TY - JOUR
T1 - Children's Exposure to Brominated Flame Retardants in the Home
T2 - The TESIE Study
AU - Hoffman, Kate
AU - Tang, Xuening
AU - Cooper, Ellen M
AU - Hammel, Stephanie C
AU - Sjodin, Andreas
AU - Phillips, Allison L
AU - Webster, Thomas F
AU - Stapleton, Heather M
N1 - Copyright © 2024 Elsevier Ltd. All rights reserved.
PY - 2024/7/1
Y1 - 2024/7/1
N2 - Due to differences in chemical properties and half-lives, best practices for exposure assessment may differ for legacy versus novel brominated flame retardants (BFRs). Our objective was to identify the environment matrix that best predicted biomarkers of children's BFR exposures. Paired samples were collected from children, aged 3-6 years, and their homes including dust, a small piece of polyurethane foam from the furniture, and a handwipe and wristband from each child. Biological samples collected included serum, which was analyzed for 11 polybrominated diphenyl ethers (PBDEs), and urine, which was analyzed for tetrabromobenzoic acid (TBBA), a metabolite of 2-ethylhexyl-2,3,4,5-tetrabromobenzoate (EH-TBB). Significant positive correlations were typically observed between BFRs measured in dust, handwipes and wristbands, though wristbands and handwipes tended to be more strongly correlated with one another than with dust. PBDEs, EH-TBB and BEH-TEBP were detected in 30% of the sofa foam samples, suggesting that the foam was treated with PentaBDE or Firemaster® 550/600 (FM 550/600). PBDEs were detected in all serum samples and TBBA was detected in 43% of urine samples. Statistically significant positive correlations were observed between the environmental samples and serum for PBDEs. Urinary TBBA was 6.86 and 6.58 times more likely to be detected among children in the highest tertile of EH-TBB exposure for handwipes and wristbands, respectively (95 % CI: 2.61, 18.06 and 1.43, 30.05 with p<0.001 and 0.02, respectively). The presence of either PentaBDE or FM 550/600 in furniture was also associated with significantly higher levels of these chemicals in dust, handwipes and serum (for PBDEs) and more frequent detection of TBBA in urine (p=0.13). Our results suggest children are exposed to a range of BFRs in the home, some of which likely originate from residential furniture, and that silicone wristbands are a practical tool for evaluating external exposure to both the legacy and novel BFRs.
AB - Due to differences in chemical properties and half-lives, best practices for exposure assessment may differ for legacy versus novel brominated flame retardants (BFRs). Our objective was to identify the environment matrix that best predicted biomarkers of children's BFR exposures. Paired samples were collected from children, aged 3-6 years, and their homes including dust, a small piece of polyurethane foam from the furniture, and a handwipe and wristband from each child. Biological samples collected included serum, which was analyzed for 11 polybrominated diphenyl ethers (PBDEs), and urine, which was analyzed for tetrabromobenzoic acid (TBBA), a metabolite of 2-ethylhexyl-2,3,4,5-tetrabromobenzoate (EH-TBB). Significant positive correlations were typically observed between BFRs measured in dust, handwipes and wristbands, though wristbands and handwipes tended to be more strongly correlated with one another than with dust. PBDEs, EH-TBB and BEH-TEBP were detected in 30% of the sofa foam samples, suggesting that the foam was treated with PentaBDE or Firemaster® 550/600 (FM 550/600). PBDEs were detected in all serum samples and TBBA was detected in 43% of urine samples. Statistically significant positive correlations were observed between the environmental samples and serum for PBDEs. Urinary TBBA was 6.86 and 6.58 times more likely to be detected among children in the highest tertile of EH-TBB exposure for handwipes and wristbands, respectively (95 % CI: 2.61, 18.06 and 1.43, 30.05 with p<0.001 and 0.02, respectively). The presence of either PentaBDE or FM 550/600 in furniture was also associated with significantly higher levels of these chemicals in dust, handwipes and serum (for PBDEs) and more frequent detection of TBBA in urine (p=0.13). Our results suggest children are exposed to a range of BFRs in the home, some of which likely originate from residential furniture, and that silicone wristbands are a practical tool for evaluating external exposure to both the legacy and novel BFRs.
KW - Children's exposure
KW - furniture foam
KW - Silicone wristbands
KW - Flame Retardants
KW - hand wipes
KW - Air Pollution, Indoor/statistics & numerical data
KW - Environmental Monitoring
KW - Humans
KW - Child, Preschool
KW - Male
KW - Housing
KW - Environmental Pollutants/urine
KW - Environmental Exposure/statistics & numerical data
KW - Halogenated Diphenyl Ethers/blood
KW - Female
KW - Dust/analysis
KW - Child
KW - Flame Retardants/analysis
KW - eksponering
KW - Flammehæmmere
KW - støv
U2 - 10.1016/j.envpol.2024.124110
DO - 10.1016/j.envpol.2024.124110
M3 - Journal article
C2 - 38723705
SN - 0269-7491
VL - 352
JO - Environmental Pollution
JF - Environmental Pollution
ER -