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Publication numberUS3298961 A
Publication typeGrant
Publication dateJan 17, 1967
Filing dateAug 26, 1965
Priority dateAug 26, 1965
Publication numberUS 3298961 A, US 3298961A, US-A-3298961, US3298961 A, US3298961A
InventorsDavis George D, Frederick Edward J, Godbee Herschel W, Holmes John M
Original AssigneeDavis George D, Frederick Edward J, Godbee Herschel W, Holmes John M
Export CitationBiBTeX, EndNote, RefMan
External Links: USPTO, USPTO Assignment, Espacenet
Concentration and containment of radioactivity from radioactive waste solutions in asphalt
US 3298961 A
Abstract  available in
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Claims  available in
Description  (OCR text may contain errors)

United States Patent T CONCENTRATION AND CONTAINMENT OF RA- DIOACTIVITY FROM RADIOACTIVE WASTE SO- LUTION S IN ASPHALT George D. Davis, Kingston, Edward J. Frederick, Knoxville, Herschel W. Godbee, Oak Ridge, and John M. Holmes, Knoxville, Tenn, assignors to the United States of America as represented by the United States Atomic Energy Commission No Drawing. Filed Aug. 26, 1965, Scr. No. 482,950

2 Claims. (Cl. 252-3011) The present invention relates to the disposal of radioactive wastesolutions. More particularly, it relates to, and has for a principal object to provide a process for the concentration and containment of radioactivity from intermediate level radioactive waste solutions. The invention described herein was made in the course of, or under, a contract with the US. Atomic Energy Commission.

For the purposes of this invention, an intermediate level waste solution is one which contains radionuclides in excess of the maximum permissible levels as established by the International Commission on Radiological Protection, provided the total radiation emanating from such radionuclides is not suflicient to adversely degrade asphalt.

Public health and safety considerations prevent release of the majority of radioactive waste solutions to the environment without first assuring that the radiot-oxicity is within biologically acceptable values. Within this framework, a simple, inexpensive, and effective method is needed to concentrate and to retain as a stable insoluble solid the radionuclide content of large volumes. As a practical matter, any process for treating radioactive waste solutions to remove radionuclides and other salts usually results in a solution which is still radioactive, but contains lesser amounts of radionuclides. The success of any method of treating and handling radioactive waste solutions is measured by (a) the degree to which the radionuclides are reduced in the treated solution, and (b) the effectiveness of the containment of the separated nuclides, as well as (c) the economics of the total process.

It is, therefore, an object of this invention to provide a process of treating an intermediate level radioactive waste solution to effectively concentrate and contain the radionuclide and salt content wherein said process is characr terized by its simplicity, ease of hand-ling, and overall economy.

'The objects of this invention are met by a process which comprises contacting an intermediate level radioactive waste solution, as previouslydefined, with an emulsified asphalt composition, evaporating the water in the resultant mixture at a temperature no greater than about 160 C., maintaining the temperature of'his dry asphalt product at a flow temperature, and then flowing the resultant asphalt composition into a storage container.

To place the present invention in its proper content, it should be noted that the concentration and containment of radionuclides of radioactive sludges with asphalt is known. A sludge is an aqueous precipitate of solid particles which contains the radioactivity. The water content of sludges is essentially non-radioactive. The object in using asphalt in such a case is to reduce the volume of the sludge by removing its water content in order to contain the radioactive precipitated phase within the volume of the asphalt. In that sense, the process is similar to the one described here. However, the water content of a viscous sludge-asphalt mixture can only be removed by heating said mixture to a temperature in excess of 200 C. while vigorously agitating the mixture. Moreover, water removal is accompanied by sputtering which adds to the technical difficulty and increases the safety hazards. In addition to this, water removal at these high tempera- Patented Jan. 17, 1967 tures presents an ever-present danger of carrying over these conditions, water removal by evaporation takes place at a temperature near the boiling point of the solution.

