Uranyl phosphate
minerals represent an important secondary source
of uranium release at contaminated sites. In flow-through column experiments
with background porewater (BPW) of typical freshwater aquifer composition
(pH 7.0, ∼0.2 mM total carbonate (TC)), dissolution of K-ankoleite
(KUO2PO4·3H2O), Na-autunite
(NaUO2PO4·3H2O), and Ca-autunite
(Ca(UO2)2(PO4)2·6H2O) was controlled by mineral solubility at steady-state U
release. Effluent concentrations indicated exchange with BPW cations,
and postreaction characterization showed alteration of the initial
mineral composition, changes in structure (decreased crystallinity,
increased disorder, and distortion of U–P mineral sheets) and
possible neoformation of phases of similar structure. Increasing the
BPW pH and TC to 8.1–8.2 and 2.2–3.7 mM, respectively,
resulted in mineral undersaturation and produced ca. 2 orders-of-magnitude
higher U and P release without reaching steady state. Minerals incorporated
less BPW cations into their structures compared to low carbonate BPW
experiments but showed structural disorder and distortion. Faster
dissolution rates were attributed to the formation of binary and ternary
uranyl carbonate complexes that accelerate the rate-determining step
of uranyl detachment from the uranyl-phosphate layered structure.
Calculated dissolution rates (log R
s between
−8.95 and −10.32 mol m–2 s–1), accounting for reaction and transport in porous media, were similar
to dissolution rates of other classes of uranyl minerals. In undersaturated
solutions, dissolution rates for uranyl phosphate, oxyhydroxide, and
silicate minerals can be predicted within 1–2 orders-of-magnitude
from pH ∼5–10 on the basis of pH/carbonate concentration.