Health & Environmental Research Online (HERO)


Print Feedback Export to File
6391216 
Journal Article 
Novel and legacy poly- and perfluoroalkyl substances (PFASs) in indoor dust from urban, industrial, and e-waste dismantling areas: The emergence of PFAS alternatives in China 
Zhang, B; He, Y; Huang, Y; Hong, D; Yao, Y; Wang, L; Sun, W; Yang, B; Huang, X; Song, S; Bai, X; Guo, Y; Zhang, T; Sun, H 
2020 
Yes 
Environmental Pollution
ISSN: 0269-7491
EISSN: 1873-6424 
ELSEVIER SCI LTD 
OXFORD 
263 
Pt A 
114461 
English 
With the phase out of perfluorooctanesulfonate (PFOS) and perfluorooctanoic acid (PFOA), the composition profiles of poly- and perfluoroalkyl substance (PFAS) in our living environment are unclear. In this study, 25 PFASs were analyzed in indoor dust samples collected from urban, industrial, and e-waste dismantling areas in China. PFOS alternatives, including 6:2 chlorinated polyfluorinated ether sulfonate (6:2 Cl-PFESA) (median: 5.52 ng/g) and 8:2 chlorinated polyfluorinated ether sulfonate (8:2 Cl-PFESA) (1.81 ng/g), were frequently detected. By contrast, PFOA alternatives, such as hexafluoropropylene oxide dimer acid (HPFO-DA, Gen-X) and ammonium 4,8-dioxa-3H-perfluorononanoate (ADONA), were not found in any of the dust samples. As expected, all legacy PFASs were widely observed in indoor dust, and 4 PFAS precursors were also detected. Dust concentrations of 6:2 Cl-PFESA were strongly correlated (p < 0.05) with those of 8:2 Cl-PFESA regardless of sampling sites. 6:2 Cl-PFESA was also significantly associated with that of PFOS in industrial and e-waste (p < 0.01) areas. Association analysis suggested that the sources of PFOS and its alternatives are common or related. Although ∑Cl-PFESA concentration was lower than that of PFOS (17.4 ng/g), industrial areas had the highest 6:2 Cl-PFESA/PFOS ratio (0.63). Composition profiles of PFASs in the industrial area showed the forefront of fluorine change. Thus, the present findings suggested that Cl-PFESAs are widely used as PFOS alternatives in China, and high levels of human Cl-PFESA exposure are expected in the future. Short-chain PFASs (C4-C7) were the predominant PFASs found in dust samples, contributing to over 40% of ∑total PFASs. Furthermore, perfluoro-1-butanesulfonate/PFOS and perfluoro-n-butanoic acid (PFBA)/PFOA ratios were 2.8 and 0.72, respectively. These findings suggested shifting to the short-chain PFASs in the environment in China. To the authors knowledge this is the first study to document the levels of 6:2 Cl-PFESA, 8:2 Cl-PFESA in indoor dust. 
PFAS alternatives; Legacy PFASs; PFAS precursors; Indoor dust 
PFAS
• Additional PFAS (formerly XAgency)
     Literature Search Update December 2021
          PubMed
          Web of Science
     Screened Studies
          Supplemental
     Not prioritized for screening
     4,8-Dioxa-3H-perfluorononanoic acid
     Ammonium 4,8-dioxa-3H-perfluorononanoate
• Expanded PFAS SEM (formerly PFAS 430)
     Ammonium 4,8-dioxa-3H-perfluorononanoate
• PFAS 150
     Literature Search Update December 2021
          PubMed
          WOS
     Missing 2021 searches
     Literature Search Update December 2020
          PubMed
          WOS
     Literature Search August 2019
          PubMed
          Web of Science
     Perfluoro-2-methyl-3-oxahexanoic acid
     Perfluorooctanesulfonate
• PFBA
     LitSearch: May 2019 - May 2020
          PubMed
     Scopus: April 2021
• PFBS
     Search
          PubMed
     Lit Search Update: May 2019 - May 2020
          PubMed
     Lit Search Update: May 2020 - April 2021
          WOS
     Scopus: April 2021
• PFNA
     Literature Search
          Pubmed
          WOS
     LitSearch: May 2019 - May 2020
          PubMed
     LitSearch: May 2020 - April 2021
          PubMed
          WoS
     Title and Abstract Screening
          Excluded
               Not relevant to PECO
• PFOA (335-67-1) and PFOS (1763-23-1)
     LitSearch: Feb 2019 - May 2020
          PubMed
     Literature Search Update (Apr 2019 - Sep 2020)
          PubMed
          WOS
     LitSearch Update (Sept 2020 - Feb 2022)
          WOS