Crystalline rock is used as the host rock for the disposal of high-level radioactive waste. Two cationic elements (Cs(I) and Ni(II)) and three anionic elements (Se(IV/VI), Mo(VI), and U(VI)) were selected to comprehensively evaluate the sorption behaviors of these radionuclides on crystalline granite and biotite gneiss. The anionic elements showed weak sorption (log K d (L·kg -1 ) < 1) and little competition effect, while the cationic elements (log K d (L·kg -1 ) = 2-3) showed clear competition (18-98% in K d values) even at low concentrations. Analysis by pseudo-second-order kinetics showed that Cs(I) sorbed at similar rates on both rocks (20% faster on biotite gneiss), but Ni(II) sorbed 190% faster on biotite gneiss than on granite. That is why the retardation factors for Cs(I) and Ni(II) were reversed in the biotite gneiss column compared to their distribution coefficients. Therefore, the sorption kinetics cannot be neglected in groundwater systems with high flow rates. In the desorption column test, the retardation followed the order of the distribution coefficient. The desorption column test revealed that the distribution coefficient determines the strength of sorption on crystalline rocks.
Keyphrases
- sewage sludge
- heavy metals
- organic matter
- room temperature
- liquid chromatography
- drinking water
- health risk
- municipal solid waste
- health risk assessment
- human health
- magnetic resonance imaging
- diffusion weighted imaging
- metal organic framework
- anaerobic digestion
- single cell
- transition metal
- high resolution
- data analysis