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. 2021 Sep;31(5):930-942.
doi: 10.1038/s41370-021-00288-7. Epub 2021 Feb 5.

Per- and polyfluoroalkyl substances (PFAS) and total fluorine in fire station dust

Affiliations

Per- and polyfluoroalkyl substances (PFAS) and total fluorine in fire station dust

Anna S Young et al. J Expo Sci Environ Epidemiol. 2021 Sep.

Abstract

Per- and polyfluoroalkyl substances (PFAS) are a class of over 4700 fluorinated compounds used in industry and consumer products. Studies have highlighted the use of aqueous film-forming foams (AFFFs) as an exposure source for firefighters, but little is known about PFAS occurrence inside fire stations, where firefighters spend most of their shifts. In this study, we aimed to characterize PFAS concentrations and sources inside fire stations. We measured 24 PFAS (using LC-MS/MS) and total fluorine (using particle-induced gamma ray emission) in dust from multiple rooms of 15 Massachusetts stations, many of which (60%) no longer use PFAS-containing AFFF at all and the rest of which only use it very rarely. Compared to station living rooms, turnout gear locker rooms had higher dust levels of total fluorine (p < 0.0001) and three PFAS: perfluorohexanoate (PFHxA), perfluoroheptanoate (PFHpA), and perfluorodecanoate (PFDoDA) (p < 0.05). These PFAS were also found on six wipes of station turnout gear. By contrast, the dominant PFAS in living rooms was N-ethyl perfluorooctane sulfonamidoacetic acid (N-MeFOSAA), a precursor to perfluorooctane sulfonate (PFOS) that still persists despite phase-outs almost two decades ago. The Σ24 PFAS accounted for less than 2% of fluorine in dust (n = 39), suggesting the potential presence of unknown PFAS. Turnout gear may be an important PFAS source in stations due to intentional additives and/or contamination from firefighting activities.

Keywords: Analytical Methods; Emerging Contaminants; Endocrine Disruptors; Healthy Buildings; PFAS; Perfluorinated Chemicals; Vulnerable Occupations; Workplace Exposures.

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Conflict of interest statement

Conflict of Interest

The authors declare no conflict of interest.

Figures

Figure 1.
Figure 1.
Boxplot of concentrations of A) total fluorine (µg/g) and B) Σ24PFAS (ng/g) in dust by room type in 15 fire stations in Massachusetts.
Figure 2.
Figure 2.
Stacked bar chart of median speciated concentrations of each PFAS (ng/g) in dust by room type in 15 fire stations in Massachusetts.
Figure 3.
Figure 3.
Profiles of PFAS on wipes of turnout gear in a subset of six fire stations in Massachusetts. Note: The total Σ24PFAS concentration on each gear wipe (ng/wipe) is listed on top of the bar.

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