USH1013H - Process for the immobilization and volume reduction of low level radioactive wastes from thorium and uranium processing - Google Patents

Process for the immobilization and volume reduction of low level radioactive wastes from thorium and uranium processing Download PDF

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Publication number
USH1013H
USH1013H US07/392,327 US39232789A USH1013H US H1013 H USH1013 H US H1013H US 39232789 A US39232789 A US 39232789A US H1013 H USH1013 H US H1013H
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US
United States
Prior art keywords
thorium
mixture
weight
low level
immobilization
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.)
Abandoned
Application number
US07/392,327
Inventor
Richard F. Wormsbecher
Alan T. Chapman, Jr.
David N. Hill
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.)
WR Grace and Co Conn
Original Assignee
WR Grace and Co Conn
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 WR Grace and Co Conn filed Critical WR Grace and Co Conn
Priority to US07/392,327 priority Critical patent/USH1013H/en
Priority to AU60176/90A priority patent/AU6017690A/en
Priority to BR909003923A priority patent/BR9003923A/en
Priority to FR9010270A priority patent/FR2652193A1/en
Application granted granted Critical
Publication of USH1013H publication Critical patent/USH1013H/en
Abandoned 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
    • G21F9/30Processing
    • G21F9/301Processing by fixation in stable solid media
    • G21F9/302Processing by fixation in stable solid media in an inorganic matrix
    • G21F9/305Glass or glass like matrix

Definitions

  • This invention relates to a process of treating radioactive waste, and more specifically to a process for the immobilization and volume reduction of low level radioactive wastes produced by Rare Earth recovery processes.
  • pitchblende or monazite produces low level radioactive waste residues which bear thorium, and/or uranium and their natural decay daughters.
  • these thorium and/or uranium bearing wastes are in the form of slurries and, as such, present disposal problems due to volume and containment considerations.
  • U.S. Pat. No. 4,725,383 teaches a process for volume reduction and solidification of a radioactive waste solution by adding ZnO or a mixture of ZnO with Al 2 O 3 and/or CaO, dehydrating the mixture, and melting to produce a vitrified solid.
  • Another process for volume reduction and immobilization of waste is taught by U.S. Pat. No. 4,395,367 wherein fission waste is treated by mixing a glass forming agent, a metal oxide and a reducing agent with the fission waste, and heating the mixture until melted.
  • a method of treating the radioactive waste residues which result from the processing of pitchblende or monazite or other thorium or uranium bearing minerals which comprises forming a mixture of a dried radioactive thorium and/or uranium containing waste residue and a fluxing agent, melting the mixture to form molten glass, and pouring the molten glass into a suitable container.
  • the present invention is directed to a process of treating the solid thorium and/or uranium containing radioactive waste obtained from the processing of monazite, pitchblende, xenotine, apatite, bastnasite or other rare-earth bearing ores.
  • the process of this invention comprises mixing the dried waste residue with about 0.1 to 50% by weight of a fluxing agent, optionally about 0.1 to 50% by weight SiO 2 , and heating the mixture to a molten glassy state, and pouring the molten glass into a suitable container for burial or storage.
  • the waste residues capable of being treated under this process are any solid radioactive waste residues which bear thorium or uranium, and their natural decay daughters.
  • Appropriate fluxing agents for use in the invention include, but are not limited to, NaOH, Na 2 CO 3 , NaBO 2 , Na 2 B 4 O 7 or mixtures thereof.
  • Silica sand may also be added to the mixture if necessary.
  • the specific proportions of fluxing agent and silica sand to be added to the mixture can vary depending on the desired melt viscosity and are not per se critical to the invention provided that adequate pour viscosities are developed in the mixture.
  • the preferred melt viscosities of this invention are in the range 1000 to 3000 centipoise at pour temperatures of 1093° to 1260° C.
  • the dried radioactive waste residues, together with the fluxing agent and optionally silica sand, may be added batchwise or in a continuous process to an appropriate glass furnace.
  • the furnace is typically heated to a temperature in the range 1200° to 1800° C., and the glass residence times in the melter are between 2 and 24 hours. Furnace temperatures and glass residence times are generally interdependent. Therefore, if a temperature higher than 1800° C. is used, a correspondingly shorter residence time will be required to achieve the desired molten glass state.
  • the molten glass waste residues are then poured into steel or stainless steel, or other similar containers in which the melt is cooled to form a solid, vitrified mass, whereupon the containers can be sealed by welding or other suitable method.
  • the final percentage of thorium and uranium present in the reduced volume vitrified waste is about 0.1 to 50% by weight and 0.01 to 10% by weight respectively.
  • Thorium bearing radioactive waste residues in the form of a thick slurry were obtained from a monazite cracking plant. The initial density of this residue was 1.85 g/cc.
  • the waste residues were dried, ground to a fine powder, and mixed with 20% by weight Na 2 B 4 O 7 . The mixture was heated to 1540° C. for two hours to produce a molten glass that was readily pourable. The glass residue was cooled to room temperature and had a density of 4.0 g/cc. After accounting for the weight loss due to water evaporation, and weight gain from the addition of the Na 2 B 4 O 7 , this represents approximately a 70% volume reduction.

