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Interactions between Concrete and Brine at the Waste Isolation Pilot Plant (WIPP) Site, New Mexico

Published online by Cambridge University Press:  15 February 2011

Steven J. Lambert
Affiliation:
Sandia National Laboratories, P. O. Box 5800, Albuquerque, NM 87185
E. James Nowak
Affiliation:
Sandia National Laboratories, P. O. Box 5800, Albuquerque, NM 87185
Lillian D. Wakeley
Affiliation:
Structures Laboratory, Department of the Army, Waterways Experiment Station, Corps of Engineers, 3900 Halls Ferry Road, Vicksburg, MS 39100–6199
Toy S. Poole
Affiliation:
Structures Laboratory, Department of the Army, Waterways Experiment Station, Corps of Engineers, 3900 Halls Ferry Road, Vicksburg, MS 39100–6199
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Abstract

A concrete liner emplaced in 1984 in a shaft at the Waste Isolation Pilot Plant has served as a natural laboratory for observing interactions among concrete, evaporite rocks, and brine. During a routine inspection of the liner in the spring of 1990, discoloration, deposition of secondary salts, wet areas with exposed aggregate grains, softening of paste, surficial spalling, and cracking were observed locally on the concrete surface of the liner. Some construction joints showed apparent leakage of brine from behind the liner, which was nominally 50 cm thick. Seepage brines were nearly saturated relative to CaCl2 and contained lesser amounts of MgCl2 and KCl, and minor NaCl. The liner surface was locally altered to a 1–2 cm friable hygroscopic layer containing little cement paste; concrete cores (7 or 10 cm diameter) through the liner at depths of 248, 254, 255, and 271 m showed similar degrees of alteration at the liner/rock interface. The most profound alteration of concrete was developed in a ˜7 cm zone sub-parallel to and straddling the construction joint cored at a depth of ˜254.5 m. This zone was extensively microfractured, transected aggregate grains, and contained brucite, gypsum, magnesium hydroxychloride hydrate, and locally calcium chloroaluminate instead of the usual phases of hydrated portland cement. Several mechanisms of chemical degradation have been proposed, the most likely being attack by magnesium ions.

Type
Research Article
Copyright
Copyright © Materials Research Society 1992

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References

REFERENCES

1. Lambert, S. J., in Scientific Basis for Nuclear Waste Management VI, edited by Brookins, D. G. (Mater. Res. Soc. Proc. 15, Elsevier Science Publishing Co., Inc., New York, 1983) pp. 291298.Google Scholar
2. Mercer, J. W., Geol., U. S. Surv. Water-Resources Inv. Rept 83–4016, 1983.Google Scholar
3. Wakely, L. D., Poole, T. S., and Burkes, J. P., presented at the 1991 ACI Spring Convention, Boston, MA, 1991 (unpublished).Google Scholar
4. Ftikos, Ch. and Parissakis, G., Cem. Conc. Res. 15(4), 593598 (1985).10.1016/0008-8846(85)90057-2Google Scholar
5. Massazza, F., il Cemento 82(1), 326 (1985).Google Scholar
6. Benstead, J., il Cemento 86(4), 217228 (1989).Google Scholar
7. Cole, W. F., Nature 171(4347), 354355 (1953).10.1038/171354a0Google Scholar
8. Cohen, M. D. and Bentur, A., ACI Mat. J. 85(3), 148157 (1988).Google Scholar