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POTENTIAL APPLICATIONS OF AHC TECHNOLOGY TO NUCLEAR WASTE DISPOSAL



AHC TECHNOLOGY - A BENEFICIAL TOOL FOR HYDROLYTIC EARTH RESTORATION APPLICATIONS TO NUCLEAR WASTE CLEANUP ACTIVITIES

This Appendix describes recently formulated concepts, "proof-of-concept" studies, and in-house development activities which establish the feasibility of incorporating AHC technology as the key element in a broad range of environmental restoration, waste management, decontamination / decommissioning projects that are currently scheduled for Hanford Washington, Rocky Flats Colorado, Savannah River Georgia, and other Department of Energy (DOE) sites.

SURFACE VITRIFICATION

The Hanford Waste Vitrification (HWV) plant, as currently designed, will be capable of processing 2.4 tons of high-level nuclear waste per day, beginning in 1999. In effect, this high temperature process will transform mixtures of high-level waste slurries, whether pre-treated or not, and sand-like material into low-grade glass which solidify in steel tube canister "molds" 2 ft. in diameter by 10 ft. long, for eventual storage in Federal repositories, e.g., Yucca Mountain, Nevada. In addition, it is anticipated that, by 2010, the installation of a replacement melter will boost the high-level nuclear waste processing capability by 300% to 500%. In any event, AHC technology, in its present form, affords a surface vitrification alternative to achieve drastic increases in processing capacity, with essentially no change in energy costs. The basic elements of this AHC alternative include: step 1 - metering, high-level nuclear waste slurries and hydrolytic cements into a high shear pin mixer; step 2 - casting the pin mixer effluent into a high speed belt of interconnected mini-briquette plastic molds, with flexibility in two dimensions; step 3 - accelerating the hydrolytic setting process with microwave heating; step 4 - surface vitrification of briquettes in the HWV plant; step 5 - pour casting mixtures of hydrolytic cement and surface-vitrified briquettes directly into steel canisters to solidify at ambient temperature; and step 6 - eventual storage in Federal repositories. An important side benefit of this AHC alternative is that radioactive gases attendant to normal operation of a HWV plant will effectively be eliminated in proportion to reduced "dwell times" of nuclear waste in the high temperature environment, i.e., surface vitrification requires orders of magnitude less time than volume vitrification.

ALTERNATIVE TO GROUT IMMOBILIZATION

In September of 1993, after nearly 5 years of intensive technical investigations and the construction of a $29 million Hanford Grout Immobilization facility, the DOE announced that the "grout concept," in its present form, was no longer a viable option for solidification of low-level nuclear waste prior to storage in underground, 123' x 50' x 34', concrete vaults. Presumably, this decision was based on the following shortcomings of Portland cement/flyash grout: excessive heat from exothermic hydraulic cement reactions; thermal stress-induced fractures during 28 day curing cycles; inadequate control of viscosities and set times; excessive shrinkage during the cure cycle; and inability to reduce leachates to acceptable levels. In any event, this decision was immediately followed by successful demonstration that, with appropriate modification to basic hydrolytic cements and/or judicious selection of dispersed phase additives, AHC technology can far surpass all grout specifications. In effect, this demonstration combined modified/unmodified hydrolytic cements with DOE-approved nuclear waste simulants, i.e., corrosive oxidizer sludges containing 32.3% sodium nitrate, sodium nitrite, sodium hydroxide, and lead nitrate salts, to achieve the following, non-optimized, results: simple replacement of Hydrolytic water components with 40oC sludge water produced dimensionally stable AHC materials with 10.7% by weight of sludge solids; dispersed phase additives of carbon black reduced ionic mobilities by 10% (surface absorption); a silicone copolymer (1 of over 300 different types) reduced ionic mobilities by an additional 83.8% (permeability reduction); special silicone-glycol surfactants reduced ionic mobilities by 99.9% (closed cell formation); selective chemical (silane) and molecular sieve (zeolite) additions to hydrolytic cements allow AHC-encapsulated nuclear wastes to easily pass EPA's toxic chemical leaching procedures; a sodium silicate molar ratio of 1.8 (SiO2:Na20) eliminated shrinkage and maintained viscosities within desired pumping limits; and Hydrolytic set times were adjustable over a very wide range.

LAND DISPOSAL / PLUME CONTAINMENT

Coincident with "proof-of-concept" investigations for Westinghouse Hanford Corp., laboratory personnel were involved in AHC product development activities that may have direct or indirect application to plume containment at various DOE sites. Specifically, these prototype development activities related to solidification of caustic soil sludges with hydrolytic cements for potential applications to soil stabilization, oil field cleanup, and low cost, water-resistant, construction materials (an improved adobe, of sorts). Sludge parameters for these investigations were limited to the following ranges: temperature 80oF to 105oF; pH - 12; soil mesh size - 50 to 100; and solids content - 40% to 72.6%. In addition, variations in hydrolytic cement/dispersed phase components included: sodium silicate molar ratio - 1.8 to 3.22; oil additives - 5% to 15%; and kerosene additives - 2% to 13.5%. Relevant data from these studies, i.e., initial set times, gelation times, water loss, etc., indicate that the optimized Hydrolytic mixing parameters and dispersed phase additives which result from "tailored AHC alternatives to grout immobilization of low-level wastes" are directly applicable in preventing ground water contamination from leaking underground storage tanks, piping systems, etc., at DOE sites.  

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