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

Abstract

A process for the immobilization and volume reduction of low level radioactive wastes produced from the processing of rare earth recovery processes comprising mixing the waste residue with 0.1 to 50% of a fluxing agent and optionally with 0.1 to 50% silica sand, heating the mixture to a temperature in the range of about 1200° to 1800° C. to form molten glass, and pouring the molten glass into a suitable container to cool and solidify into a vitrified mass. Suitable fluxing agents include sodium hydroxide, sodium carbonate, sodium borate, sodium perborate, or mixtures thereof.

Description

BACKGROUND OF THE INVENTION
1. Field of Invention
This invention relates to a process of treating radioactive waste, and more specifically to a process for the immobilization and volume reduction of low level radioactive wastes produced by Rare Earth recovery processes.
2. Description of the Prior Art
The processing of pitchblende or monazite produces low level radioactive waste residues which bear thorium, and/or uranium and their natural decay daughters. Typically, these thorium and/or uranium bearing wastes are in the form of slurries and, as such, present disposal problems due to volume and containment considerations.
Various processes are known in the prior art to concentrate and immobilize toxic and/or radioactive wastes. For example, U.S. Pat. No. 4,725,383 teaches a process for volume reduction and solidification of a radioactive waste solution by adding ZnO or a mixture of ZnO with Al2 O3 and/or CaO, dehydrating the mixture, and melting to produce a vitrified solid. Another process for volume reduction and immobilization of waste is taught by U.S. Pat. No. 4,395,367 wherein fission waste is treated by mixing a glass forming agent, a metal oxide and a reducing agent with the fission waste, and heating the mixture until melted.
However, none of the known processes are effective on thorium and/or uranium bearing waste residues due to the extremely high melting point of ThO2 (3200° C.) and UO2 (2500° C.). Under the process of this invention, it has now been discovered that the volume of these thorium and/or uranium bearing waste residues can be reduced by as much as 60 to 80 percent and that it is possible to immobilize these wastes into a solid, vitrified mass.
SUMMARY OF THE INVENTION
It is an object of this invention to provide a process for the concentration and immobilization of radioactive waste residues.
It is another object of this invention to provide a process for vitrifying the waste residues obtained from processing pitchblende or monazite.
It is another object of this invention to provide a process for reducing the volume of radioactive waste residues and immobilizing these residues to produce a dustless environmentally safe form.
It is another object of this invention to reduce the diffusion of radon into the environment, reduce alpha and beta radiation exposures, and maintain gamma radiation exposure within reasonable limits.
Under the process of the present invention, there has been provided a method of treating the radioactive waste residues which result from the processing of pitchblende or monazite or other thorium or uranium bearing minerals, which comprises forming a mixture of a dried radioactive thorium and/or uranium containing waste residue and a fluxing agent, melting the mixture to form molten glass, and pouring the molten glass into a suitable container.
DETAILED DESCRIPTION
The present invention is directed to a process of treating the solid thorium and/or uranium containing radioactive waste obtained from the processing of monazite, pitchblende, xenotine, apatite, bastnasite or other rare-earth bearing ores. The process of this invention comprises mixing the dried waste residue with about 0.1 to 50% by weight of a fluxing agent, optionally about 0.1 to 50% by weight SiO2, and heating the mixture to a molten glassy state, and pouring the molten glass into a suitable container for burial or storage.
The waste residues capable of being treated under this process are any solid radioactive waste residues which bear thorium or uranium, and their natural decay daughters. Appropriate fluxing agents for use in the invention include, but are not limited to, NaOH, Na2 CO3, NaBO2, Na2 B4 O7 or mixtures thereof. Silica sand may also be added to the mixture if necessary. The specific proportions of fluxing agent and silica sand to be added to the mixture can vary depending on the desired melt viscosity and are not per se critical to the invention provided that adequate pour viscosities are developed in the mixture. The preferred melt viscosities of this invention are in the range 1000 to 3000 centipoise at pour temperatures of 1093° to 1260° C.
