Environmental Engineering Reference
In-Depth Information
6.5.5
A PPLICATION
The HC process was specifically developed to deal with INEEL reprocessing waste.
INEEL waste is uniquely suited for cementitious solidification because overwhelm-
ing amounts of salt-forming caustic were never added to it and ~95% of it was
calcined. Like most of DOE's high-level waste, its total radionuclide content (~30
watts/m 3 ) is well under that of some of the “intermediate level” wastes routinely
converted to 0.5-m 3 concrete waste forms at Great Britain's THORP facility. A
portion of the reprocessing waste generated at other DOE fuel reprocessing facilities
could be directly processed into HC-type concrete (e.g., Scientific Review Panel's
strongly caustic “sludge washing” solutions 18 or the sludges now destined for its
glass melter), but the majority (the “supernates” and “salt cakes”) is unfit for making
anything but “saltstone” (or glass) unless first pretreated in a way that re-speciates
the sodium. “Steam reforming” is the only calcination technology still viable in the
DOE Complex that could conceivably be employed to accomplish this.
REFERENCES
1.
Bell, J., Nuclear Technology, 130, 89, 2000.
2.
“Idaho Clean-up Project Statement of Work,” DE-RP07-03ID14516, February 2004.
3.
Palmer, J. D. and Fairhall, G. A., Cement and Concrete Research , 22, 325, 1992.
4.
Siemer, D. D., Olanrewaju, J., Scheetz, B. E., Krishnamurthy, N., and Grutzeck, M.
W., Development of Hydroceramic Waste Forms, C eram. Trans. , 119, 383-390, 2001.
5.
Siemer, D. D., Olanrewaju, J., Scheetz, B. E., and Gruzeck, M. W., Development of
Hydroceramic Waste Forms for INEEL Calcined Waste, Ceram. Trans. , 119, 391-398,
2001.
6.
Dole, R. L. et al., Cement-Based Radioactive Hosts Formed Under Elevated Tem-
peratures and Pressures (FUETAP Concretes) for Savannah River Plant High-Level
Defense Waste, ORNL/TM-8579, March 1983.
7.
Soelberg, N., R., Marshall, D. W., Bates, S. O., and Taylor, D. D., Phase 2 THOR
Steam Reforming Tests for Sodium-Bearing Waste Treatment, INEEL/EXT-04-
01493, January 30, 2004.
8.
Conner, J. R., Chemical Fixation and Solidification of Hazardous Wastes , Van Nos-
trand Reinhold, New York, p. 13, 1990.
9.
Barney, G. S., Fixation of Radioactive Wastes by Hydrothermal Reactions with Clays,
Advances in Chemistry Series 153, American Chemical Society, Washington, D.C.,
pp. 108-125, 1976.
10.
Brownell, L. E., Kindle, C. H., and Theis, T. L., Review of Literature Pertinent to
the Aqueous Conversion of Radionuclides to Insoluble Silicates with Selected Ref-
erences and Bibliography (revised), ARH-2731 Rev., 1973.
11.
Jantzen, C. M. et al., Characterization of the Defense Waste Processing Facility
(DWPF) Environmental Assessment (EA) Glass Standard Reference Material,
WSRC-TR-92-346, Rev 1, June 1, 1993.
12.
Shi-Ben, Xing and Pegg, I. L., Effects of Container Materials on PCT Leach Test
Results for High-Level Nuclear Waste Glasses, Mat. Res. Soc. Symp., Proc., Vol. 333 ,
pp. 557-564 (Scientific Basis for Nuclear Waste Management XVII), 1994.
13.
U.S. EPA, SW-846, Test Methods for Characterization of Solid Waste: Physi-
cal/Chemical Methods, 3rd Edition , Method 1311, 1996.
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