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EP0092941A2 - Méthode de traitement des déchets de béton radioactifs ou autres - Google Patents

Méthode de traitement des déchets de béton radioactifs ou autres Download PDF

Info

Publication number
EP0092941A2
EP0092941A2 EP83302113A EP83302113A EP0092941A2 EP 0092941 A2 EP0092941 A2 EP 0092941A2 EP 83302113 A EP83302113 A EP 83302113A EP 83302113 A EP83302113 A EP 83302113A EP 0092941 A2 EP0092941 A2 EP 0092941A2
Authority
EP
European Patent Office
Prior art keywords
dust
concrete
dust particles
silicate solution
liquid medium
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Withdrawn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
EP83302113A
Other languages
German (de)
English (en)
Other versions
EP0092941A3 (fr
Inventor
Dennis Granville Langridge
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.)
Taylor Woodrow Construction Ltd
Original Assignee
Taylor Woodrow Construction 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 Taylor Woodrow Construction Ltd filed Critical Taylor Woodrow Construction Ltd
Publication of EP0092941A2 publication Critical patent/EP0092941A2/fr
Publication of EP0092941A3 publication Critical patent/EP0092941A3/fr
Withdrawn legal-status Critical Current

Links

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
    • G21F9/02Treating gases
    • 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

Definitions

  • This invention relates to a method for treatment of concrete wastes, especially, but not exclusively, radioactive concrete wastes.
  • Nuclear reactors employed in the production of electricity generally comprise, surrounding the nuclear reactor, a steel reactor vessel for containing the nuclear reactor and then, outside this, a thick concrete structure to serve as a biological shield.
  • a steel reactor vessel for containing the nuclear reactor and then, outside this, a thick concrete structure to serve as a biological shield.
  • an integrated circuit has been used and the reactor has been housed in a prestressed concrete structure in which the various cavities are lined with steel.
  • the steel vessels and considerable quantities of the concrete used for shielding or other purposes become significantly radioactive. This poses problems during the dismantling of nuclear installations, not only because of the mass of active material to be disposed of, but also because of its form.
  • a method for the fixing of concrete dust produced on demolition of a concrete installation which comprises collecting such dust which is airborne and taking it up in a liquid medium which has the ability to wet and bind the dust particles together and set to a cohesive mass under ambient temperature conditions and conditions such that the setting is solely the result of reaction involving the chemical contents of the dust particles and said solution.
  • a variety of materials may in principle, be used to carry out the method of this invention. However, many have inherent characteristics which detract from their ease and convenience of use. Among these drawbacks are the presence of inflammable or noxious components, the necessity of including in them additives in order to bring about a reaction by which the mixture of dust and liquid will set to a firm and readily handleable solid, high cost or limited availability, or lack of resistance to atomic radiation.
  • the materials which have been found most suitable for use in carrying out this invention are aqueous solutions of the alkali metal silicates and more particularly those aqueous solutions which are based on sodium silicate.
  • Sodium silicate is manufactured in a range of silica/alkali ratios and the properties of the solution are largely defined by this ratio. It might be thought that a solution of high silica/alkali ratio will be more effective in carrying out the method of the invention than a solution of lower silica/alkali ratio and will enable the volume of material used to be kept down. In fact this is not the case. It is preferable to use relatively low silica/alkali ratios whereby a stronger product is obtained. Thus there is no advantage to be obtained in using silica/alkali ratios in the range of 3.4-4:1 and higher and in fact better results are usually obtained at much lower ratios e.g. 2-2.5:1.
  • the solids content of the silicate solution employed is concerned it is preferred to use a solution strength of from 5-50% by weight solids.
  • a solution strength of from 5-50% by weight solids.
  • silica/alkali ratio and solids content are interrelated, and for silica/alkali ratios in the range 2-2.5:1 it is preferred to use a sodium silicate solution having a solids content of 25-40% by weight, the higher solids contents being more suitable for the coarser concrete dusts.
  • the setting of sodium silicate solution to form substantially solid material is a well known phenomenon in itself.
  • a variety of processes are known for achieving this setting, for example loss of relatively small quantities of water and reaction with acid in solution or absorption of carbon dioxide from the atmosphere.
  • This phenomenon has been employed for many years in the binding of sand in the production of foundry moulds, where the use of carbon dioxide and heat is required.
  • the speed of reaction and strength of the gel formed depends inter alia upon the silica/alkali ratio and upon the solids content of the sodium silicate solution. It is a general characteristic of these known procedures that either heat or a chemical treatment is required to promote the setting reaction.
  • the method of the present invention can be carried out under ambient conditions without the need for either application of heat or addition of any outside chemical agents. It is thought that the presence of calcium ions from lime in the concrete is sufficient to bring about the setting reaction. In fact the age of the concrete may affect the speed of the setting reaction. Thus old concrete in which the lime has largely been converted to carbonate may react with the silicate solution more slowly.
  • the containment vessel in which the concrete rubble and dust are present after demolition can be held at below atmospheric pressure to prevent escape of the dust into the atmosphere and the finer dust can be extracted by suction, separated from the air stream by one of a variety of available methods using cyclones, filters or electrostatic precipitators and thereafter mixed with the silicate solution to form a slurry which is allowed to set, or otherwise mixed with the silicate solution to form pellets or lumps of a convenient size.
  • the dust which is left adhering to the lumps of rubble may be fixed thereto by spraying with the same silicate solution after dilution thereof.
  • silicate solution it is possible in carrying out this invention to employ the silicate in powdered form, to mix it with the concrete dust, and then to add water to enable the setting reaction to take place.

