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137 Cs and 90 Sr, both byproducts of the uranium and plutonium fission processes, make up the majority of high-level waste from nuclear power plants. 63 Ni is a byproduct of the erosion-corrosion process of the reactor components in nuclear energy plants. The concentrations of these ions in solution determine the Waste Class (A, B, or C); thus, their selective removal in the presence of large excesses of nonradioactive ions is necessary to reduce waste volume and cut disposal costs. We report the new material K 2 x Mg x Sn 3– x S 6 ( x = 0.5–1, KMS-2) and its application for the ion exchange of Cs +, Sr 2+, and Ni 2+ in varying conditions. This compound crystallizes in the hexagonal space group P 6 3 / mmc with cell parameters a = b = 3.6749(8) Å and c = 16.827(4) Å. The difference in crystal structure between KMS-2, the previously reported Mn analog K 2 x Mn x Sn 3– x S 6 (KMS-1), and their parent SnS 2 is also described. Distribution coefficients for KMS-2 are high for Cs + (7.1 × 10 3 mL/g) and Sr 2+ (2.1 × 10 4 mL/g) at neutral pH (∼ 6 ppm, V/m ∼1000 mL/g). We also report on the comparative study of Ni 2+ ion exchange with both KMS-1 and KMS-2. Additional competitive reactions using Cs +, Sr 2+, and Ni 2+ in high concentrations of salt solution and at different pH values are reported.
Mertz et al. (Wed,) studied this question.