Test chamber investigation of the volatilization from source materials of brominated flame retardants and their subsequent deposition to indoor dust

Numerous studies have reported elevated concentrations of brominated flame retardants (BFRs) in dust from indoor micro‐environments. Limited information is available, however, on the pathways via which BFRs in source materials transfer to indoor dust. The most likely hypothesized pathways are (a) vo...

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Published inIndoor air Vol. 25; no. 4; pp. 393 - 404
Main Authors Rauert, C., Harrad, S., Stranger, M., Lazarov, B.
Format Journal Article
LanguageEnglish
Published England Blackwell Publishing Ltd 01.08.2015
John Wiley & Sons, Inc
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Summary:Numerous studies have reported elevated concentrations of brominated flame retardants (BFRs) in dust from indoor micro‐environments. Limited information is available, however, on the pathways via which BFRs in source materials transfer to indoor dust. The most likely hypothesized pathways are (a) volatilization from the source with subsequent partitioning to dust, (b) abrasion of the treated product, transferring microscopic fibers or particles to the dust (c) direct uptake to dust via contact between source and dust. This study reports the development and application of an in‐house test chamber for investigating BFR volatilization from source materials and subsequent partitioning to dust. The performance of the chamber was evaluated against that of a commercially available chamber, and inherent issues with such chambers were investigated, such as loss due to sorption of BFRs to chamber surfaces (so‐called sink effects). The partitioning of polybrominated diphenyl ethers to dust, post‐volatilization from an artificial source was demonstrated, while analysis in the test chamber of a fabric curtain treated with the hexabromocyclododecane formulation, resulted in dust concentrations exceeding substantially those detected in the dust pre‐experiment. These results provide the first experimental evidence of BFR volatilization followed by deposition to dust.
Bibliography:ark:/67375/WNG-Q42F7BCX-J
ArticleID:INA12151
Table S1. Average ± s.d. and (minimum, maximum) starting concentrations of BFRs (ng/g) in bulk dust used for chamber experiments from 6 and 7 repeat analyses respectively. Table S2. Average concentrations (ng/g) in 7 analyses of SRM 2585 and the reported certified PBDE (Stapleton et al., ) and indicative HBCD values (Keller et al., ). Table S3. BFR mass collected on PUFs with different air sampling train lengths and analytes recovered (%) by heating the chamber post experiment. Table S4. BFR recovery (%) on chamber exit PUF achieved by heating UoB chamber post-experiment to 80°C for 6 h.
istex:EC4BBCF6321EDFF6017CD80A93A6BC8841EB5DF9
European Union Seventh Framework Program - No. FP7/2007-2013; No. 264600
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ISSN:0905-6947
1600-0668
1600-0668
DOI:10.1111/ina.12151