3 As the water is removed, the emulsion is destroyed and the particles of asphalt begin to agglomerate. However, be-

fore complete agglomeration has taken place, substantially all of the water will have been removed under the relatively mild conditions described without violent sputtering.

After the water is removed, the resultant asphalt product will be found to contain virtually all of the solid content originally in solution, including the radionuclides, within a relatively small asphalt volume. In some cases, the collected aqueous condensate will be found to contain so little radioactivity as to be safely discharged into soil environments. On the other hand, where the radionuclide content is abovebiologically safe threshold values, previous treatment with the emulsified asphalt still constitutes an effective process treatment because the aqueous condensate is now in condition for further treatment by standard ion exchange adsorption or precipitation means to remove substantially all of the radionuclide content.

After water removal, the asphalt is maintained at a temperature at which it will flow freely from the evaporator. Most asphalt compositions containing up to 60% solids resulting from the treatment of radioactive waste solutions will fiow freely from the evaporator at C. If the solid content is appreciably greater, higher temperatures are needed to obtain a free-flowing product. For example, an asphalt loaded with 80% by weight solids will not flow readily until a temperature of C. is reached.

The asphalt emulsion compositions useful for the purposes of this invention are commercially available products which are normally used in the maintenance and construction of roads and pavement. More particularly, the asphalt paving emulsions useful in removing and containing radionuclides from an aqueous solution are those defined in the United States Government Federal Specification SS-A-674b, dated November 25, 1965, and SS-A-00674c dated August 20, 1962, as issued by the Materials Specification Department of the General Services Administration Agency of the United States Federal Government.

The emulsified asphalt compositions useful for this invention may vary widely within the framework of the aforementioned specification in order to attain the objects of this invention. It is most desirable to use an emulsified asphalt which yields a resilient product at room temperature after it has been loaded with solids. A satisfactory product for practicing our process is that asphalt emulsion defined in the aforementioned Federal specifications as type RS2, a rapid setting, high viscosity emulsion, a composition normally used in the surface treatment of roads. This type of asphalt emulsion contains about 63 weight percent asphalt, 2% emulsifying agent, and the remainder water.

Having defined our invention in general terms together with operating parameters, the following embodiment is provided by way of example, and is not to be construed as limiting the scope of our invention.

EXAMPLE I In the course of separating nuclear fuel values by liquidliquid solvent extraction techniques derived from the dissolution of spent nuclear fuel elements, large volumes of aqueous stripping solutions are generated. The strip solutions contain large amounts of salting out agents, as well as fission product radionuclides. Such strip solutions are generally classified as intermediate waste solutions, as previously defined, and constitutes a major problem of disposal. The process of this invention is eminently suitable for use in removing and containing the major percentage of inorganic salts and radionuclides from such strip solutions into a biologically safe and easily handled asphalt mass, as will be hereinafter described.

One pound of an RS2 emulsifiedasphalt, as previously defined, was mixed with mild stirring with 2.67 pounds of an intermediate waste solution in an evaporator unit containing means for collecting an aqueous condensate. After evaporating the water, the resultant mixture was heated to a temperature of 160 C. The aqueous condensate was collected during evaporation. At the end of this time all of the water had evaporated and a solid viscous mass of liquid asphalt containing solids remained in the evaporator. The asp-halt was poured from the evaporator at a temperature of 130 C. into a container and allowed to cool. The following data represents a material balance breakdown of a representative run conducted in accordance with this invention.

Sodium 16.06 w. peroent.

Aluminum 4.62 g./l 0.60 w. percent. Sulfate 28.0 g./l 3.65 w. percent. Chloride 1.71 g./l 0.22. Hydroxide 37.9 g./l--. 4.94 w. percent. Nitrate 226 g.ll 29.48 w. percent. Water 853.77 g./l 336 g./l. 1,000 g./l Asphalt plusemul- 624 g./l. 44.22 w. persifier. cent. Total Activity 4.82 curies 2.81X- 9.39 euries per gal. curios/gal. per gal.

