A mathematical model is developed for metal leaching from contaminated
soils subjected to acid extraction in a batch reactor. The model cons
iders transport by pore diffusion and film transfer, leaching of metal
bound to reversible and irreversible phases, and metal complexation b
y ions in solution, As currently developed, the model is semiempirical
, with the primary objective of exploring the relative significance of
chemical kinetics and diffusional transport under acidic leaching con
ditions. Simulation results and sensitivity analyses show that leachin
g kinetics vary according to the metal binding mechanism and location
within a soil particle, The effects of pH, pore diffusion, film transf
er, chemical reaction rate, particle size, and initial metal distribut
ion are examined using parameter estimates derived from experimental d
ata for a hazardous-waste-site soil contaminated with lead. Depending
on leaching conditions, diffusion, reaction, or both may control metal
leaching for time-scales of interest in soil washing. Both the distri
bution of contaminant metal between the reversibly and irreversibly so
rbed fractions and the initial spatial distribution within the soil pa
rticle are important in determining leaching behavior.