“…Given the unique physicochemical properties of PFAS, including the hydrophobic and oleophobic characteristics of the perfluoroalkyl tail and the charged functional headgroup, PFAS are susceptible to various chemical interactions. These include but are not limited to electrostatic, ion exchange, ligand exchange, and hydrophobic interactions, as well as physical interactions, including surface adsorption and occlusion within adsorbent pores. − Specifically, key sorption mechanisms for ion-exchange resins include ion exchange, electrostatic interactions between the charged functional groups of PFAS and the resin matrix, hydrophobic interactions between the fluoroalkyl PFAS tail and the polymer chain of the resin, and the formation of aggregates on active sites of the resin surface, − and carbonaceous adsorbents (such as granular activated carbon) can adsorb PFAS via hydrophobic partitioning of PFAS onto the carbon matrix and via sequestration in micropores, with the larger surface areas of powdered activated carbon, facilitating faster and increased sorption. , Clay and variably modified clay adsorbents, such as amine-modified adsorbents, including clay–carbon composite materials, also facilitate PFAS sorption via mixed mode hydrophobic and electrostatic interactions. ,, As a result, these adsorbent-based treatments are widely applied or the treatment of PFAS-contaminated soil and water, especially focusing on ex situ applications. ,,− …”