Ethylenediaminetetraacetic acid (EDTA),
a strong complexing agent,
is a common constituent of liquid nuclear waste streams. The interaction
of EDTA or other organic or inorganic ligands with uranyl enhances
the mobilization of uranium and therefore significantly influences
the disposal and remediation of uranium waste. Although numerous studies
have focused on the effect of EDTA on the mobilization of environmental
uranium, including the adsorption and redox reactions of uranium on
mineral surfaces, few studies have differentiated the reaction-controlling
steps (diffusion, adsorption, and chemical reaction/electron transfer)
occurring at heterogeneous interfaces to assess the effect of EDTA
complexation on each of these processes. Here, a combination of in
situ electrochemical methods and quantum-mechanical calculations was
used to study the effect of EDTA complexation on the kinetics and
thermodynamics of redox reactions of uranium at the pyrite-solution
interface. Experiments indicate a potential shift of U(VI)/U(V) on
the pyrite surface of ∼0.04 V due to surface adsorption and
−0.21 V due to EDTA complexation, with similar results from
the calculations. The oxidation of the U(IV) reaction is more sensitive
to EDTA complexation in solution than that of U(V). Disproportionation,
affecting 2/3 of the intermediate pentavalent state, is the rate-limiting
step of the overall redox cycle of uranyl. The charge transfer was
controlled by diffusion and adsorption processes. EDTA can promote
the delivery of free uranyl from the bulk solution to the pyrite–water
interface where the reaction takes place, making the electron-transfer
process less diffusion-limited. Adsorption of uranyl onto pyrite surfaces
in the gradient electric field is multimolecular layer adsorption,
through which electron transfer can occur.