A highly acidic aqueous waste containing metals was released into unli
ned seepage basins between 1955 and 1988 resulting in the contaminatio
n of the underlying aquifer. To provide insight about the mechanism(s)
responsible for the facilitated movement of several of these contamin
ant metals, ground-water samples were recovered from the aquifer along
a 1.02-km transect at approximately the rate of ground-water flow. Fa
cilitated contaminant transport was attributed primarily to the poor c
ation-sorbing capacity of the aquifer matrix and the soluble nature of
the metals in the acidic plume. Based on chemical equilibrium calcula
tions of ground-water ultrafiltrates which agreed with results from ca
tionic and anionic resin-exchange experiments, over 90% of each contam
inant metal (Cr, Ni, Cu, Cd, Pb, and U) existed in cationic forms in t
he aquifer: either as soluble metals or as sorbates associated with po
sitively charged ground-water colloids. These cationic species were no
t retained by the aquifer because the pH of the aquifer matrix was sli
ghtly below the measured point-of-zero charge, indicating the variable
charge sites on the mineral surfaces within the aquifer likely had a
net positive charge. Contaminants were associated with recovered groun
d-water colloids and this association increased with the pH of the sys
tem. However, mobile colloids would likely play only a small role in t
he transport of contaminants through this aquifer because of their rel
atively low concentration.