The chemical interactions of hydrophobic organic contaminants (HOCs) w
ith soils and sediments (geosorbents) may result in strong binding and
slow subsequent release rates that significantly affect remediation r
ates and endpoints. The underlying physical and chemical phenomena pot
entially responsible for this apparent sequestration of HOCs by geosor
bents are not well understood. This challenges our concepts for assess
ing exposure and toxicity and for setting environmental quality criter
ia. Currently there are no direct observational data revealing the mol
ecular-scale locations in which nonpolar organic compounds accumulate
when associated with natural soils or sediments. Hence macroscopic obs
ervations are used to make inferences about sorption mechanisms and th
e chemical factors affecting the sequestration of HOCs by geosorbents.
Recent observations suggest that HOC interactions with geosorbents co
mprise different inorganic and organic surfaces and matrices, and dist
inctions may be drawn along these lines, particularly with regard to t
he roles of inorganic micropores, natural sorbent organic matter compo
nents, combustion residue particulate carbon, and spilled organic liqu
ids. Certain manipulations of sorbates or sorbent media may help revea
l sorption mechanisms, but mixed sorption phenomena complicate the int
erpretation of macroscopic data regarding diffusion of HOCs into and o
ut of different matrices and the hysteretic sorption and aging effects
commonly observed for geosorbents. Analytical characterizations at th
e microscale, and mechanistic models derived therefrom, are needed to
advance scientific knowledge of HOC sequestration, release, and enviro
nmental risk.