The objective of this study was to develop and evaluate electrochemically-e
nhanced immobilization of radionuclides in contaminated groundwater using F
e-0. A bench-scale flow-through Fe-0 reactor column with direct current was
tested to increase the efficiency and effective life of the Fe-0 medium by
(i) providing an external supply of electrons, (ii) controlling the rate o
f iron oxidation, and (iii) enhancing the rate of radionuclide immobilizati
on. The removal mechanism appears to be reductive coprecipitation of radion
uclides by iron oxidation by creating a reducing environment in the reactiv
e iron barrier. Several factors influence the removal of radionuclides from
groundwater using this reactor column including electrode configuration, a
pplied voltage, distance between cathode and anode, and radionuclide concen
tration.