Interactions of actinides with pyrite
surfaces are highly important
in catalyzing their reductive immobilization, thereby controlling
the movement of these species in the environment. Here, surface adsorption
and subsequent reduction of aqueous actinyl(VI) on pyrite surfaces
were explored using density functional hybrid theory (DFT-B3LYP) combined
with a first hydration sphere of water molecules and a dielectric
continuum for solvation effects. Adsorption of cationic (AnO2(H2O)5)2+(An = U, Np, Pu) and neutral
AnO2(OH)2(H2O)3 actinyl
onto a small pyrite cluster (Fe4S8) and the
effect of coadsorption on the energetics and electron transfer are
evaluated by adding either hydroquinone, H2Q (reduced),
or quinone, Q (oxidized). The pyrite surface instantaneously transfers
an electron to the adsorbed cationic actinyl. Unpaired electron atomic
spin densities confirm the electron transfer from the pyrite surface
to An atoms. For the neutral actinyl adsorption, electron transfer
is confirmed for neptunyl and plutonyl but not for uranyl. Several
factors control the overall adsorption energetics and kinetics, such
as the nature of the coadsorbate (H2Q/Q), pyrite surface,
actinyl, and charge or protonation state (cationic or neutral). The
surface-mediated reduction of adsorbed actinyl occurs by receiving
electrons either directly from the sulfide or from the coadsorbed
H2Q through the sulfide. In the direct reduction case,
an H+ ion is added to the surface-bound cationic actinyl,
and the mineral surface acts as an electron donor. In contrast, in
the proton-coupled electron transfer (PCET) reduction, the surface
mediates the electrons through the surface by synergistically aligning
relevant orbitals in line. This results in the less soluble and stable
An(IV). Our results indicate that the pyrite surface promotes a faster
PCET reaction for the actinyl reduction under circumneutral (pH 4–7)
conditions