Literature DB >> 18853808

Alternate and new brominated flame retardants detected in U.S. house dust.

Heather M Stapleton1, Joseph G Allen, Shannon M Kelly, Alex Konstantinov, Susan Klosterhaus, Deborah Watkins, Michael D McClean, Thomas F Webster.   

Abstract

Due to the voluntary withdrawals and/or bans on the use of two polybrominated diphenyl ether (PBDE) commercial mixtures, an increasing number of alternate flame retardant chemicals are being introduced in commercial applications. To determine if these alternate BFRs are present in indoor environments, we analyzed dust samples collected from 19 homes in the greater Boston, MA area during 2006. Using pure and commercial standards we quantified the following brominated flame retardant chemicals using GC/ECNI-MS methods: hexabromocyclododecane (sigma HBCD), bis(2,4,6,-tribromphenoxy)ethane (BTBPE), decabromodiphenyl ethane (DBDPE), and the brominated components found in Firemaster 550 (FM 550): 2-ethylhexyl 2,3,4,5-tetrabromobenzoate (TBB) and (2-ethylhexyl)tetrabromophthalate (TBPH), the latter compound being a brominated analogue of di(2-ethylhexyl)phthalate (DEHP). The concentrations of all compounds were log-normally distributed and the largest range in concentrations was observed for HBCD (sum of all isomers), with concentrations ranging from <4.5 ng/g to a maximum of 130,200 ng/g with a median value of 230 ng/g. BTBPE ranged from 1.6 to 789 ng/g with a median value of 30 ng/g and DBDPE ranged from <10.0 to 11,070 ng/g with a median value of 201 ng/g. Of the FM 550 components, TBB ranged from <6.6 to 15,030 ng/g with a median value of 133 ng/g; whereas TBPH ranged from 1.5 to 10,630 ng/g with a median value of 142 ng/g. Furthermore, the ratio of TBB/TBPH present in the dust samples ranged from 0.05 to 50 (average 4.4), varying considerably from the ratio observed in the FM 550 commercial mixture (4:1 by mass), suggesting different sources with different chemical compositions, and/or differential fate and transport within the home. Analysis of paired dust samples collected from different rooms in the same home suggests HBCD, TBB, and TBPH are higher in dust from the main living area compared to dust collected in bedrooms; however, BTBPE and DBDPE levels were comparable between rooms. This study highlights the fact that numerous types of brominated flame retardants are present in indoor environments, raising questions about exposure to mixtures of these contaminants.

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Year:  2008        PMID: 18853808     DOI: 10.1021/es801070p

Source DB:  PubMed          Journal:  Environ Sci Technol        ISSN: 0013-936X            Impact factor:   9.028


  102 in total

1.  Non-PBDE halogenated flame retardants in Canadian indoor house dust: sampling, analysis, and occurrence.

Authors:  Xinghua Fan; Cariton Kubwabo; Pat E Rasmussen; Fang Wu
Journal:  Environ Sci Pollut Res Int       Date:  2016-01-16       Impact factor: 4.223

2.  Evaluating the Use of Silicone Wristbands To Measure Personal Exposure to Brominated Flame Retardants.

Authors:  Stephanie C Hammel; Allison L Phillips; Kate Hoffman; Heather M Stapleton
Journal:  Environ Sci Technol       Date:  2018-10-02       Impact factor: 9.028

3.  Activation of Human Peroxisome Proliferator-Activated Nuclear Receptors (PPARγ1) by Semi-Volatile Compounds (SVOCs) and Chemical Mixtures in Indoor Dust.

Authors:  Mingliang Fang; Thomas F Webster; Heather M Stapleton
Journal:  Environ Sci Technol       Date:  2015-07-30       Impact factor: 9.028

4.  Geographical distribution of non-PBDE-brominated flame retardants in mussels from Asian coastal waters.

Authors:  Tomohiko Isobe; Shohei P Ogawa; Karri Ramu; Agus Sudaryanto; Shinsuke Tanabe
Journal:  Environ Sci Pollut Res Int       Date:  2012-08-09       Impact factor: 4.223

5.  Levels of non-polybrominated diphenyl ether brominated flame retardants in residential house dust samples and fire station dust samples in California.

Authors:  F Reber Brown; Todd P Whitehead; June-Soo Park; Catherine Metayer; Myrto X Petreas
Journal:  Environ Res       Date:  2014-09-27       Impact factor: 6.498

6.  Estimation of tetrabromobisphenol A (TBBPA) percutaneous uptake in humans using the parallelogram method.

Authors:  Gabriel A Knudsen; Michael F Hughes; Katelyn L McIntosh; J Michael Sanders; Linda S Birnbaum
Journal:  Toxicol Appl Pharmacol       Date:  2015-09-24       Impact factor: 4.219

7.  Dermal disposition of Tetrabromobisphenol A Bis(2,3-dibromopropyl) ether (TBBPA-BDBPE) using rat and human skin.

Authors:  Gabriel A Knudsen; Michael F Hughes; Linda S Birnbaum
Journal:  Toxicol Lett       Date:  2018-11-24       Impact factor: 4.372

8.  Effects of Prenatal Exposure to a Mixture of Organophosphate Flame Retardants on Placental Gene Expression and Serotonergic Innervation in the Fetal Rat Brain.

Authors:  Kylie D Rock; Genevieve St Armour; Brian Horman; Allison Phillips; Matthew Ruis; Allison K Stewart; Dereje Jima; David C Muddiman; Heather M Stapleton; Heather B Patisaul
Journal:  Toxicol Sci       Date:  2020-07-01       Impact factor: 4.849

9.  From the Cover: Exposure to an Environmentally Relevant Mixture of Brominated Flame Retardants Decreased p-β-Cateninser675 Expression and Its Interaction With E-Cadherin in the Mammary Glands of Lactating Rats.

Authors:  Elham Dianati; Michael G Wade; Barbara F Hales; Bernard Robaire; Isabelle Plante
Journal:  Toxicol Sci       Date:  2017-09-01       Impact factor: 4.849

10.  House dust concentrations of organophosphate flame retardants in relation to hormone levels and semen quality parameters.

Authors:  John D Meeker; Heather M Stapleton
Journal:  Environ Health Perspect       Date:  2010-03       Impact factor: 9.031

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