Brominated flame retardants in children's toys: concentration, composition, and children's exposure and risk assessment.

Brominated flame retardants (BFRs), including polybrominated diphenyl ethers (PBDEs), 1,2-bis(2,4,6-tribromophenoxy)ethane (BTBPE), decabromodiphenyl ethane (DBDPE), and polybrominated biphenyls (PBBs) were found in children's toys purchased from South China. The median BFR concentrations in the hard plastic toys were 53,000, 5540 ng/g, 101.1 ng/g, and 27.9 ng/g, fortotal PBDEs, DBDPE, BTBPE, and PBBs, respectively,which were notably higher than values in other toys. The PBDE concentrations were below the threshold limit (1000 ppm) required bythe European Commission's Restriction of Hazardous Substances (RoHS) and Waste Electrical and Electronic Equipment (WEEE) directives in all of the toys, except for one hard plastic toy with a total PBDE concentration of 5,344,000 ng/g. The BFR profiles in the toys were consistent with the patterns of their current production and consumption in China, where PBDEs, specifically decaBDE product, were the dominant BFR, followed by the emerging DBDPE. The relatively high concentrations of octa- and nonaBDEs in the foam toys and the results of principal component analysis (PCA) may suggest the decomposition of highly brominated BDEs during the manufacturing processes of the toys. Daily total PBDE exposures associated with toys via inhalation, mouthing, dermal contact, and oral ingestion ranged from 82.6 to 8992 pg/kg bw-day for children of 3 months to 14 years of age. Higher exposures, predominantly contributed through the mouthing pathway, were observed for infants and toddlers than for the other subgroups. In most cases, children's BFR exposure via the toys likely accounts for a small proportion of their daily BFR exposure, and the hazard quotients for noncancer risk evaluation were far below 1. To the author's knowledge, this is the first study to examine the concentrations of BFRs in toys, and the potential exposures to children.

[1]  G. O. Thomas,et al.  Different Levels of Polybrominated Diphenyl Ethers (PBDEs) and Chlorinated Compounds in Breast Milk from Two U.K. Regions , 2004, Environmental health perspectives.

[2]  Ulrika Fridén,et al.  Identification of the flame retardant decabromodiphenyl ethane in the environment. , 2004, Environmental science & technology.

[3]  Kellyn Betts,et al.  Does a key PBDE break down in the environment? , 2008, Environmental science & technology.

[4]  B. Mai,et al.  Assessment of human exposure to polybrominated diphenyl ethers in China via fish consumption and inhalation. , 2007, Environmental science & technology.

[5]  O. Jann,et al.  Emissions of organophosphate and brominated flame retardants from selected consumer products and building materials , 2003 .

[6]  Xiao-Jun Luo,et al.  Occurrence of brominated flame retardants other than polybrominated diphenyl ethers in environmental and biota samples from southern China. , 2009, Chemosphere.

[7]  Ronald A Hites,et al.  Polybrominated diphenyl ethers in the environment and in people: a meta-analysis of concentrations. , 2004, Environmental science & technology.

[8]  Matthew Lorber,et al.  Exposure of Americans to polybrominated diphenyl ethers , 2008, Journal of Exposure Science and Environmental Epidemiology.

[9]  D. Paustenbach,et al.  Assessment of polybrominated diphenyl ether exposures and health risks associated with consumption of southern Mississippi catfish. , 2008, Environmental science & technology.

[10]  P. B. Larsen,et al.  Polybrominated diphenyl ethers: occurrence, dietary exposure, and toxicology. , 2001, Environmental health perspectives.

[11]  Robert C Hale,et al.  Potential role of fire retardant-treated polyurethane foam as a source of brominated diphenyl ethers to the US environment. , 2002, Chemosphere.

[12]  Xiaojun Luo,et al.  Polybrominated diphenyl ethers in birds of prey from Northern China. , 2007, Environmental science & technology.

[13]  Heather M Stapleton,et al.  Measurement of polybrominated diphenyl ethers on hand wipes: estimating exposure from hand-to-mouth contact. , 2008, Environmental science & technology.

[14]  S. Olin,et al.  Similarities and differences between children and adults: implications for risk assessment , 1992 .

[15]  M. Ikonomou,et al.  Photochemistry of a major commercial polybrominated diphenyl ether flame retardant congener: 2,2',4,4',5,5'-hexabromodiphenyl ether (BDE153). , 2006, Environment international.

[16]  M. L. La Guardia,et al.  Evidence of debromination of decabromodiphenyl ether (BDE-209) in biota from a wastewater receiving stream. , 2007, Environmental science & technology.

[17]  Mats Tysklind,et al.  Photolytic debromination of decabromodiphenyl ether (BDE 209). , 2004, Environmental science & technology.

[18]  Harvey J Clewell,et al.  Exposure assessment and risk characterization for perfluorooctanoate in selected consumer articles. , 2005, Environmental science & technology.

[19]  Yong Ran,et al.  In- and outdoor sources of polybrominated diphenyl ethers and their human inhalation exposure in Guangzhou, China , 2008 .

[20]  Xiaojun Luo,et al.  Brominated flame retardants, polychlorinated biphenyls, and organochlorine pesticides in captive giant panda (ailuropoda melanoleuca) and red panda (Ailurus fulgens) from China. , 2008, Environmental science & technology.

[21]  L Claudio,et al.  Pesticides and inner-city children: exposures, risks, and prevention. , 1999, Environmental health perspectives.

[22]  H. Stapleton,et al.  In vivo and in vitro debromination of decabromodiphenyl ether (BDE 209) by juvenile rainbow trout and common carp. , 2006, Environmental science & technology.

[23]  S. Sakai,et al.  Degradation pathways of decabromodiphenyl ether during hydrothermal treatment. , 2007, Chemosphere.

[24]  Stuart Harrad,et al.  Concentrations of polychlorinated biphenyls in indoor air and polybrominated diphenyl ethers in indoor air and dust in Birmingham, United Kingdom: implications for human exposure. , 2006, Environmental science & technology.