Landscapes

  • Engineering & Computer Science (AREA)
  • Physics & Mathematics (AREA)
  • General Engineering & Computer Science (AREA)
  • High Energy & Nuclear Physics (AREA)
  • Environmental & Geological Engineering (AREA)
  • Processing Of Solid Wastes (AREA)
EP83302113A 1982-04-22 1983-04-14 Méthode de traitement des déchets de béton radioactifs ou autres Withdrawn EP0092941A3 (fr)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
GB8211667 1982-04-22
GB8211667 1982-04-22

Publications (2)

Publication Number Publication Date
EP0092941A2 true EP0092941A2 (fr) 1983-11-02
EP0092941A3 EP0092941A3 (fr) 1986-02-12

Family

ID=10529862

Family Applications (1)

Application Number Title Priority Date Filing Date
EP83302113A Withdrawn EP0092941A3 (fr) 1982-04-22 1983-04-14 Méthode de traitement des déchets de béton radioactifs ou autres

Country Status (3)

Country Link
EP (1) EP0092941A3 (fr)
JP (1) JPS58192000A (fr)
AU (1) AU1384983A (fr)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE3901783A1 (de) * 1989-01-21 1990-08-02 Kernforschungsz Karlsruhe Verfahren zum endlagern von schwachkontaminiertem bauschutt aus dem abriss kerntechnischer anlagen
DE4023118A1 (de) * 1990-07-20 1992-01-30 Kernforschungsz Karlsruhe Verfahren zum endlagern von schwach kontaminiertem bauschutt aus dem abriss kerntechnischer anlagen und vorrichtung zur durchfuehrung des verfahrens
DE4023117A1 (de) * 1990-07-20 1992-01-30 Kernforschungsz Karlsruhe Verfahren zum endlagern von schwach kontaminiertem bauschutt aus dem abriss kerntechnischer anlagen und vorrichtung zur durchfuehrung des verfahrens
ES2156513A1 (es) * 1998-12-03 2001-06-16 Nac De Residuos Radioactivos S Procedimiento para descontaminacion ionica del hormigon en instalaciones nucleares.

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5043424B2 (ja) * 2006-12-25 2012-10-10 株式会社M−Tec セメント硬化体の処理方法及び既処理物

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA965966A (en) * 1970-01-08 1975-04-15 Jesse R. Conner Land improvement with waste materials
DE2228938A1 (de) * 1972-06-14 1974-01-03 Nukem Gmbh Verfahren und einrichtung zur verfestigung von festen und fluessigen radioaktiven abfallstoffen, insbesondere von nasschlaemmen
BE812192A (en) * 1974-03-12 1974-07-01 Radioactive or hazardous liquid wastes treatment - to produce solid masses suitable for storage using a silicate carrier soln.
US3988258A (en) * 1975-01-17 1976-10-26 United Nuclear Industries, Inc. Radwaste disposal by incorporation in matrix
DE2559724C3 (de) * 1975-07-11 1980-03-06 Kernforschungsanlage Juelich Gmbh, 5170 Juelich Verfahren zum Verfestigen einer radioaktive oder toxische Abfallstoffe enthaltenden wäßrigen Lösung

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE3901783A1 (de) * 1989-01-21 1990-08-02 Kernforschungsz Karlsruhe Verfahren zum endlagern von schwachkontaminiertem bauschutt aus dem abriss kerntechnischer anlagen
DE4023118A1 (de) * 1990-07-20 1992-01-30 Kernforschungsz Karlsruhe Verfahren zum endlagern von schwach kontaminiertem bauschutt aus dem abriss kerntechnischer anlagen und vorrichtung zur durchfuehrung des verfahrens
DE4023117A1 (de) * 1990-07-20 1992-01-30 Kernforschungsz Karlsruhe Verfahren zum endlagern von schwach kontaminiertem bauschutt aus dem abriss kerntechnischer anlagen und vorrichtung zur durchfuehrung des verfahrens
ES2156513A1 (es) * 1998-12-03 2001-06-16 Nac De Residuos Radioactivos S Procedimiento para descontaminacion ionica del hormigon en instalaciones nucleares.

Also Published As

Publication number Publication date
AU1384983A (en) 1983-10-27
JPS58192000A (ja) 1983-11-09
EP0092941A3 (fr) 1986-02-12

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Ipc: G21F 9/34

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Effective date: 19851101

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Inventor name: LANGRIDGE, DENNIS GRANVILLE