2021
DOI: 10.1021/acs.macromol.1c00096
|View full text |Cite
|
Sign up to set email alerts
|

Amphiphilic Perfluoropolyether Copolymers for the Effective Removal of Polyfluoroalkyl Substances from Aqueous Environments

Abstract: Effective removal of per- and polyfluoroalkyl substances (PFAS) from the environment has become a major focus of a number of research groups due to their high stability and persistence in the environment. In this study, we report a fundamental study of the removal of one of the most extensively produced PFAS, perfluorooctanoic acid (PFOA), using amphiphilic perfluoropolyether (PFPE)-containing block copolymers as effective sorbents. The results demonstrate interactions between PFOA and the PFPE blocks and that… Show more

Help me understand this report

Search citation statements

Order By: Relevance

Paper Sections

Select...
2
1
1

Citation Types

3
38
0

Year Published

2021
2021
2024
2024

Publication Types

Select...
7
2

Relationship

6
3

Authors

Journals

citations
Cited by 25 publications
(41 citation statements)
references
References 52 publications
3
38
0
Order By: Relevance
“…The 19 F resonances due to PFOA in Figure 4 broaden upon the addition of polymer (Table S1), mainly due to the restriction of mobility of the fluorinated segments on interacting with the polymer through fluorine−fluorine hydrophobic interactions and/or electrostatic attraction. 17,22,39 With increasing PFOA concentration >0.3 mM (still below the CMC), the 19 F NMR resonances of PFOA in the presence of the polymer shift back and approach the chemical shifts of free PFOA, indicating the effects of fast chemical exchange (Figures S7−S9). 19 F DOSY NMR provides additional understanding of the nature of fluorine−fluorine and electrostatic interactions by providing measurements of the self-diffusion coefficients (D f ) of PFOA and the polymer sorbent upon mixing.…”
Section: ■ Results and Discussionmentioning
confidence: 98%
“…The 19 F resonances due to PFOA in Figure 4 broaden upon the addition of polymer (Table S1), mainly due to the restriction of mobility of the fluorinated segments on interacting with the polymer through fluorine−fluorine hydrophobic interactions and/or electrostatic attraction. 17,22,39 With increasing PFOA concentration >0.3 mM (still below the CMC), the 19 F NMR resonances of PFOA in the presence of the polymer shift back and approach the chemical shifts of free PFOA, indicating the effects of fast chemical exchange (Figures S7−S9). 19 F DOSY NMR provides additional understanding of the nature of fluorine−fluorine and electrostatic interactions by providing measurements of the self-diffusion coefficients (D f ) of PFOA and the polymer sorbent upon mixing.…”
Section: ■ Results and Discussionmentioning
confidence: 98%
“…The synthetic details and characterization data for the copolymers are shown in the experimental section and Table S1. [25][26][27][28][29][30][31][32][33][34] Fig. 1a illustrates the chemical structures of PFPE polymer (EO10-PFPE) and control polymer (EO10-CTRL).…”
Section: Resultsmentioning
confidence: 99%
“…[27-30, 32, 34, 35] Many emerging PFAS remediation technologies have demonstrated efficient PFAS removal in batch studies conducted in pure water at low to moderate PFAS concentrations, but few have been studied in real water matrices or in flow-through columns. In general, emerging PFAS remediation technologies leverage intermolecular interactions such as ion exchange, [36][37][38][39][40] hydrophobic or fluorous interactions, [39][40][41][42][43][44][45] or encapsulation by supramolecular receptors [46][47][48][49][50][51][52] to bind PFAS.…”
Section: Introductionmentioning
confidence: 99%