Mammalian toxicology and human exposures to the flame retardant 2,2',6,6'-tetrabromo-4,4'-isopropylidenediphenol (TBBPA): implications for risk assessment

被引:101
作者
Colnot, Thomas [1 ]
Kacew, Sam [2 ]
Dekant, Wolfgang [3 ]
机构
[1] CIS Toxicol, Osorno, Chile
[2] Univ Ottawa, Ottawa, ON, Canada
[3] Univ Wurzburg, Dept Toxicol, D-97078 Wurzburg, Germany
关键词
Endocrine toxicity; Exposure assessment; Repeated-dose toxicity; Role of in vitro assays; Two-generation studies; Toxicokinetics; Bioaccumulation; TETRABROMOBISPHENOL-A TBBPA; THYROID-HORMONE RECEPTOR; HALOGENATED BISPHENOL-A; FREE-RADICAL FORMATION; MODEL-DERIVED RISKS; IN-VITRO; URINARY-BLADDER; WISTAR RATS; CELL-DEATH; TOXICOKINETICS;
D O I
10.1007/s00204-013-1180-8
中图分类号
R99 [毒物学(毒理学)];
学科分类号
100405 ;
摘要
The compound 2,2',6,6'-Tetrabromo-4,4'-isopropylidenediphenol (tetrabromobisphenol A, TBBPA) is used as a reactive and additive flame retardant. This review evaluates the mammalian toxicology of TBBPA and summarizes recent human exposure and risk assessments. TBBPA has a low potential for systemic or reproductive toxicity, and no-observed-adverse-effect-levels were greater than 1,000 mg/kg body weight (bw)/day in a 90-day oral toxicity study, a developmental toxicity study and a two-generation reproductive and developmental toxicity study. Some interactions of TBBPA with hormone-mediated pathways were noted in vitro; however, when studied in vivo, TBBPA did not produce adverse effects that might be considered to be related to disturbances in the endocrine system. Therefore, in accordance with internationally accepted definitions, TBBPA should not be considered an "endocrine disruptor." Furthermore, TBBPA is rapidly excreted in mammals and therefore does not have a potential for bioaccumulation. Measured concentrations of TBBPA in house dust, human diet and human serum samples are very low. Daily intakes of TBBPA in humans were estimated to not exceed a few ng/kg bw/day. Due to the low exposures and the low potential for toxicity, margins of exposures for TBBPA in the human population were between 6 x 10(4) (infants) to 6 x 10(7) (adults). Exposures of the general population are also well below the derived-no-effect-levels derived for endpoints of potential concern in REACH.
引用
收藏
页码:553 / 573
页数:21
相关论文
共 97 条
  • [21] Determinants of Plasma Concentrations of Perfluorooctanesulfonate and Brominated Organic Compounds in Nunavik Inuit Adults (Canada)
    Dallaire, Renee
    Ayotte, Pierre
    Pereg, Daria
    Dery, Serge
    Dumas, Pierre
    Langlois, Eric
    Dewailly, Eric
    [J]. ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2009, 43 (13) : 5130 - 5136
  • [22] de Winter-Sorkina R, 2003, 313050012003 RIVM
  • [23] THE OBESOGEN HYPOTHESIS: A SHIFT OF FOCUS FROM THE PERIPHERY TO THE HYPOTHALAMUS
    Decherf, Stephanie
    Demeneix, Barbara A.
    [J]. JOURNAL OF TOXICOLOGY AND ENVIRONMENTAL HEALTH-PART B-CRITICAL REVIEWS, 2011, 14 (5-7): : 423 - 448
  • [24] Disruption of thyroid hormone-dependent hypothalamic set-points by environmental contaminants
    Decherf, Stephanie
    Seugnet, Isabelle
    Fini, Jean-Baptiste
    Clerget-Froidevaux, Marie-Stephanie
    Demeneix, Barbara A.
    [J]. MOLECULAR AND CELLULAR ENDOCRINOLOGY, 2010, 323 (02) : 172 - 182
  • [25] Urothelial carcinogenesis in the urinary bladder of male rats treated with muraglitazar, a PPAR α/γ agonist:: Evidence for urolithiasis as the inciting event in the mode of action
    Dominick, Mark A.
    White, Melvin R.
    Sanderson, Thomas P.
    Van Vleet, Terry
    Cohen, Samuel M.
    Arnold, Lora E.
    Cano, Marty
    Tannehill-Gregg, Sarah
    Moehlenkamp, Jeffrey D.
    Waites, Crystal R.
    Schilling, Beth E.
    [J]. TOXICOLOGIC PATHOLOGY, 2006, 34 (07) : 903 - 920
  • [26] Determination of brominated flame retardants in food by LC-MS/MS: diastereoisomer-specific hexabromocyclododecane and tetrabromobisphenol A
    Driffield, Malcolm
    Harmer, Nick
    Bradley, Emma
    Fernandes, Alwyn R.
    Rose, Martin
    Mortimer, David
    Dicks, Pamela
    [J]. FOOD ADDITIVES AND CONTAMINANTS PART A-CHEMISTRY ANALYSIS CONTROL EXPOSURE & RISK ASSESSMENT, 2008, 25 (07): : 895 - 903
  • [27] EC-CSTEE, 2001, 22 CSTEE PLEN M BRUS
  • [28] EC-EFSA, 2012, EFSA J, V10, P2578
  • [29] EC-SCENIHR, 2005, SCENIHR ITS 17 PLEN
  • [30] EC-SCHER, 2005, SCHER 7 PLEN 23 SEP