RADIOACTIVITY BREAKDOWN Percent In Feed Aqueous Condensate, Percent (35-137 99 99. 9 Ell-106 1. 0 0. 1

Others:

Volume reduction volumes of waste solution 1 95 volume of asphalt product Material balance In. level waste g 385 Emulsified asphalt g 156 Total g. 541

dm a. salts Balance of material is that coating the surfaces of the evaporator and stirrer.

The asphalt product, as shown in the above data, contains 60% solids and essentially all of the inorganic salt content of the feed solution. This asphalt product was then leach tested in static water over a period of several months by examining the radionuclide content of the leachant collected at intervals of time during this period. The leaching solutions were tested for their cesium-137 and ruthenium-J06 content, and showed that the average leach rate for cesium-137 was about 5X l0 g./cm. of

exposed surface per day; and for ruthenium-106, the average leach rate was 7 10- g./ cc. per day. It was found that essentially all of the inorganic salts as well as the Cs-l37 and Ru-106 content was incorporated into the asphaltic mass, as shown in the material balance data above. While the aqueous condensate could not be discharged directly into natural soil or streams, standard treatment by flow through readily available ion exchange resins such as strong acid phenolic resin will easily remove sufficient radionuclide content to provide a biologically safe aqueous efiiuent. v

This example demonstrates the value of the process in treating radioactive waste solutions containing large amounts of inorganic salts to concentrate and contain the major percentage of the solids content in a. readily available asphalt material. The solid asphalt product is an effective container for the solids and the aqueous efiluent is now in condition for disposal to soil or natural stream environments, or easily converted to a biologically safe solution by standard ion-exchange or complexing techniques. While the utility of the process has been demonstrated for treatment of a solution which is heavily loaded in inorganic salts, the advantages of the process will be realized in treating any intermediate level radioactive waste solution.

Having thus described our invention, we claim:

1. A method of concentrating and containing the solid content of an intermediate level radioactive solution which comprises mixing said solution with emulsified asphalt, evaporating essentially all of the water content of said mixture at a temperature no greater than C., and then flowing the resultant asphalt composition into a container to solidify in a desired configuration.

2. A method of concentrating and containing the solid content of an intermediate level nadioactive solution which comprises mixing said solution with emulsified asphalt,

evaporating essentially all of the water content of said mixture at the boiling point of the said mixture, and then flowing the resultant asphalt composition into a container to solidify in a desired configuration.

References Cited by the Examiner UNITED STATES PATENTS 3,142,648 7/1964 Lefillatre et a1 252 30l.1

6 OTHER REFERENCES

Patent Citations
Cited PatentFiling datePublication dateApplicantTitle
US3142648 *Dec 6, 1962Jul 28, 1964Commissariat Energie AtomiqueProcess for the production of solid products containing radioactive waste material and products obtained by this process
Referenced by
Citing PatentFiling datePublication dateApplicantTitle
US3971732 *Dec 5, 1974Jul 27, 1976Gesellschaft Fur Kernforschung M.B.H.Apparatus for fixing radioactive waste
US4139488 *Jun 22, 1976Feb 13, 1979Vereinigte Edelstahlwerke AktiengesellschaftMethod of preparing solid radioactive or toxic waste for long-term storage
US4180476 *Dec 14, 1977Dec 25, 1979Commissariat A L'energie AtomiqueProcess for the extraction of fission products
US4643846 *Nov 19, 1984Feb 17, 1987Doryokuro Kakunenryo Kaihatsu JigyodanProcess for the treatment of radioactive sodium
US4832874 *Jul 6, 1987May 23, 1989Ebara CorporationAsphalts blended with polyolefin
US4847006 *Aug 29, 1986Jul 11, 1989Hoeglund Lars OSwelling, encapsulation, radioactive materials
Classifications
U.S. Classification588/5, 976/DIG.385
International ClassificationG21F9/16
Cooperative ClassificationG21F9/167
European ClassificationG21F9/16D