The effect of citric acid (CA), desferrioxamine B (DFOB), fulvic acid (FA), and humic acid (HA) on plutonium (Pu) sorption to goethite was studied as a function of organic carbon concentration and pH using batch sorption experiments at 5 mg·L and 50 mg·L natural organic matter (NOM), 10-10 M Pu, and 0.1 g·L goethite concentrations, at pH 3, 5, 7, and 9. Low sorption of ligands coupled with strong Pu complexation decreased Pu sorption at pH 5 and 7, relative to a ligand-free system. Conversely, CA, FA, and HA increased Pu sorption to goethite at pH 3, suggesting ternary complex formation or, in the case of humic acid, incorporation into HA aggregates. Mechanisms for ternary complex formation were characterized by Fourier transform infrared spectroscopy in the absence of Pu. CA and FA demonstrated clear surface interactions at pH 3, HA appeared unchanged suggesting HA aggregates had formed, and no DFOB interactions were observed. Plutonium sorption decreased in the presence of DFOB (relative to a ligand free system) at all pH values examined. Thus, DFOB does not appear to facilitate formation of ternary Pu-DFOB-goethite complexes. At pH 9, Pu sorption in the presence of all NOM increased relative to pH 5 and 7; speciation models attributed this to Pu(IV) hydrolysis competing with ligand complexation, increasing sorption. The results indicate that in simple Pu-NOM-goethite ternary batch systems, NOM will decrease Pu sorption to goethite at all but particularly low pH conditions.

Coordination of uranyl (U(vi)) with carboxylate groups on functionalized graphene oxide (GO) surfaces has been shown to alter the reduction potential of the sorbed uranium ion. A quantitative measure of the reduction potential and qualitative estimation of sorption/desorption processes were conducted using cyclic voltammetry, and the proposed coordination environment was determined using the surface sensitive attenuated total reflection mode of infrared spectroscopy (ATR-FTIR). GO is a nanostructured material possessing a large amount of oxygen-containing functional groups both on basal planes and at the edges, which can form strong surface complexes with radionuclides. The presence of these functional groups on the surface of GO allows efficient immobilization of uranium due to sorption of uranyl (UO) to carboxylate, hydroxide, or sulfonate functional groups and the potential for enhanced reduction of U(vi) to more strongly sorbing and insoluble U(iv). Herein, binding of U(vi) to carboxylate groups on the GO surface is proposed as the primary sorption mechanism based on the FTIR study. Furthermore, the coordination of uranium with the surface increases the reduction potential of the U(vi)/U(iv) redox couple as compared to the case of the aqueous U(vi)/U(iv) species. This is consistent with the alteration of the electronic structure of the sorbed ion, which can be determined in our case due to the use of a GO-coated working electrode. Thus, GO-coated glassy carbon electrodes and other semi-conducting electrodes with high ion sorption capacities may provide a means of examining the oxidation/reduction potentials of sorbed ions.

Poly(amidoamine) (PAMAM) dendrimers have been established as efficient ligands for the removal of humic acid (HA) foulant, based upon electrostatic and hydrophobic interactions, as well as hydrogen bonding. This proof-of-concept study indicates the broad utility of dendritic nanotechnology for water treatment and environmental applications.

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Preparation of relatively pure low concentration Pu(V) solutions for environmental studies is nontrivial due to the complex redox chemistry of Pu. Ozone gas generated by an inexpensive unit designed for household-use was used to oxidize a 2 × 10(-8) M Pu(IV) solution to predominantly Pu(VI) with some Pu(V) present. Over several days, the Pu(VI) in the solution reduced to Pu(V) without further reducing to Pu(IV). The reduction from Pu(VI) to Pu(V) could be accelerated by raising the pH of the solution, which led to an immediate conversion without substantial conversion to Pu(IV). The aqueous Pu was found to be stable as predominately Pu(V) for greater than one month from pH 3-7; however, at circumneutral pH, a sizable fraction of Pu was lost from solution by either precipitation or sorption to the vial walls. This method provides a fast means of preparing Pu(V) solutions for tracer concentration studies without numerous extraction or cleanup steps.