GB2048555A - Plutonium waste fixation - Google Patents

Plutonium waste fixation Download PDF

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Publication number
GB2048555A
GB2048555A GB7915298A GB7915298A GB2048555A GB 2048555 A GB2048555 A GB 2048555A GB 7915298 A GB7915298 A GB 7915298A GB 7915298 A GB7915298 A GB 7915298A GB 2048555 A GB2048555 A GB 2048555A
Authority
GB
United Kingdom
Prior art keywords
block
glaze
cement
wastes
firing
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Withdrawn
Application number
GB7915298A
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
British Nuclear Fuels Ltd
Original Assignee
British Nuclear Fuels Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by British Nuclear Fuels Ltd filed Critical British Nuclear Fuels Ltd
Priority to GB7915298A priority Critical patent/GB2048555A/en
Priority to DE19803015885 priority patent/DE3015885A1/en
Priority to JP5772480A priority patent/JPS55151299A/en
Priority to FR8009876A priority patent/FR2455784A1/en
Publication of GB2048555A publication Critical patent/GB2048555A/en
Withdrawn legal-status Critical Current

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Classifications

    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21FPROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
    • G21F9/00Treating radioactively contaminated material; Decontamination arrangements therefor
    • G21F9/28Treating solids
    • G21F9/34Disposal of solid waste
    • G21F9/36Disposal of solid waste by packaging; by baling
    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21FPROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
    • G21F9/00Treating radioactively contaminated material; Decontamination arrangements therefor
    • G21F9/28Treating solids
    • G21F9/30Processing
    • G21F9/301Processing by fixation in stable solid media
    • G21F9/302Processing by fixation in stable solid media in an inorganic matrix
    • G21F9/304Cement or cement-like matrix

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  • Engineering & Computer Science (AREA)
  • Physics & Mathematics (AREA)
  • General Engineering & Computer Science (AREA)
  • High Energy & Nuclear Physics (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

A process for the containment of radioactive wastes involves fixing the wastes in a high-alumina cement, firing to form an integral solid body and glazing the surface of the solid body. A clay can be included with the cement to assist the glazing step.

Description

SPECIFICATION Plutonium waste fixation The present invention concerns the containment or fixing of radioactive waste products.
Many processes have been proposed for the containment or fixing of radioactive wastes and resulting in products which are stable and safe. The final products should satisfy a number of conditions and in particular they should be (a) chemically inert (b) monolithic form so that dispersion to the environment is difficult (c) resistant to leaching by known solvents (d) preferably capable of retreatment should it become necessary to recover the radioactive wastes.
According to the present invention a process for the containment of radioactive wastes comprises fixing the wastes in a high-alumina cement, firing to form an integral solid body and glazing the surface of the solid body.
Preferably, a clay is included with the cement to provide a smooth surface finish to the solid body and to assist in the application of the glazing.
High-alumina cement which comprises calcium aluminates has desirable green and fired properties.
Its setting and hardening times are approximately 4 and 8 hours respectively and ceramic bonding is induced on firing to temperatures in excess of about 1 000 C.
The invention will be described further, by way of example, with reference to the following embodiment.
A mixture of high-alumina cement, radioactive waste and clay is blended and hydrated to form a slurry. The slurry is vibrated in a mould and cured in a damp atmosphere. The composition can comprise 40% cement, 50% waste and 10% clay, preferably a whiteware clay. Such a composition is derived on the basis of friability, surface finish and drying properties.
After curing, the resulting block is fired at a temperature of about 1 000"C for approximately 2 hours to remove all combined water and to induce ceramic bonding. The block is then coated wtih a glaze and glostfired to about 1010"C for about 10 minutes. The glaze is a thin glassy layer formed on the surface of the block to seal the outer pores. For best finish it is desirable that the applied glaze is in compression, that is, the block should possess a greater coefficient of thermal expansion than the glaze. This condition is insured by the addition of approximately 20% quartz in the glaze solution which has the effect of reducing the thermal expansion coefficient of the glaze to below that of the block.The preferred glazes are coloured, leadless varieties which contain metallic stains and a low boron oxide content. Such glazes have a high viscosity value at the fusion temperature and provide a better coverage of the block.
It is important to achieve a smooth surface finish on the green block and to avoid holes which could result in blow-holes in the glaze. The thickness of the glaze applied to the block can be about 0.5 mm.
The radioactive wastes can be actinide containing wastes, such as ash from incineration or crushed contaminated glassware. Conveniently, the cement/ waste slurry is moulded into a flat cylindrical block prior to the application of the glaze. However, other shapes of block are clearly possible. The invention is not restricted to the composition percentages given in the above example nor to the particular firing temperatures and times.
1. A process for the containment of radioactive wastes characterised by fixing the wastes in highalumina cement, firing to form an integral solid body and glazing the surface of the solid body.
2. A process according to claim 1 characterised by including a clay with the cement to provide a smooth surface finish to the solid body and to assist in the application of the glazing.
3. A process according to claim 2 characterised by moulding a cement/waste slurry into a block, curing and thereafter firing the block.
4. A process according to claim 3 characterised by firing the block at a temperature in the region of 1 0000C for approximately 2 hours.
5. A process according to claim 1, characterised by including 20% quartz in the glaze to reduce the thermal expansion coefficient of the glaze to below that of the block.
6. A process for the containment of radioactive wastes according to claim 1 and substantially as herein particularly described.
**WARNING** end of DESC field may overlap start of CLMS **.

