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Flow-electrode CDI removes the uncharged Ca-UO$$_{2}$$-CO$$_{3}$$ ternary complex from brackish potable groundwater; Complex dissociation, transport, and sorption

Ma, J.*; Zhang, Y.*; Collins, R. N.*; Tsarev, S.*; Aoyagi, Noboru   ; Kinsela, A. S.*; Jones, A. M.*; Waite, T. D.*

Unacceptably high uranium concentrations in decentralized and remote potable groundwater resources, especially those of high hardness, are a common worldwide problem. The complexation of alkali earth metals, carbonate and uranium(VI) results in the formation of thermodynamically stable ternary aqueous species that are predominantly neutrally-charged. The removal of the uncharged (non-adsorbing) complexes is a problematic issue for many water treatment technologies. As such, we have evaluated the efficacy of a recently-developed electrochemical technology, termed flow-electrode capacitive deionization (FCDI), to treat a synthetic groundwater, the composition of which is comparable to groundwater resources in the Northern Territory, Australia. Theoretical calculations and time-resolved laser fluorescence spectroscopy analyses confirmed that the complex was the primary aqueous species followed. Results under different operating conditions demonstrated that FCDI is versatile in reducing uranium concentrations to $$<$$ 10 $$mu$$g L$$^{-1}$$ with low electrical consumption (e.g. $$sim$$ 0.1 kWh m$$^{-3}$$). It is concluded that the capability of FCDI to remove uranium under these common conditions depends on the dissociation kinetics of the complex in the electrical field.

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