US EPA

1915751 

Technical Report 

Adsorption of Cs(sup +), Sr(sup 2+) and Ni(sup 2+) on bitumen: a mechanistic model 

Loon, LR; Kopajtic, Z 

1991 

NTIS/02976260_a 

GRA and I 

GRA and I 

The adsorption of radionuclides on the waste matrix is a positive effect and contributes to the retardation of released radionuclides migrating to the geo-and biosphere. For the safety assessment studies, it is important to know whether or not radionuclides do adsorb on the waste matrix. In the present work the adsorption of (sup 134)Cs(sup +), (sup 85)Sr(sup 2+) and (sup 63)Ni(sup 2+) on bitumen was studied as a function of the pH and ionic strength of the equilibrium solution. Bitumen emulsions with well defined surfaces were used. The surface of bitumen is negatively charged due to the deprotonation of weak acid carboxyl groups at the interface. The functional group density amounts to 1.37.10(sup 18) groups/m(sup 2) and their deprotonation behaviour can be well described by the 'Ionizable Surface Group' model. Cs(sup +), Sr(sup 2+) and Ni(sup 2+) adsorb on the surface by three different processes, i.e. ion exchange, outer sphere complexation and inner sphere surface complexation respectively. The adsorption depends on the pH and the ionic strength of the contact solution. Under near field conditions, Cs(sup +) and Sr(sup 2+) do not adsorb on the bitumen due to the competition with Na(sup +), K(sup +) and Ca(sup 2+) present in the cement pore water in contact with the bitumen. Ni(sup 2+) adsorption can also be neglected because the formation of neutral and anionic hydroxo complexes in solution competes strongly with the adsorption reaction. Other hydrolysable radionuclides of interest are expected to behave similarly to Ni(sup 2+). The main conclusion of the study is that the adsorption of radionuclides under near field conditions is expected to be very low. Consequently, this process need not to be considered in safety assessment studies. (author) figs., tabs., 30 refs. (Atomindex citation 22:027940)