Three models for sorption/desorption of polycyclic aromatic hydrocarbon (PA
H) contaminants from soil were compared for their ability to predict the tr
ansport of PAH in soil: a "gamma" model, a "two-site/two-region" nonequilib
rium model, and a "hybrid" model. In the "hybrid" model, soil organic matte
r was conceptually divided into two compartments; a fraction with rapid sor
ption/desorption kinetics and a compartment with mass-transfer-limited kine
tics. Contaminant sorbed in the rapid compartment was assumed to be in inst
antaneous equilibrium with the aqueous phase, while the release of contamin
ant from the slow fraction was assumed to be governed by a gamma distributi
on of rate coefficients. The "hybrid" model successfully described the init
ial rapid release of a model PAH contaminant, naphthalene, from a sieved so
il sample of moderate organic content (congruent to 2.3%) as well as the fo
llowing slow release observed over 25 days in batch desorption experiments.
Other necessary model parameters, such as the hydrodynamic dispersion coef
ficient of naphthalene and the macropore porosity, were evaluated in separa
te experiments. A transport model incorporating the "hybrid" model for naph
thalene sorption/desorption successfully predicted the elution profile of n
aphthalene in independent soil-column experiments with no adjustable parame
ters. The success of the hybrid model suggests that a wide array of rate co
ntrols govern PAH desorption. This conclusion is consistent with the view o
f soils as consisting of a mix of different sorptive constituents and heter
ogeneous physical constraints on PAH release.