eliminated at a faster rate (t½= 17.3 d) than BDE‐99 and BDE‐100 (t½ = 63.0 d and 69.3 d, respectively). Because the kinetics of PBDEs in L. pipiens differed among life stages, developmental life stage—especially for species that undergo metamorphosis—should be considered when determining the toxicity of persistent organic pollutants. Environ Toxicol Chem 2013;32:1631–1640. © 2013 SETAC |
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However, little is known about the toxicokinetics of total and congener‐specific BDEs in lower vertebrates. The authors exposed northern leopard frog (Lithobates (Rana) pipiens) tadpoles to diets containing DE‐71 (a pentabromodiphenyl ether mixture (0 ng/g as control, 71.4 ng/g, and 634 DE‐71 ng/g wet mass)) for 50 d, followed by a period of depuration during which they were fed only undosed (control) food. After 28 d, tadpoles eliminated over 94% of the ΣPBDEs from their tissues (t½ = 5.9 ± 1.9 d) with no significant differences in elimination rates for the predominant congeners. Elimination of BDE‐99 was independent of dose, indicating first‐order kinetics. It did not fit a biexponential model significantly better than a monoexponential model, indicating single‐compartment elimination. To compare developmental life‐stage kinetics following larval exposure, the authors collected individuals at the beginning and end of metamorphosis and at 70 d postmetamorphosis. During metamorphosis, total‐body residues per individual did not significantly change, implying little to no elimination. After 70 d, juvenile frogs eliminated 89.7% of the ΣPBDEs from their tissues, and BDE‐47 was eliminated at a faster rate (t½= 17.3 d) than BDE‐99 and BDE‐100 (t½ = 63.0 d and 69.3 d, respectively). Because the kinetics of PBDEs in L. pipiens differed among life stages, developmental life stage—especially for species that undergo metamorphosis—should be considered when determining the toxicity of persistent organic pollutants. 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However, little is known about the toxicokinetics of total and congener‐specific BDEs in lower vertebrates. The authors exposed northern leopard frog (Lithobates (Rana) pipiens) tadpoles to diets containing DE‐71 (a pentabromodiphenyl ether mixture (0 ng/g as control, 71.4 ng/g, and 634 DE‐71 ng/g wet mass)) for 50 d, followed by a period of depuration during which they were fed only undosed (control) food. After 28 d, tadpoles eliminated over 94% of the ΣPBDEs from their tissues (t½ = 5.9 ± 1.9 d) with no significant differences in elimination rates for the predominant congeners. Elimination of BDE‐99 was independent of dose, indicating first‐order kinetics. It did not fit a biexponential model significantly better than a monoexponential model, indicating single‐compartment elimination. To compare developmental life‐stage kinetics following larval exposure, the authors collected individuals at the beginning and end of metamorphosis and at 70 d postmetamorphosis. During metamorphosis, total‐body residues per individual did not significantly change, implying little to no elimination. After 70 d, juvenile frogs eliminated 89.7% of the ΣPBDEs from their tissues, and BDE‐47 was eliminated at a faster rate (t½= 17.3 d) than BDE‐99 and BDE‐100 (t½ = 63.0 d and 69.3 d, respectively). Because the kinetics of PBDEs in L. pipiens differed among life stages, developmental life stage—especially for species that undergo metamorphosis—should be considered when determining the toxicity of persistent organic pollutants. Environ Toxicol Chem 2013;32:1631–1640. © 2013 SETAC</description><subject>Amphibian</subject><subject>Amphibians</subject><subject>Animals</subject><subject>Bioaccumulation</subject><subject>Elimination</subject><subject>Environmental Pollutants - metabolism</subject><subject>Environmental Pollutants - toxicity</subject><subject>Ethers</subject><subject>Flame retardants</subject><subject>Flame Retardants - metabolism</subject><subject>Flame Retardants - toxicity</subject><subject>Food chains</subject><subject>Food webs</subject><subject>Frogs</subject><subject>Halogenated Diphenyl Ethers - metabolism</subject><subject>Halogenated Diphenyl Ethers - toxicity</subject><subject>Kinetics</subject><subject>Metamorphosis</subject><subject>Metamorphosis, Biological</subject><subject>Persistent organic pollutant</subject><subject>Persistent organic pollutants</subject><subject>Pollutants</subject><subject>Polybrominated diphenyl ethers</subject><subject>Rana pipiens - metabolism</subject><subject>Toxicity</subject><subject>Toxicokinetics</subject><subject>Toxins</subject><issn>0730-7268</issn><issn>1552-8618</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2013</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp10E1LIzEcx_GwKGvtCvsKloAXPYzmYZJJjlLWByiK0EXxEjIz_9jodDImU9a-e6e29uYph3z4hvwQ-k3JGSWEnUNfnTFGxQ80okKwTEmq9tCIFJxkBZPqAB2m9EIIlVrrn-iA8VxIKegILWfh3Vfh1bfQ-yrh4HAXmlUZw8K3toca176bQ7tqMPRziAnbKoaUcOMd4NTbZ0jYt3i4w22Ia9LiBkJnY41dDM_4ZOr7eSiHVsKd7zy06fQX2ne2SXC0Pcfo3-Xf2eQ6m95d3UwuplnFVSEyIFwrVgNjmlbgHOHAc6JzqmrBS6qUtYXiouayJjavoCKOgdRU5qoswTE-RsebbhfD2xJSb17CMrbDk4ZypQmjxRAYo5ON-vxZBGe66Bc2rgwlZr2vGfY1630H-mcbXJYLqHfwa9ABZBvw3zew-jZkBrMNbr1PPbzvvI2vRha8EObh9sro6b140uLRXPMPE-CUlQ</recordid><startdate>201307</startdate><enddate>201307</enddate><creator>Cary, Tawnya L.</creator><creator>Karasov, William H.