Hexabromocyclododecanes in indoor dust from Canada, the United Kingdom, and the United States.
alpha-, beta-, and gamma-hexabromocyclododecane diastereomers (HBCDs) were measured in house dust from Birmingham, U.K. (n=31, median concentration=730 ng sigmaHBCDs g(-1)); Amarillo/Austin, TX (n=13, 390 ng g(-1)); and Toronto, Canada (n=8, 640 ng g(-1)). Concentrations in dust (n=6, 650 ng g(-1)) from U.K. offices were within the range for UK homes. Concentrations from each country were statistically indistinguishable. In one UK house dust sample, 110,000 ng g(-1) was recorded-the highest recorded in indoor dust to date. While upper bound average U.K. dietary exposures for adults and toddlers, respectively, are 413 and 240 ng sigmaHBCDs day(-1), U.K. adults and toddlers daily ingesting, respectively, 50 and 200 mg of dust contaminated at the 95th percentile concentration are exposed, respectively, to 1100 and 4400 ng sigmaHBCDs day(-1). Normalized to body weight, this high-end exposure scenario estimate for toddlers is within the range reported elsewhere for occupationally exposed adults. While in commercial formulations gamma-HBCD predominates (>80%), alpha-HBCD in dust constitutes 14-67% of sigmaHBCDs (average 32%). Hence the predominance of the alpha-diastereomer in humans may arise partly from dust ingestion, and not solely to in vivo metabolism (when alpha-HBCD is formed from bioisomerization of other diastereomers), or dietary exposure (where alpha-HBCD predominates in most foodstuffs).
Abdallah Mohamed
Abou-Elwafa
AE
Division of Environmental Health and Risk Management, School of Geography, Earth and Environmental Sciences, University of Birmingham, Birmingham, B15 2TT, United Kingdom.
Harrad
Stuart
S
Ibarra
Catalina
C
Diamond
Miriam
M
Melymuk
Lisa
L
Robson
Matthew
M
Covaci
Adrian
A
D000328:Adult; D000393:Air Pollutants / Q000032:analysis*; D016902:Air Pollution, Indoor / Q000032:analysis*; D004391:Dust / Q000032:analysis*; D004435:Eating; D004781:Environmental Exposure / Q000032:analysis*; D004784:Environmental Monitoring; D005411:Flame Retardants / Q000032:analysis*; D006798:Housing; D006801:Humans; D006842:Hydrocarbons, Brominated / Q000032:analysis*; D007223:Infant; D009864:Ontario; D013781:Texas; D006113:United Kingdom
D000393:Air Pollutants; D004391:Dust; D005411:Flame Retardants; D006842:Hydrocarbons, Brominated; C089796:hexabromocyclododecane