The dried radioactive waste residues, together with the fluxing agent and optionally silica sand, may be added batchwise or in a continuous process to an appropriate glass furnace. The furnace is typically heated to a temperature in the range 1200° to 1800° C., and the glass residence times in the melter are between 2 and 24 hours. Furnace temperatures and glass residence times are generally interdependent. Therefore, if a temperature higher than 1800° C. is used, a correspondingly shorter residence time will be required to achieve the desired molten glass state.
The molten glass waste residues are then poured into steel or stainless steel, or other similar containers in which the melt is cooled to form a solid, vitrified mass, whereupon the containers can be sealed by welding or other suitable method.
The final percentage of thorium and uranium present in the reduced volume vitrified waste is about 0.1 to 50% by weight and 0.01 to 10% by weight respectively.
Without further elaboration, it is believed that one skilled in the art, using the preceding detailed description can utilize the present invention to its fullest extent.
The following example is provided to illustrate the invention in accordance with the principles of this invention, but is not to be construed as limiting the invention in any way except as indicated in the appended claims. All parts and percentages are by weight unless otherwise indicated.
EXAMPLE 1
Thorium bearing radioactive waste residues in the form of a thick slurry were obtained from a monazite cracking plant. The initial density of this residue was 1.85 g/cc. The waste residues were dried, ground to a fine powder, and mixed with 20% by weight Na2 B4 O7. The mixture was heated to 1540° C. for two hours to produce a molten glass that was readily pourable. The glass residue was cooled to room temperature and had a density of 4.0 g/cc. After accounting for the weight loss due to water evaporation, and weight gain from the addition of the Na2 B4 O7, this represents approximately a 70% volume reduction.

Claims (3)

What is claimed is:
1. A process for treating low level radioactive waste comprising:
(a) drying a waste residue obtained from the removal of rare-earths from a rare-earth bearing ore selected from the group consisting of monazite, pitchblende, xenotine, apatite and bastnasite to obtain a dried waste residue which contains 0.1 to 50% by weight thorium and/or 0.01 to 10% by weight uranium;
(b) mixing the dried residue with silica sand and a glass forming agent selected from the group consisting of NaOH, Na2 CO3, Na2 B4 O7 and NaBO2 and mixtures thereof to obtain a mixture which contains 0.1 to 50% by weight of said agent;
(c) heating the mixture to a temperature of 1200° to 1800° C. to obtain a molten mass; and
(d) cooling said molten mass to obtain a solid, vitrified mass having a volume 60 to 80 percent less than said waste residue.
2. The process of claim 1 wherein the sand is added in amounts ranging from 0.1 to 50 percent by weight of the total mixture.
3. A solid vitrified product prepared by the process of claim 2.
US07/392,327 1989-08-11 1989-08-11 Process for the immobilization and volume reduction of low level radioactive wastes from thorium and uranium processing Abandoned USH1013H (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
US07/392,327 USH1013H (en) 1989-08-11 1989-08-11 Process for the immobilization and volume reduction of low level radioactive wastes from thorium and uranium processing
AU60176/90A AU6017690A (en) 1989-08-11 1990-08-06 Process for the immobilization and volume reduction of low level radioactive wastes from thorium and uranium processing
BR909003923A BR9003923A (en) 1989-08-11 1990-08-09 PROCESS FOR IMMOBILIZATION AND REDUCING THE VOLUME OF LOW LEVEL RADIOACTIVITY WASTE CONTAINING TORIO AND URANIUM, COMPOSITION OF VITRIFIED AND REDUCED VOLUME RADIOACTIVE WASTE
FR9010270A FR2652193A1 (en) 1989-08-11 1990-08-10 Method for immobilisation and volume reduction of low-level radioactive waste in the processing of thorium and uranium

