Abstract:
Ion exchange and adsorption (can both be referred to as ‘sorption’) are widely used as purification
and concentration methods in the nuclear industry. Various mathematic models have been
developed to describe the mechanisms of sorption using the kinetics and equilibrium data. In this
study, the ion exchange and adsorption capability and efficacy of various inorganic sorbent
materials to remove contaminants were investigated with the intent of applying the process in the
purification of post reactor uranium for reuse and cleaning of research reactors pool water. The
contaminants studied are Ce, Co, Ru, Sb and Sr ions. The sorbent materials candidates investigated
are antimony pentoxide, CoTreat®, IONSIV R9120B, activated carbons, alumina, titania,
manganese oxide and SrTreat®.
The sorption of Ce and Sr on antimony pentoxide was determined to be a slow sorption process.
The sorption kinetics data obtained for Sr removal by antimony pentoxide conformed to the
pseudo-second order kinetic model, with the sorption process reaching completion after 78 hours
contact time. The considerably slow kinetics makes the sorbent material a less suitable candidate.
At fixed solid/aqueous ratio, various parameters affecting sorption of Co on CoTreat® were
studied which include initial Co concentration, contact time, solution pH and temperature. The
sorption capacity of CoTreat® for Co ions was identified to increase with increasing contact time
and with increasing initial Co concentration. The Co sorption was halted at pH < 2. The sorption
of Co on CoTreat® reaction can be approximated to first order reversible kinetics at high initial
concentrations of Co while the sorption kinetics followed the pseudo-second order kinetics at low
initial concentrations of Co. The examination of the thermodynamic parameters revealed that the
sorption of Co on CoTreat® is an endothermic process and is spontaneous in the studied
temperature range. The equilibrium isotherm data was analysed using the Langmuir, Freundlich
and Dubinin-Radushkevich equations. The sorption of Co on CoTreat® followed the Langmuir
isotherm model. The Dubinin-Radushkevich parameters revealed that the sorption process is
driven by ion exchange. Slow kinetics were obtained for the Co removal by IONSIV R9120B
sorption process, therefore making the sorbent material not a good candidate for practical
application.
The sorption capacities of manganese oxide for Ru removal from aqueous solutions was
investigated at different initial concentrations of Ru. The fitting of the Langmuir and Freundlich
sorption models to the equilibrium data was investigated. The equilibrium data for the Ru sorption
on manganese oxide followed the Freundlich isotherm. The monolayer sorption capacity was determined to be 0.90 mg/g at 30 °C. The pseudo-first order and the pseudo-second order kinetic
models were used to fit the kinetic experimental data. The sorption of Ru on manganese oxide
follows the pseudo-second order kinetic model. The temperature dependent data revealed that the
sorption process is an endothermic and spontaneous ion exchange process. Poor sorption
capacities were determined for Ru removal by activated carbons.
The maximum sorption of Sb on titania was obtained at 0.1 M nitric acid medium. Kinetics studies
revealed that the sorption process followed pseudo-second order kinetics. The equilibrium data
was evaluated using the Langmuir and Freundlich isotherm models, and well fitted the Freundlich
isotherm. The obtained negative values of ΔG° and positive value of ΔH° advocate that Sb
sorption on titania is a spontaneous and endothermic process.
The effect of the experimental parameters: contact time, initial concentration of metal ion and
solution pH were investigated for Sb removal by alumina. The sorption capacity increased with
increasing contact time and initial Sb concentration. The sorption data could be explained by the
pseudo-first order kinetic model and the Langmuir isotherm.
The sorption data on Sr removal by SrTreat® revealed that the sorption capacity increases with
increasing initial Sr concentration. The sorption of Sr ions on SrTreat® was halted at pH < 2, and
the kinetics data obtained at high initial Sr concentration can be approximated to the pseudosecond
order kinetics.
The dynamic sorption studies revealed that efficacy of the studied sorbent materials to remove the
target contaminants drastically declined in the presence of uranium ions.