</creator><general>Blackwell Publishing Ltd</general><scope>BSCLL</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QO</scope><scope>7SN</scope><scope>7SS</scope><scope>7ST</scope><scope>7T7</scope><scope>7TK</scope><scope>7U7</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>K9.</scope><scope>P64</scope><scope>RC3</scope><scope>SOI</scope></search><sort><creationdate>201307</creationdate><title>Toxicokinetics of polybrominated diphenyl ethers across life stages in the northern leopard frog (Lithobates pipiens)</title><author>Cary, Tawnya L. ; Karasov, William H.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c3875-e03982de2291ceff03e3409418d53b188aa7835d36d0a4cec0f2e691648bbef23</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2013</creationdate><topic>Amphibian</topic><topic>Amphibians</topic><topic>Animals</topic><topic>Bioaccumulation</topic><topic>Elimination</topic><topic>Environmental Pollutants - metabolism</topic><topic>Environmental Pollutants - toxicity</topic><topic>Ethers</topic><topic>Flame retardants</topic><topic>Flame Retardants - metabolism</topic><topic>Flame Retardants - toxicity</topic><topic>Food chains</topic><topic>Food webs</topic><topic>Frogs</topic><topic>Halogenated Diphenyl Ethers - metabolism</topic><topic>Halogenated Diphenyl Ethers - toxicity</topic><topic>Kinetics</topic><topic>Metamorphosis</topic><topic>Metamorphosis, Biological</topic><topic>Persistent organic pollutant</topic><topic>Persistent organic pollutants</topic><topic>Pollutants</topic><topic>Polybrominated diphenyl ethers</topic><topic>Rana pipiens - metabolism</topic><topic>Toxicity</topic><topic>Toxicokinetics</topic><topic>Toxins</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Cary, Tawnya L.</creatorcontrib><creatorcontrib>Karasov, William H.</creatorcontrib><collection>Istex</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Biotechnology Research Abstracts</collection><collection>Ecology Abstracts</collection><collection>Entomology Abstracts (Full archive)</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Neurosciences Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>ProQuest Health & Medical Complete (Alumni)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Genetics Abstracts</collection><collection>Environment Abstracts</collection><jtitle>Environmental toxicology and chemistry</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Cary, Tawnya L.</au><au>Karasov, William H.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Toxicokinetics of polybrominated diphenyl ethers across life stages in the northern leopard frog (Lithobates pipiens)</atitle><jtitle>Environmental toxicology and chemistry</jtitle><addtitle>Environ Toxicol Chem</addtitle><date>2013-07</date><risdate>2013</risdate><volume>32</volume><issue>7</issue><spage>1631</spage><epage>1640</epage><pages>1631-1640</pages><issn>0730-7268</issn><eissn>1552-8618</eissn><abstract>Polybrominated diphenyl ethers (PBDEs), a class of flame retardants, are bioaccumulative toxins that can biomagnify in food webs. However, little is known about the toxicokinetics of total and congener‐specific BDEs in lower vertebrates. The authors exposed northern leopard frog (Lithobates (Rana) pipiens) tadpoles to diets containing DE‐71 (a pentabromodiphenyl ether mixture (0 ng/g as control, 71.4 ng/g, and 634 DE‐71 ng/g wet mass)) for 50 d, followed by a period of depuration during which they were fed only undosed (control) food. After 28 d, tadpoles eliminated over 94% of the ΣPBDEs from their tissues (t½ = 5.9 ± 1.9 d) with no significant differences in elimination rates for the predominant congeners. Elimination of BDE‐99 was independent of dose, indicating first‐order kinetics. It did not fit a biexponential model significantly better than a monoexponential model, indicating single‐compartment elimination. To compare developmental life‐stage kinetics following larval exposure, the authors collected individuals at the beginning and end of metamorphosis and at 70 d postmetamorphosis. During metamorphosis, total‐body residues per individual did not significantly change, implying little to no elimination. After 70 d, juvenile frogs eliminated 89.7% of the ΣPBDEs from their tissues, and BDE‐47 was eliminated at a faster rate (t½= 17.3 d) than BDE‐99 and BDE‐100 (t½ = 63.0 d and 69.3 d, respectively). Because the kinetics of PBDEs in L. pipiens differed among life stages, developmental life stage—especially for species that undergo metamorphosis—should be considered when determining the toxicity of persistent organic pollutants. Environ Toxicol Chem 2013;32:1631–1640. © 2013 SETAC</abstract><cop>United States</cop><pub>Blackwell Publishing Ltd</pub><pmid>23456651</pmid><doi>10.1002/etc.2215</doi><tpages>10</tpages></addata></record> |
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subjects | Amphibian Amphibians Animals Bioaccumulation Elimination Environmental Pollutants - metabolism Environmental Pollutants - toxicity Ethers Flame retardants Flame Retardants - metabolism Flame Retardants - toxicity Food chains Food webs Frogs Halogenated Diphenyl Ethers - metabolism Halogenated Diphenyl Ethers - toxicity Kinetics Metamorphosis Metamorphosis, Biological Persistent organic pollutant Persistent organic pollutants Pollutants Polybrominated diphenyl ethers Rana pipiens - metabolism Toxicity Toxicokinetics Toxins |
title | Toxicokinetics of polybrominated diphenyl ethers across life stages in the northern leopard frog (Lithobates pipiens) |
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