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The Solubility and Sorption of Lead-210 and Carbon-14 in a Near-Field Environment

Published online by Cambridge University Press:  28 February 2011

S. Bayliss
Affiliation:
UKAEA, Harwell Laboratory, Oxfordshire, OX11 ORA, UK.
F. T. Ewart
Affiliation:
UKAEA, Harwell Laboratory, Oxfordshire, OX11 ORA, UK.
R. M. Howse
Affiliation:
UKAEA, Harwell Laboratory, Oxfordshire, OX11 ORA, UK.
J. L. Smith-Briggs
Affiliation:
UKAEA, Harwell Laboratory, Oxfordshire, OX11 ORA, UK.
H. P. Thomason
Affiliation:
UKAEA, Harwell Laboratory, Oxfordshire, OX11 ORA, UK.
H. A. Willmott
Affiliation:
UKAEA, Harwell Laboratory, Oxfordshire, OX11 ORA, UK.
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Abstract

This paper reports the results of some recent experimental studies of the solubility and sorption behaviour of lead-210 and carbon-14 under cementitious near-field conditions.

These studies have shown that under these conditions carbon-14 will have a maximum solubility limit of 10−4 M and that the distribution ratio, RD, will increase with increasing carbon-14 concentrations from 10−9 to 10−7 M. Not all of the carbon in the cement is available for exchange with carbon in the pore water. Differences in values of RD are observed between the two cement grout types studied, SRPC and OPC/BFS. Lead has been shown to have a maximum solubility limit of about 10−3 M at high pH. Good agreement is obtained between these measurements and thermodynamic modelling using the PHREEQE code. No differences were observed between lead solubilities under reducing or oxidising conditions at high pH values using the same phase separation techniques. Lead is particularly sensitive to the phase separation techniques employed. A factor of up to 250 difference is observed between 25000 and 30000 molecular weight cut-off filters. The values of RD for lead increase with decreasing lead concentrations and the values of RD for 10−3 M solutions are observed to be 500 mlg−1 for SRPC and 1300 mlg−1 for OPC/BFS.

Type
Research Article
Copyright
Copyright © Materials Research Society 1988

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References

[1] Ewart, F.T. and Tasker, P.W.. Chemical Effects in the Near-Field. ‘Waste Management 87’, Tuscon, Arizona. March 1987.Google Scholar
[2] Atkinson, A., UKAEA Report AERE-R11777 (1985).Google Scholar
[3] Sharland, S.M., Tasker, P.W. and Tweed, C.J.. UKAEA Report AERE-R12442 (1986).Google Scholar
[4] Hodgkinson, D.P., Robinson, P.C., Herbert, A.W., Tasker, P.W. and Grime, P.W.. UKAEA Report AERE-R11854 (1986).Google Scholar
[5] Ewart, F.T., Howse, R.M., Thomason, H.P., Williams, S.J. and Cross, J.E., in IX Symp. on Scientific Basis for Nuclear Waste Management, Ed. Werne, L., Publ. Elsevier, New York (1986).Google Scholar
[6] Ewart, F.T., Gore, S.J.M. and Williams, S.J., UKAEA Report AERE R-11975 (1985).Google Scholar
[7] Amicon Ltd., Upper Mill, Stonehouse, Glos, GL10 2BJ, UK.Google Scholar
[8] Rai, D., Radiochim. Acta 35 97 (1984).CrossRefGoogle Scholar
[9] Atkinson, A., UKAEA, Harwell (private communication).Google Scholar
[10] Cross, J.E., Ewart, F.T. and Tweed, C.J.. UKAEA Report, AERE-R12324, (1987).Google Scholar
[11] Pilkington, N.J., UKAEA Harwell (private communication).Google Scholar