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
US07/392,327 USH1013H (en) 1989-08-11 1989-08-11 Process for the immobilization and volume reduction of low level radioactive wastes from thorium and uranium processing

Publications (1)

Publication Number Publication Date
USH1013H true USH1013H (en) 1992-01-07

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US07/392,327 Abandoned USH1013H (en) 1989-08-11 1989-08-11 Process for the immobilization and volume reduction of low level radioactive wastes from thorium and uranium processing

Country Status (4)

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US (1) USH1013H (en)
AU (1) AU6017690A (en)
BR (1) BR9003923A (en)
FR (1) FR2652193A1 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5350569A (en) * 1993-03-30 1994-09-27 The United States Of America As Represented By The United States Department Of Energy Storage of nuclear materials by encapsulation in fullerenes
US6454695B1 (en) * 1998-02-05 2002-09-24 Fumie Morishige Therapeutic instrument for treating or relieving psoriasis, atopic dermatitis, articular rheumatism and/or cancer or preventing the progress of these diseases and method of utilization thereof
US6635796B2 (en) 1990-03-16 2003-10-21 Sevenson Environmental Services, Inc. Reduction of leachability and solubility of radionuclides and radioactive substances in contaminated soils and materials

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE4427179A1 (en) * 1994-08-01 1996-02-08 Siemens Ag Process for recycling metal parts that are radioactively contaminated by uranium

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5343640A (en) * 1976-10-01 1978-04-19 Hitachi Denkaihaku Kenkyusho Electrolytic etching method for aluminum
DE2731327C3 (en) * 1977-07-12 1981-01-22 Kernforschungszentrum Karlsruhe Gmbh, 7500 Karlsruhe Process for filtering dust from radioactive waste gases and equipment for carrying out the process
JPS58115066A (en) * 1981-12-25 1983-07-08 動力炉・核燃料開発事業団 Artificial ore
JPS6038700A (en) * 1983-08-10 1985-02-28 東京電力株式会社 Method of melting and solidifying radioactive waste incinerated ash
JPS60236098A (en) * 1984-05-09 1985-11-22 日本碍子株式会社 Method of treating radioactive waste
JPS6186692A (en) * 1984-10-05 1986-05-02 株式会社日立製作所 Method of solidifying spent radioactive ion exchange resin
JPS61132899A (en) * 1984-12-03 1986-06-20 明星工業株式会社 Volume reducing method of radioactive heat-insulating waste

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
Bruce et al., Progress in Nuclear Energy, 1958, p. 443-455.

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6635796B2 (en) 1990-03-16 2003-10-21 Sevenson Environmental Services, Inc. Reduction of leachability and solubility of radionuclides and radioactive substances in contaminated soils and materials
US5350569A (en) * 1993-03-30 1994-09-27 The United States Of America As Represented By The United States Department Of Energy Storage of nuclear materials by encapsulation in fullerenes
US6454695B1 (en) * 1998-02-05 2002-09-24 Fumie Morishige Therapeutic instrument for treating or relieving psoriasis, atopic dermatitis, articular rheumatism and/or cancer or preventing the progress of these diseases and method of utilization thereof

Also Published As

Publication number Publication date
BR9003923A (en) 1991-09-03
AU6017690A (en) 1991-02-14
FR2652193A1 (en) 1991-03-22

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