Literature DB >> 21239062

Concentrations and loadings of polybrominated diphenyl ethers in dust from low-income households in California.

Lesliam Quirós-Alcalá1, Asa Bradman, Marcia Nishioka, Martha E Harnly, Alan Hubbard, Thomas E McKone, Brenda Eskenazi.   

Abstract

California residents may experience the highest polybrominated diphenyl ether (PBDE) flame retardant exposures in the United States, the nation with the highest body burdens worldwide. It is hypothesized that Californians' high exposures are due to the state's strict furniture flammability standards. Ingestion of PBDE-contaminated dust, to which children may be particularly susceptible, is a dominant exposure pathway. Low-income populations may also face disparately high exposures due to the presence of older, deteriorated or poorly manufactured furniture treated with PBDEs. We collected up to two dust samples per home (54 samples total), several days apart, from low-income California households in the urban community of Oakland (n=13 homes) and the agricultural community of Salinas (n=15 homes). We measured BDE-47, BDE-99 and BDE-100, the major constituents of the penta-PBDE flame retardant formulation commonly used in furniture. All three PBDE congeners were detected in every sample with concentrations (loadings) ranging from 185 to 126,000ng/g (621-264,000ng/m(2)), 367-220,000ng/g (1550-457,000ng/m(2)), and 84-41,100ng/g (257-85,700ng/m(2)) for BDE-47, BDE-99 and BDE-100, respectively. Median concentrations (loadings) observed in Salinas homes for BDE-47, BDE-99 and BDE-100 were 3100ng/g (10,800ng/m(2)), 5480ng/g (19,500ng/m(2)), and 1060ng/g (3810ng/m(2)), respectively, and in Oakland homes 2780ng/g (10,700ng/m(2)), 4450ng/g (19,100ng/m(2)), and 1050ng/g (4000ng/m(2)), respectively. Maximum concentrations for BDE-47 and BDE-99 are the highest reported to date. Indoor concentrations and loadings did not significantly differ between communities; concentrations and loadings were strongly correlated between collections for all three congeners (Spearman rho=0.79-0.97, p<0.002). We estimated non-dietary ingestion of each congener for one child in each home (n=28 children) and found that estimated intake for BDE-47 and BDE-99 exceeded the U.S. Environmental Protection Agency's recommended chronic reference dose for three and five children, respectively. Children's estimated intake via dust ranged from 1.0 to 599ng/kg/day, 2.0-1065ng/kg/day and 0.5-196ng/kg/day for BDE-47, BDE-99 and BDE-100, respectively. In order to mitigate these exposures, future research must address the factors that contribute to PBDE exposures in low-income homes.
Copyright © 2010 Elsevier Ltd. All rights reserved.

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Year:  2011        PMID: 21239062     DOI: 10.1016/j.envint.2010.12.003

Source DB:  PubMed          Journal:  Environ Int        ISSN: 0160-4120            Impact factor:   9.621


  11 in total

1.  Factors associated with serum polybrominated diphenyl ether (PBDE) levels among school-age children in the CHAMACOS cohort.

Authors:  Asa Bradman; Rosemary Castorina; Andreas Sjödin; Laura Fenster; Richard S Jones; Kim G Harley; Jonathan Chevrier; Nina T Holland; Brenda Eskenazi
Journal:  Environ Sci Technol       Date:  2012-06-12       Impact factor: 9.028

2.  Polybrominated diphenyl ethers in residential dust: sources of variability.

Authors:  Todd P Whitehead; F Reber Brown; Catherine Metayer; June-Soo Park; Monique Does; Myrto X Petreas; Patricia A Buffler; Stephen M Rappaport
Journal:  Environ Int       Date:  2013-04-27       Impact factor: 9.621

3.  Flame retardants and their metabolites in the homes and urine of pregnant women residing in California (the CHAMACOS cohort).

Authors:  Rosemary Castorina; Craig Butt; Heather M Stapleton; Dylan Avery; Kim G Harley; Nina Holland; Brenda Eskenazi; Asa Bradman
Journal:  Chemosphere       Date:  2017-03-22       Impact factor: 7.086

4.  Determinants of serum polybrominated diphenyl ether (PBDE) levels among pregnant women in the CHAMACOS cohort.

Authors:  Rosemary Castorina; Asa Bradman; Andreas Sjödin; Laura Fenster; Richard S Jones; Kim G Harley; Ellen A Eisen; Brenda Eskenazi
Journal:  Environ Sci Technol       Date:  2011-07-13       Impact factor: 9.028

5.  Polybrominated diphenyl ether (PBDE) concentrations and resulting exposure in homes in California: relationships among passive air, surface wipe and dust concentrations, and temporal variability.

Authors:  D H Bennett; R E Moran; X May Wu; N S Tulve; M S Clifton; M Colón; W Weathers; A Sjödin; R Jones; I Hertz-Picciotto
Journal:  Indoor Air       Date:  2014-06-25       Impact factor: 5.770

6.  A comparison of PBDE serum concentrations in Mexican and Mexican-American children living in California.

Authors:  Brenda Eskenazi; Laura Fenster; Rosemary Castorina; Amy R Marks; Andreas Sjödin; Lisa Goldman Rosas; Nina Holland; Armando Garcia Guerra; Lizbeth Lopez-Carillo; Asa Bradman
Journal:  Environ Health Perspect       Date:  2011-04-15       Impact factor: 9.031

7.  Hand-me-down hazard: flame retardants in discarded foam products.

Authors:  Kellyn S Betts
Journal:  Environ Health Perspect       Date:  2015-03       Impact factor: 9.031

8.  Novel and high volume use flame retardants in US couches reflective of the 2005 PentaBDE phase out.

Authors:  Heather M Stapleton; Smriti Sharma; Gordon Getzinger; P Lee Ferguson; Michelle Gabriel; Thomas F Webster; Arlene Blum
Journal:  Environ Sci Technol       Date:  2012-11-28       Impact factor: 9.028

9.  After the PBDE phase-out: a broad suite of flame retardants in repeat house dust samples from California.

Authors:  Robin E Dodson; Laura J Perovich; Adrian Covaci; Nele Van den Eede; Alin C Ionas; Alin C Dirtu; Julia Green Brody; Ruthann A Rudel
Journal:  Environ Sci Technol       Date:  2012-11-28       Impact factor: 9.028

10.  Semivolatile organic compounds in homes: strategies for efficient and systematic exposure measurement based on empirical and theoretical factors.

Authors:  Robin E Dodson; David E Camann; Rachel Morello-Frosch; Julia G Brody; Ruthann A Rudel
Journal:  Environ Sci Technol       Date:  2014-12-09       Impact factor: 9.028

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