Claims (6)

**WARNING** start of CLMS field may overlap end of DESC **. SPECIFICATION Plutonium waste fixation The present invention concerns the containment or fixing of radioactive waste products. Many processes have been proposed for the containment or fixing of radioactive wastes and resulting in products which are stable and safe. The final products should satisfy a number of conditions and in particular they should be (a) chemically inert (b) monolithic form so that dispersion to the environment is difficult (c) resistant to leaching by known solvents (d) preferably capable of retreatment should it become necessary to recover the radioactive wastes. According to the present invention a process for the containment of radioactive wastes comprises fixing the wastes in a high-alumina cement, firing to form an integral solid body and glazing the surface of the solid body. Preferably, a clay is included with the cement to provide a smooth surface finish to the solid body and to assist in the application of the glazing. High-alumina cement which comprises calcium aluminates has desirable green and fired properties. Its setting and hardening times are approximately 4 and 8 hours respectively and ceramic bonding is induced on firing to temperatures in excess of about 1 000 C. The invention will be described further, by way of example, with reference to the following embodiment. A mixture of high-alumina cement, radioactive waste and clay is blended and hydrated to form a slurry. The slurry is vibrated in a mould and cured in a damp atmosphere. The composition can comprise 40% cement, 50% waste and 10% clay, preferably a whiteware clay. Such a composition is derived on the basis of friability, surface finish and drying properties. After curing, the resulting block is fired at a temperature of about 1 000"C for approximately 2 hours to remove all combined water and to induce ceramic bonding. The block is then coated wtih a glaze and glostfired to about 1010"C for about 10 minutes. The glaze is a thin glassy layer formed on the surface of the block to seal the outer pores. For best finish it is desirable that the applied glaze is in compression, that is, the block should possess a greater coefficient of thermal expansion than the glaze. This condition is insured by the addition of approximately 20% quartz in the glaze solution which has the effect of reducing the thermal expansion coefficient of the glaze to below that of the block.The preferred glazes are coloured, leadless varieties which contain metallic stains and a low boron oxide content. Such glazes have a high viscosity value at the fusion temperature and provide a better coverage of the block. It is important to achieve a smooth surface finish on the green block and to avoid holes which could result in blow-holes in the glaze. The thickness of the glaze applied to the block can be about 0.5 mm. The radioactive wastes can be actinide containing wastes, such as ash from incineration or crushed contaminated glassware. Conveniently, the cement/ waste slurry is moulded into a flat cylindrical block prior to the application of the glaze. However, other shapes of block are clearly possible. The invention is not restricted to the composition percentages given in the above example nor to the particular firing temperatures and times. CLAIMS
1. A process for the containment of radioactive wastes characterised by fixing the wastes in highalumina cement, firing to form an integral solid body and glazing the surface of the solid body.
2. A process according to claim 1 characterised by including a clay with the cement to provide a smooth surface finish to the solid body and to assist in the application of the glazing.
3. A process according to claim 2 characterised by moulding a cement/waste slurry into a block, curing and thereafter firing the block.
4. A process according to claim 3 characterised by firing the block at a temperature in the region of 1 0000C for approximately 2 hours.
5. A process according to claim 1, characterised by including 20% quartz in the glaze to reduce the thermal expansion coefficient of the glaze to below that of the block.
6. A process for the containment of radioactive wastes according to claim 1 and substantially as herein particularly described.
GB7915298A 1979-05-02 1979-05-02 Plutonium waste fixation Withdrawn GB2048555A (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
GB7915298A GB2048555A (en) 1979-05-02 1979-05-02 Plutonium waste fixation
DE19803015885 DE3015885A1 (en) 1979-05-02 1980-04-24 METHOD FOR BINDING RADIOACTIVE WASTE
JP5772480A JPS55151299A (en) 1979-05-02 1980-04-30 Plutonium waste fixation
FR8009876A FR2455784A1 (en) 1979-05-02 1980-04-30 METHOD FOR CONTAINING RADIO-ACTIVE WASTE

