The long-term interactions of aromatic amines with soils are important in d
efining the fate and transport of these compounds in the environment. Abiot
ic loss of aniline from the aqueous phase to the soil phase occurs with an
initial rapid loss due to reversible mass transfer processes, followed by a
slow loss due to irreversible reactions. A kinetic model describing these
processes in water-saturated soils was developed and evaluated. The model a
ssumes that instantaneous equilibrium occurs for the following reversible p
rocesses: (i) acid dissociation of the protonated organic base (BH+) in the
aqueous phase; (ii) ion exchange between inorganic divalent cations (D2+ =
Ca2+ + Mg2+) on the soil and the protonated organic base; and (iii) partit
ioning of the nonionic species of aniline (B-aq) to soil organic carbon. Th
e model assumes that irreversible loss of aniline occurs through reaction o
f B-aq with irreversible sites (C-ir) on the soil. A kinetic rate constant,
k(ir), and the total concentration of irreversible sites, C-T were employe
d as adjustable model parameters. The model was evaluated with measured mas
s distributions of aniline between water (with 5 mM added CaCl2) and five s
oils ranging in pH (4.4-7.3), at contact times ranging from 2 to 1600 h. So
me experiments were performed at different soil mass to water volume ratios
. A good fit was obtained with a single value of ki,for all soils, pH value
s, and soil-water ratios. To accurately predict soil-water distributions at
contact times < 24 h, mass transfer of the neutral species to the soil was
modeled as a kinetic process, again, assuming that ion exchange processes
are instantaneous.