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Per- and polyfluoroalkylated substances (PFAS) are a large group of toxic compounds which have been widely used in industrial and consumer applications, from where they can migrate into the environment. They can pose a risk to human health because they have been associated with several diseases. To obtain more information on the risk of PFAS in fast food packaging materials, several PFAS (perfluorocarboxylic acids or PFCAs (n = 16), perfluorosulfonic acids or PFSAs (n = 14), and a miscellaneous group constituted by sulfonamides (n = 5) and fluorotelomer phosphate esters or PAPs (n = 5)) were quantified in food contact materials (FCMs) from fast-food restaurants in France. Perfluorohexanoic acid (PFHxA), 6:2 fluorotelomer sulfonic acid (6:2 FTS) and 6:2/6:2 fluorotelomer phosphate diester (6:2/6:2 diPAP) were detected in all samples. PFCAs with shorter chain lengths (C-C) showed the highest concentrations compared to median (C-C) and longer chain length PFCAs (C-C). However, they had lower detection frequencies (DFs) (except for PFHxA, DF = 100%) with values of 36 and 34% for C and C PFCAs, respectively. The DF of longer chain length PFCAs was higher, especially those of the median chain length PFCAs (C-C, with DF = 79-98%). Analytes from the PFSA group with high DFs (70-98%) were perfluorobutane sulfonic acid (PFBS), perfluorohexane sulfonic acid (PFHxS), perfluorooctane sulfonic acid (PFOS, linear and branched) and 10:2 fluorotelomer sulfonic acid (10:2 FTS), with concentrations similar to some analytes from the PFCA group. 4:2 Fluorotelomer phosphate monoester (4:2 mPAP), 8:2 fluorotelomer phosphate monoester (8:2 mPAP) and 8:2/8:2 fluorotelomer phosphate diester (8:2/8:2 diPAP) were found with the highest concentrations (<0.006-42.7 ng g, <0.001-2.7 ng g and <0.001-287 ng g, respectively) and the highest DFs (ranged 68-94%). Some correlations between analytes were found, indicating similar degradation routes or a common origin.
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http://dx.doi.org/10.1016/j.chemosphere.2023.139734 | DOI Listing |
Environ Sci Process Impacts
December 2024
Department of Environmental and Molecular Toxicology, Oregon State University, Corvallis, OR 97331, USA.
Per- and polyfluoroalkyl substances (PFAS) are reported in residential and commercial paints, but there are no data for paints used in the transportation sector. From 2023 to 2024, 16 traffic paints and 10 bridge paints were collected from Pacific Northwest regional transportation facilities or purchased and analyzed for total fluorine by F-nuclear magnetic resonance (NMR) spectroscopy, volatile PFAS by gas chromatography-mass spectrometry (GC-MS), and ionic target and suspect PFAS by liquid chromatography-quadrupole time-of-flight mass spectrometry. The only target PFAS identified was 6:2 fluorotelomer phosphate diester (diPAP) which ranged in concentrations from 0.
View Article and Find Full Text PDFFood Chem Toxicol
November 2024
School of Public Health, Capital Medical University, Beijing, 100069, China; Beijing Key Laboratory of Diagnostic and Traceability Technologies for Food Poisoning, Beijing Center for Disease Prevention and Control, Beijing, 100013, China; Food Laboratory of Zhongyuan, Luohe, 450007, China. Electronic address:
J Hazard Mater
December 2024
Nanjing Institute of Environmental Sciences, Ministry of Environment and Ecology of China, Nanjing 210042, China. Electronic address:
Wastewater acts as a significant sink and source of per- and polyfluoroalkyl substances (PFAS). This study investigated the occurrence, removal and mass flow of 48 emerging and legacy PFAS in 8 domestic and general industrial wastewater treatment plants (WWTPs) throughout entire treatment processes. In wastewater and sludge, 24 and 26 PFAS were detected, with concentrations of 246-27,100 ng/L and 91.
View Article and Find Full Text PDFAnal Bioanal Chem
December 2024
Department of Geosciences, Environmental Analytical Chemistry, University of Tübingen, Schnarrenbergstraße 94-96, 72076, Tübingen, Germany.
Organofluorine mass balance approaches are increasingly applied to investigate the occurrence of per- and polyfluoroalkyl substances (PFAS) and other organofluorines in environmental samples more comprehensively. Usually, complex samples prevent the identification and quantification of every fluorine-containing molecule. Consequently, large unidentified fractions between fluorine sum parameters such as extractable organic fluorine (EOF) and the sum of quantified analytes are frequently reported.
View Article and Find Full Text PDFChemosphere
October 2024
Hampton Roads Sanitation District, Virginia Beach, VA, USA.
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