EP0242890A2 - Barrier against the release of radionuclides from vitrified radioactive wastes and process for accomplishing it - Google Patents
Barrier against the release of radionuclides from vitrified radioactive wastes and process for accomplishing it Download PDFInfo
- Publication number
- EP0242890A2 EP0242890A2 EP87200213A EP87200213A EP0242890A2 EP 0242890 A2 EP0242890 A2 EP 0242890A2 EP 87200213 A EP87200213 A EP 87200213A EP 87200213 A EP87200213 A EP 87200213A EP 0242890 A2 EP0242890 A2 EP 0242890A2
- Authority
- EP
- European Patent Office
- Prior art keywords
- glass
- oxides
- radioactive wastes
- container
- radionuclides
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Withdrawn
Links
Classifications
-
- G—PHYSICS
- G21—NUCLEAR PHYSICS; NUCLEAR ENGINEERING
- G21F—PROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
- G21F9/00—Treating radioactively contaminated material; Decontamination arrangements therefor
- G21F9/28—Treating solids
- G21F9/34—Disposal of solid waste
- G21F9/36—Disposal of solid waste by packaging; by baling
Definitions
- the present invention relates to a barrier against the release of radionuclides from vitrified radioactive wastes and to the process for accomplishing it.
- the liquid radioactive wastes are, presently, concentrated to dryness, incorporated inside solid materials (glass, ceramic, cement) and then stored inside underground cavities, wherein they are out of contact, as extensively as possible, with such agents, as water, which tend to disperse the radionuclides.
- Processes are known, according to which the radioactive wastes undergo solidification inside ceramic matrices constituted by mixtures of Ti, Al, Zr, Ca, Ba oxides, Such crystalline materials display the advantage of incorporating a large amount of radioactive material (up to 70%) and of being endowed with a high corrosion strength, but suffer from the disadvantage of requiring high costs.
- the most widespread processes consist in dispersing the wastes inside monolithic shapes of glass, which are in their turn inserted inside metal containers.
- Such processes are basically of three types.
- the first type, ICGM - "in-can glass melting” - consists in placing both the dried radioactive wastes and the glass inside the metal container and melting all of the material.
- the second type, JHGM - "joule-heated glass melting” - involves the melting of both the wastes and the glass inside a furnace, and the subsequent introduction of the obtained molten material inside the container.
- the third type, GC -"glass-ceramic” - differs from the second one only in that the container undergoes a high-temperature treatment, so that a partial glass crystallization may occur.
- a barrier constituted by a layer of suitably selected oxides, between the glass and the metal container, obviates such drawbacks.
- the oxides used are Al2O3, TiO2, ZrO2, either individually taken, or taken as couples, in any percentages, or taken all together, in any percentages and in any crystalline forms.
- the process for the accomplishment of such a barrier comprises the following steps:
- the process comprises moreover, as an important step besides the above mentioned four steps, a fifth step consisting in keeping the layer of oxides (the oxide powder applied onto the glass surface being included) and the molten glass in contact at a temperature of from 950°C to 1350°C for a time period ranging from a few minutes up to many hours (in particular, of 2-3 hours).
- the purpose of the oxide layer is to act as a further obstacle to the contact of water with the glass, and to bring in the nearby of, and within, the surface layers, Al3+, Ti4+, Zr3+ ions, in as much as such ions give rise to the formation, on the same glass, of a passivating layer, which decreases the leaching rate, up to nullifying it. From this viewpoint, the efficaciousness of the protection is not impaired by the presence of cracks or of a dusty consistency.
- an AISI 316 stainless-steel container having a square cross section of 2.5 ⁇ 2.5 cm, 1 cm high is painted, by means of a brush, with Ceramabond by AREMCO, an Al2O3 -based ceramic paint; it is then dried at 120°C. After being filled with Pyrex type glass, it is placed inside a muffle. The container is heated to 1000° and is kept at this temperature for half an hour. The muffle is turned off and the sample is extracted when the temperature is of 350°C.
- the Al2O3 layer results compact.
