2023
DOI: 10.1016/j.chemosphere.2023.138661
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Mechanistic understanding of perfluorooctane sulfonate (PFOS) sorption by biochars

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Cited by 19 publications
(36 citation statements)
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“…Recent studies indicated that the Freundlich model typically fits PFAS sorption data better, although the Langmuir model fitting performs better for other cases. ,, In this study, both Langmuir ( R 2 = 0.98 and 0.95 for commercial and Douglas Fir 900 biochars, respectively) and Freundlich ( R 2 = 0.95 and 0.96 for commercial and Douglas Fir biochars, respectively) models fitted the experimental data well (Figure ). These partially suggest that PFOS was sorbed onto biochar heterogeneous surface sites via different sorption mechanisms and subsequently percolating into biochar pores when the surface was fully occupied, ,, which is depicted in our recent study. Values of n ( n = 1.59 and 2.18 for commercial and Douglas Fir 900 biochars, respectively) in the Freundlich model indicate favorable sorption to heterogeneous surface sites, confirming nonlinear sorption. ,, This observation coincides with our previous findings that biochars sorb PFAS from a variety of sorption mechanisms such as hydrophobic and electrostatic interactions with positively charged N-containing functional groups and pore size trapping mechanisms. , The Langmuir model estimated a maximum monolayer sorption capacity ( Q m ) of 42.3 and 4.97 mg/g, respectively, for commercial and Douglas Fir 900 biochars (Table ).…”
Section: Resultssupporting
confidence: 62%
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“…Recent studies indicated that the Freundlich model typically fits PFAS sorption data better, although the Langmuir model fitting performs better for other cases. ,, In this study, both Langmuir ( R 2 = 0.98 and 0.95 for commercial and Douglas Fir 900 biochars, respectively) and Freundlich ( R 2 = 0.95 and 0.96 for commercial and Douglas Fir biochars, respectively) models fitted the experimental data well (Figure ). These partially suggest that PFOS was sorbed onto biochar heterogeneous surface sites via different sorption mechanisms and subsequently percolating into biochar pores when the surface was fully occupied, ,, which is depicted in our recent study. Values of n ( n = 1.59 and 2.18 for commercial and Douglas Fir 900 biochars, respectively) in the Freundlich model indicate favorable sorption to heterogeneous surface sites, confirming nonlinear sorption. ,, This observation coincides with our previous findings that biochars sorb PFAS from a variety of sorption mechanisms such as hydrophobic and electrostatic interactions with positively charged N-containing functional groups and pore size trapping mechanisms. , The Langmuir model estimated a maximum monolayer sorption capacity ( Q m ) of 42.3 and 4.97 mg/g, respectively, for commercial and Douglas Fir 900 biochars (Table ).…”
Section: Resultssupporting
confidence: 62%
“…Nevertheless, high R 2 values obtained from the pseudo-first-order kinetic model suggest that physical interactions, such as pore filling, hydrogen bonding, and hydrophobic interactions, also likely contribute to PFAS removal by biochars. The measured contact angles of the commercial biochar and Douglas Fir 900 biochar were 135.3 and 145.5°, respectively, indicating that both PFAS and biochar had a great hydrophobicity and hydrophobic interaction, which was one of the factors facilitating PFAS sorption by biochars …”
Section: Resultsmentioning
confidence: 98%
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