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
GB7915298A GB2048555A (en) 1979-05-02 1979-05-02 Plutonium waste fixation

Publications (1)

Publication Number Publication Date
GB2048555A true GB2048555A (en) 1980-12-10

Family

ID=10504912

Family Applications (1)

Application Number Title Priority Date Filing Date
GB7915298A Withdrawn GB2048555A (en) 1979-05-02 1979-05-02 Plutonium waste fixation

Country Status (4)

Country Link
JP (1) JPS55151299A (en)
DE (1) DE3015885A1 (en)
FR (1) FR2455784A1 (en)
GB (1) GB2048555A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0071927A1 (en) * 1981-08-07 1983-02-16 Forschungszentrum Jülich Gmbh Process for solidifying radioactive wastes
GB2130784A (en) * 1982-10-07 1984-06-06 Ronald Leslie Attwell Filling interstices between pieces of material
WO2006047070A1 (en) * 2004-10-22 2006-05-04 Studsvik, Inc. In-container mineralization
US7531152B2 (en) 2000-10-19 2009-05-12 Studsvik, Inc. Mineralization of alkali metals, sulfur, and halogens
US10593437B2 (en) 2015-01-30 2020-03-17 Studsvik, Inc. Methods for treatment of radioactive organic waste

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE3219114A1 (en) * 1982-05-21 1983-11-24 Kernforschungsz Karlsruhe METHOD FOR IMPROVING THE PROPERTIES OF RESTORATION OF RADIOACTIVE FASTE WASTE
JPS58218696A (en) * 1982-06-15 1983-12-19 株式会社東芝 Method of processing radioactive waste
JPS61191999A (en) * 1985-02-20 1986-08-26 動力炉・核燃料開発事業団 Method of stabilizing and treating uranium slag or uranium smelting waste slag
JP2014235024A (en) * 2013-05-31 2014-12-15 株式会社E&Eテクノサービス Manufacturing method of solidified body, and solidified body manufactured by the same

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3093593A (en) * 1958-07-14 1963-06-11 Coors Porcelain Co Method for disposing of radioactive waste and resultant product
NL235423A (en) * 1959-01-19
FR1246848A (en) * 1959-10-13 1960-11-25 Commissariat Energie Atomique Process for the disposal of radioactive waste and products obtained by this process
US3988258A (en) * 1975-01-17 1976-10-26 United Nuclear Industries, Inc. Radwaste disposal by incorporation in matrix
DE2726087C2 (en) * 1977-06-10 1978-12-21 Kernforschungszentrum Karlsruhe Gmbh, 7500 Karlsruhe Process for the final disposal-ready, environmentally friendly solidification of "and moderately radioactive and / or actinide-containing, aqueous waste concentrates or of fine-grained solid waste suspended in water

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0071927A1 (en) * 1981-08-07 1983-02-16 Forschungszentrum Jülich Gmbh Process for solidifying radioactive wastes
GB2130784A (en) * 1982-10-07 1984-06-06 Ronald Leslie Attwell Filling interstices between pieces of material
US7476194B2 (en) 1999-10-20 2009-01-13 Studsvik, Inc. In-container mineralization
US7531152B2 (en) 2000-10-19 2009-05-12 Studsvik, Inc. Mineralization of alkali metals, sulfur, and halogens
WO2006047070A1 (en) * 2004-10-22 2006-05-04 Studsvik, Inc. In-container mineralization
US10593437B2 (en) 2015-01-30 2020-03-17 Studsvik, Inc. Methods for treatment of radioactive organic waste

Also Published As

Publication number Publication date
FR2455784A1 (en) 1980-11-28
JPS55151299A (en) 1980-11-25
DE3015885A1 (en) 1980-11-13

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WAP Application withdrawn, taken to be withdrawn or refused ** after publication under section 16(1)