ArticleEnvironmental pollution (Barking, Essex : 1987)2022
Transport and fate of aqueous film forming foam in an urban estuary.
Article in Environmental pollution (Barking, Essex : 1987), 2022. The graph could read no effect estimate from its abstract, so it casts no vote on the map. Cited by 7 papers.
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Who cites it
7 citing papers in PubMed.
- Evaluating the environmental occurrence of per- and polyfluoroalkyl substances (PFAS) and potential exposure risk for recreational shellfish harvesters in the Great Bay Estuary, New Hampshire.The Science of the total environment · 2025Article
- The quest for the perfect "total PFAS" method: how can the total oxidisable precursor (TOP) assay be made reliable?Analytical and bioanalytical chemistry · 2025Review
- Assessing Bivalves as Biomonitors of Per- and Polyfluoroalkyl Substances in Coastal Environments.Environmental science & technology · 2025Article
- Hunting Metabolic Biomarkers for Exposure to Per- and Polyfluoroalkyl Substances: A Review.Metabolites · 2024Review
- Unregulated Active and Closed Textile Mills Represent a Significant Vector of PFAS Contamination into Coastal Rivers.ACS ES&T water · 2024Article
- Ecological characteristics impact PFAS concentrations in a U.S. North Atlantic food web.The Science of the total environment · 2023Article
- Field Validation of a Novel Passive Sampler for Dissolved PFAS in Surface Waters.Environmental toxicology and chemistry · 2022Article
Corrections and comments
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Authors and funding
8 authors.
Funding
Abstract
The deployment of aqueous film forming foams (AFFF) used for firefighting during emergencies and training often releases per- and polyfluoroalkyl substances (PFAS) into the environment. In October 2018, first responders in Providence, RI, USA applied an AFFF during a fuel spill. Due to the proximity of the incident to the upper reaches of Narragansett Bay (NB), an unknown quantity of gasoline and AFFF entered the estuary via surface runoff and stormwater drains. Water samples near the spill were collected approximately 15 h after the incident and analyzed for 24 PFAS. Minor increases in measured PFAS concentrations were observed relative to pre- and post-spill samples at monitoring sites near the incident, except 6:2-fluorotelomer sulfonate (6:2-FTS) that peaked post-spill (max 311 ng/L). After performing the total oxidizable precursor (TOP) assay on water samples and the AFFF concentrate, significant increases in perfluorocarboxylic acids (PFCAs) were observed. One compound, 6:2 fluorotelomer mercaptoalkylamido sulfonate (6:2-FTSAS), was identified as a major component of the AFFF used. Peak areas of 6:2-FTSAS and the degradation product 6:2-FTSAS-sulfoxide corresponded to observed increases in the TOP assay results and were useful as tracers of AFFF in surrounding waters. Elevated levels of PFAS at the time of sampling were limited to a confined area of the Providence River due to river flow and tidal action. Observed concentrations were also compared to hydrodynamic model results, and results confirmed rapid dissipation of AFFF components with distance from the spill. However, modeled results did not capture possible secondary releases of AFFF from local municipal stormwater and sewer infrastructure, as observational data suggest. The multiple lines of evidence of PFAS present in surface waters permitted a better assessment of the potential environmental impacts from products such as AFFF for which the chemical composition is largely unknown.
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Registered trials
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