“…As summarized in recent critical reviews, , retardation of nonpolymeric PFAS within vadose zone soils is a complex combination of multiple retention mechanisms and processes. Specific to the anionic perfluoroalkyl acids (PFAAs) of primary regulatory interest relevant to legacy AFFF formulations, these include hydrophobic interactions with the organic carbon (OC) fraction in soil, electrostatic interactions with the surfaces of variable-charged clay minerals including iron (Fe) and aluminum (Al) oxides and hydroxides to include potential irreversible chemisorption, and fluid–fluid (e.g., air–water) interfacial accumulation resulting in retardation from a “surface excess”. − Laboratory experiments further suggest that PFAA transport in soil is complicated by rate-limiting kinetics attributable to diffusive fluxes into and out of the OC matrix and associated hydrophobic solid-phase interactions, nonlinear (i.e., concentration-dependent) sorption to both solids and air–water interfaces, , and significant desorption hysteresis − resulting at least in part from biphasic porosity domains (highlighting the importance of diffusive fluxes) within natural soils. , In general, PFAS transport through unsaturated soil is “nonideal” even at environmentally relevant concentrations, and studies have suggested that kinetic models with these multiprocess retention mechanisms may be prerequisites for simulating transport under field conditions. , The various soil retention processes and their kinetics, interactions thereof, and potential confounding effects from the accumulation of PFAAs in soil as a result of polyfluorinated precursor transformation are the subject of much ongoing research …”