- the inner surface of a 3.5-cm high steel cylinder of 3.5 cm in diameter is painted, by a brush, with an aqueous solution of alpha-Al2O3 (Alcoa Al6), containing 2% polyvinyl alcohol as bonding agent. After being dried at 150°C, the cylinder is filled with minced Pyrex and is maintained at 1050°C for 2 hrs. After turning off the muffle, the sample is extracted when the temperature has decreased to 200°C. The coating results unbroken.
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- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Physics & Mathematics (AREA)
- General Engineering & Computer Science (AREA)
- High Energy & Nuclear Physics (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
- The present invention relates to a barrier against the release of radionuclides from vitrified radioactive wastes and to the process for accomplishing it.
- The liquid radioactive wastes are, presently, concentrated to dryness, incorporated inside solid materials (glass, ceramic, cement) and then stored inside underground cavities, wherein they are out of contact, as extensively as possible, with such agents, as water, which tend to disperse the radionuclides. Processes are known, according to which the radioactive wastes undergo solidification inside ceramic matrices constituted by mixtures of Ti, Al, Zr, Ca, Ba oxides, Such crystalline materials display the advantage of incorporating a large amount of radioactive material (up to 70%) and of being endowed with a high corrosion strength, but suffer from the disadvantage of requiring high costs. The most widespread processes consist in dispersing the wastes inside monolithic shapes of glass, which are in their turn inserted inside metal containers.
- Such processes are basically of three types. The first type, ICGM - "in-can glass melting" - consists in placing both the dried radioactive wastes and the glass inside the metal container and melting all of the material. The second type, JHGM - "joule-heated glass melting" - involves the melting of both the wastes and the glass inside a furnace, and the subsequent introduction of the obtained molten material inside the container. The third type, GC -"glass-ceramic" - differs from the second one only in that the container undergoes a high-temperature treatment, so that a partial glass crystallization may occur.
- These processes show low costs, both thanks to the wide availability of the raw material, glass, and due to the simpleness of the processes. However the possibility exists, in the long term, of tightness losses, by the glass, caused by the corrosive water action - the leaching.
- It was surprisingly found that the insertion of a barrier, constituted by a layer of suitably selected oxides, between the glass and the metal container, obviates such drawbacks. The oxides used are Al₂O₃, TiO₂, ZrO₂, either individually taken, or taken as couples, in any percentages, or taken all together, in any percentages and in any crystalline forms. The process for the accomplishment of such a barrier comprises the following steps:
- 1) coating the inner surface of a metal container with a, preferably aqueous, suspension of oxides selected from Al₂O₃ and/or ZrO₂ and/or TiO₂, so to form a layer having a thickness comprised within the range of from 0.05 to 10 mm, preferably of from 0.1 mm to 3 mm.
- 2) concentrating to dryness, heating up to a temperature comprised within the range of from 110 to 170°C, preferably of 150°C.
- 3) pouring into the metal container, processed as described under (1) and (2), the glassy substance, as well as the radioactive wastes in either solid or molten form.
(In case the glassy substance and the wastes are poured into the container as solids, they are molten inside the container and are then solidified according to the ICGM and GC processes). - 4) covering the upper portion by using the following procedures:
- a) smear the upper glassy surface with a powder of the oxides as per point (1) and mechanically press such a powder, so to form a compact layer having a thickness equal to that applied onto the inner container surface.
- b) place above the glassy surface a metal cover, the inner surface of which has been previously processed as described under (1) and (2).
- The process comprises moreover, as an important step besides the above mentioned four steps, a fifth step consisting in keeping the layer of oxides (the oxide powder applied onto the glass surface being included) and the molten glass in contact at a temperature of from 950°C to 1350°C for a time period ranging from a few minutes up to many hours (in particular, of 2-3 hours).
The purpose of the oxide layer is to act as a further obstacle to the contact of water with the glass, and to bring in the nearby of, and within, the surface layers, Al³⁺, Ti⁴⁺, Zr³⁺ ions, in as much as such ions give rise to the formation, on the same glass, of a passivating layer, which decreases the leaching rate, up to nullifying it. From this viewpoint, the efficaciousness of the protection is not impaired by the presence of cracks or of a dusty consistency. - The purpose of the following Examples is to illustrate the invention; they are not to be considered in a limitative sense.
