Literature DB >> 8887438

Toxic equivalency factors of polybrominated dibenzo-p-dioxin, dibenzofuran, biphenyl, and polyhalogenated diphenyl ether congeners based on rainbow trout early life stage mortality.

M W Hornung1, E W Zabel, R E Peterson.   

Abstract

Polybrominated and polychlorinated biphenyls (PBBs/PCBs), dibenzo-p-dioxins (PBDDs/PCDDs), dibenzofurans (PBDFs/PCDFs), and diphenyl ethers (PBDEs/PCDEs) are persistent, lipophilic environmental contaminants that may pose a risk to fish early life stage survival. To determine this potential risk, a rainbow trout early life stage mortality bioassay was used in which the potency of individual polybrominated chemicals was compared to the potency of the most potent polychlorinated chemical in these classes, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Following injection of newly fertilized rainbow trout eggs, fish-specific toxic equivalency factors (TEFs) were calculated as the molar ratio of TCDD LD50 to brominated compound LD50. Signs of toxicity were identical to those produced by polychlorinated TCDD-like chemicals and included yolk sac edema, pericardial edema, multifocal hemorrhages, reduced growth, and craniofacial malformations. Polybrominated dibenzo-p-dioxins, dibenzofurans, and biphenyls exhibited decreased potency with increased bromine substitution. Only 2,3,7,8-TBDD was more potent than 2,3,7,8-TCDD, whereas other polybrominated dibenzo-p-dioxins were equipotent or less potent than identically substituted polychlorinated dibenzo-p-dioxins in this assay. Although two PBDF congeners were equipotent to identically substituted PCDFs, 2,3,7,8-TBDF was 9-fold more potent than 2,3,7,8-TCDF. Both 3,3',4,4'-TBB and 3,3',4,4',5,5'-HxBB were 10-fold more potent than identically substituted polychlorinated biphenyls. The halogenated diphenyl ethers and di-ortho polybrominated biphenyls were inactive in this assay. Thus, in this in vivo assay the polybrominated and polychlorinated TCDD-like chemicals were not always equally potent. To assess the risk posed by mixtures of these chemicals to feral fish populations, fish-specific TEFs for both polybrominated and polychlorinated chemicals should be used.

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Year:  1996        PMID: 8887438     DOI: 10.1006/taap.1996.0217

Source DB:  PubMed          Journal:  Toxicol Appl Pharmacol        ISSN: 0041-008X            Impact factor:   4.219


  8 in total

Review 1.  Reproductive and developmental toxicity of dioxin in fish.

Authors:  Tisha C King-Heiden; Vatsal Mehta; Kong M Xiong; Kevin A Lanham; Dagmara S Antkiewicz; Alissa Ganser; Warren Heideman; Richard E Peterson
Journal:  Mol Cell Endocrinol       Date:  2011-09-21       Impact factor: 4.102

2.  Long-term disruption of growth, reproduction, and behavior after embryonic exposure of zebrafish to PAH-spiked sediment.

Authors:  Caroline Vignet; Marie-Hélène Devier; Karyn Le Menach; Laura Lyphout; Jérémy Potier; Jérôme Cachot; Hélène Budzinski; Marie-Laure Bégout; Xavier Cousin
Journal:  Environ Sci Pollut Res Int       Date:  2014-03-23       Impact factor: 4.223

3.  Formation of polybrominated dibenzofurans (PBDFs) after heating of a salmon sample spiked with decabromodiphenyl ether (BDE-209).

Authors:  Walter Vetter; Paul Bendig; Marina Blumenstein; Florian Hägele; Peter A Behnisch; Abraham Brouwer
Journal:  Environ Sci Pollut Res Int       Date:  2014-07-22       Impact factor: 4.223

4.  Polybrominated dibenzo-p-dioxins, dibenzofurans, and biphenyls: inclusion in the toxicity equivalency factor concept for dioxin-like compounds.

Authors:  Martin van den Berg; Michael S Denison; Linda S Birnbaum; Michael J Devito; Heidelore Fiedler; Jerzy Falandysz; Martin Rose; Dieter Schrenk; Stephen Safe; Chiharu Tohyama; Angelika Tritscher; Mats Tysklind; Richard E Peterson
Journal:  Toxicol Sci       Date:  2013-03-14       Impact factor: 4.849

5.  Formation of polychlorinated diphenyl ethers from condensation of chlorophenols with chlorobenzenes.

Authors:  Wenxia Liu; Minghui Zheng; Wenbin Liu; Xiaodong Ma; Yong Qian; Bing Zhang
Journal:  Environ Sci Pollut Res Int       Date:  2008-01       Impact factor: 4.223

6.  Developmental exposure to a complex PAH mixture causes persistent behavioral effects in naive Fundulus heteroclitus (killifish) but not in a population of PAH-adapted killifish.

Authors:  D R Brown; J M Bailey; A N Oliveri; E D Levin; R T Di Giulio
Journal:  Neurotoxicol Teratol       Date:  2015-11-06       Impact factor: 3.763

Review 7.  Toxic equivalency factors (TEFs) for PCBs, PCDDs, PCDFs for humans and wildlife.

Authors:  M Van den Berg; L Birnbaum; A T Bosveld; B Brunström; P Cook; M Feeley; J P Giesy; A Hanberg; R Hasegawa; S W Kennedy; T Kubiak; J C Larsen; F X van Leeuwen; A K Liem; C Nolt; R E Peterson; L Poellinger; S Safe; D Schrenk; D Tillitt; M Tysklind; M Younes; F Waern; T Zacharewski
Journal:  Environ Health Perspect       Date:  1998-12       Impact factor: 9.031

Review 8.  Facing the challenge of data transfer from animal models to humans: the case of persistent organohalogens.

Authors:  Alexander Suvorov; Larissa Takser
Journal:  Environ Health       Date:  2008-11-13       Impact factor: 5.984

  8 in total

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