- The inner surface of an AISI 316 stainless-steel container having a square cross section of 2.5×2.5 cm, 1 cm high, is painted, by means of a brush, with Ceramabond by AREMCO, an Al₂O₃ -based ceramic paint; it is then dried at 120°C. After being filled with Pyrex type glass, it is placed inside a muffle. The container is heated to 1000° and is kept at this temperature for half an hour. The muffle is turned off and the sample is extracted when the temperature is of 350°C.
- The Al₂O₃ layer results compact.
- The inner surface of a 3.5-cm high steel cylinder of 3.5 cm in diameter is painted, by a brush, with an aqueous solution of alpha-Al₂O₃ (Alcoa Al6), containing 2% polyvinyl alcohol as bonding agent. After being dried at 150°C, the cylinder is filled with minced Pyrex and is maintained at 1050°C for 2 hrs. After turning off the muffle, the sample is extracted when the temperature has decreased to 200°C. The coating results unbroken.
Claims (5)
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
IT19550/86A IT1190612B (en) | 1986-02-26 | 1986-02-26 | BARRIER AGAINST THE RELEASE OF RADIONUCLIDES FROM VITRIFIED RADIOACTIVE SLAGS AND PROCESS FOR ITS REALIZATION |
IT1955086 | 1986-02-26 |
Publications (2)
Publication Number | Publication Date |
---|---|
EP0242890A2 true EP0242890A2 (en) | 1987-10-28 |
EP0242890A3 EP0242890A3 (en) | 1989-05-17 |
Family
ID=11158969
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP87200213A Withdrawn EP0242890A3 (en) | 1986-02-26 | 1987-02-11 | Barrier against the release of radionuclides from vitrified radioactive wastes and process for accomplishing it |
Country Status (2)
Country | Link |
---|---|
EP (1) | EP0242890A3 (en) |
IT (1) | IT1190612B (en) |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2375696A1 (en) * | 1976-12-21 | 1978-07-21 | Asea Ab | PROCESS FOR ENCLOSING USED NUCLEAR FUEL OR WASTE NUCLEAR FUEL |
US4404129A (en) * | 1980-12-30 | 1983-09-13 | Penberthy Electromelt International, Inc. | Sequestering of radioactive waste |
DE3212507A1 (en) * | 1982-04-03 | 1983-10-13 | Steag Kernenergie Gmbh, 4300 Essen | Casks for the storage of radioactive substances having a ceramic corrosion-protective layer surrounding the substances |
FR2575319A1 (en) * | 1984-12-21 | 1986-06-27 | Sgn Soc Gen Tech Nouvelle | Method of leakproof packaging for a container enclosing toxic substances |
-
1986
- 1986-02-26 IT IT19550/86A patent/IT1190612B/en active
-
1987
- 1987-02-11 EP EP87200213A patent/EP0242890A3/en not_active Withdrawn
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2375696A1 (en) * | 1976-12-21 | 1978-07-21 | Asea Ab | PROCESS FOR ENCLOSING USED NUCLEAR FUEL OR WASTE NUCLEAR FUEL |
US4404129A (en) * | 1980-12-30 | 1983-09-13 | Penberthy Electromelt International, Inc. | Sequestering of radioactive waste |
DE3212507A1 (en) * | 1982-04-03 | 1983-10-13 | Steag Kernenergie Gmbh, 4300 Essen | Casks for the storage of radioactive substances having a ceramic corrosion-protective layer surrounding the substances |
FR2575319A1 (en) * | 1984-12-21 | 1986-06-27 | Sgn Soc Gen Tech Nouvelle | Method of leakproof packaging for a container enclosing toxic substances |
Also Published As
Publication number | Publication date |
---|---|
IT1190612B (en) | 1988-02-16 |
EP0242890A3 (en) | 1989-05-17 |
IT8619550A1 (en) | 1987-08-26 |
IT8619550A0 (en) | 1986-02-26 |
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Free format text: STATUS: THE APPLICATION IS DEEMED TO BE WITHDRAWN |
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18D | Application deemed to be withdrawn |
Effective date: 19920507 |
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RIN1 | Information on inventor provided before grant (corrected) |
Inventor name: DE ANGELIS, BERNARDO |