WO2000032524A1 - Procede et dispositif d'incineration et de vitrification de dechets, notamment radioactifs - Google Patents

Procede et dispositif d'incineration et de vitrification de dechets, notamment radioactifs Download PDF

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Publication number
WO2000032524A1
WO2000032524A1 PCT/FR1999/002977 FR9902977W WO0032524A1 WO 2000032524 A1 WO2000032524 A1 WO 2000032524A1 FR 9902977 W FR9902977 W FR 9902977W WO 0032524 A1 WO0032524 A1 WO 0032524A1
Authority
WO
WIPO (PCT)
Prior art keywords
reactor
waste
oxygen
glass bath
bath
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.)
Ceased
Application number
PCT/FR1999/002977
Other languages
English (en)
French (fr)
Inventor
Pierre Brunelot
Jacques Lacombe
Serge Merlin
Patrice Roux
Valérie THIEBAUT
Kwan-Sik Choi
Myung-Jae Song
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.)
Societe Generale pour les Techniques Nouvelles SA SGN
Korea Electric Power Corp
Original Assignee
Societe Generale pour les Techniques Nouvelles SA SGN
Korea Electric Power Corp
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
Priority claimed from KR1019980052360A external-priority patent/KR20000037710A/ko
Priority claimed from KR1019980052361A external-priority patent/KR100305724B1/ko
Priority to EP99973006A priority Critical patent/EP1137603B1/fr
Application filed by Societe Generale pour les Techniques Nouvelles SA SGN, Korea Electric Power Corp filed Critical Societe Generale pour les Techniques Nouvelles SA SGN
Priority to CA002352107A priority patent/CA2352107C/fr
Priority to KR10-2001-7006819A priority patent/KR100501640B1/ko
Priority to US09/856,684 priority patent/US6815572B1/en
Priority to AT99973006T priority patent/ATE238970T1/de
Priority to DE69907507T priority patent/DE69907507T2/de
Priority to JP2000585171A priority patent/JP4048025B2/ja
Publication of WO2000032524A1 publication Critical patent/WO2000032524A1/fr
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03BMANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
    • C03B5/00Melting in furnaces; Furnaces so far as specially adapted for glass manufacture
    • C03B5/005Melting in furnaces; Furnaces so far as specially adapted for glass manufacture of glass-forming waste materials
    • 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
    • G21F9/32Processing by incineration
    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03BMANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
    • C03B3/00Charging the melting furnaces
    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03BMANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
    • C03B5/00Melting in furnaces; Furnaces so far as specially adapted for glass manufacture
    • C03B5/02Melting in furnaces; Furnaces so far as specially adapted for glass manufacture in electric furnaces, e.g. by dielectric heating
    • C03B5/021Melting in furnaces; Furnaces so far as specially adapted for glass manufacture in electric furnaces, e.g. by dielectric heating by induction heating
    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03BMANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
    • C03B5/00Melting in furnaces; Furnaces so far as specially adapted for glass manufacture
    • C03B5/02Melting in furnaces; Furnaces so far as specially adapted for glass manufacture in electric furnaces, e.g. by dielectric heating
    • C03B5/025Melting in furnaces; Furnaces so far as specially adapted for glass manufacture in electric furnaces, e.g. by dielectric heating by arc discharge or plasma heating
    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03BMANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
    • C03B5/00Melting in furnaces; Furnaces so far as specially adapted for glass manufacture
    • C03B5/02Melting in furnaces; Furnaces so far as specially adapted for glass manufacture in electric furnaces, e.g. by dielectric heating
    • C03B5/027Melting in furnaces; Furnaces so far as specially adapted for glass manufacture in electric furnaces, e.g. by dielectric heating by passing an electric current between electrodes immersed in the glass bath, i.e. by direct resistance heating
    • C03B5/0275Shaft furnaces
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/50Glass production, e.g. reusing waste heat during processing or shaping
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10TECHNICAL SUBJECTS COVERED BY FORMER USPC
    • Y10STECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10S423/00Chemistry of inorganic compounds
    • Y10S423/09Reaction techniques
    • Y10S423/12Molten media
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10TECHNICAL SUBJECTS COVERED BY FORMER USPC
    • Y10STECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10S588/00Hazardous or toxic waste destruction or containment
    • Y10S588/90Apparatus

Definitions

  • the subject of the present invention is a process and a device for incineration and vitrification of waste, in particular radioactive waste.
  • Said invention is part of the treatment of hazardous combustible waste, the ashes of which should be immobilized in a stable manner. For a long time, we neutralized this type of waste in two stages, each of said stages being implemented in an independent device:
  • a second step of immobilizing the ash recovered at the end of said first step said second step being implemented in a suitable device which contains a glass bath kept in the molten state.
  • Improvement which is the main object of the present invention, can be analyzed in terms of both process and device and is involved in the quality of the glass bath. Said improvement which can be qualified, for the sake of clarity of the present description, as a main improvement, is advantageously implemented with other improvements which can be qualified, in the same spirit, of secondary improvements. Said improvements, main and secondary, are described below in general terms and then, in more detail, with reference to the appended figures.
  • the present invention therefore relates to a process for the treatment of organic waste (therefore combustible), divided solid (to facilitate its introduction and their combustion) and / or liquid, implemented in a single reactor containing a glass bath melted topped with a gas phase; said treatment process comprising: incineration, in the presence of oxygen, of said waste on the surface of said molten glass bath (said waste falls on said surface, decomposes therein and the gaseous products which result from this decomposition are burned in said oxygenated gas phase), and the vitrification of said incinerated waste in said molten glass bath.
  • the process of the invention is a process of direct vitrification.
  • said method further comprises injecting oxygen into said molten glass bath, in an amount sufficient to minimize or even avoid the formation of metal within said glass bath; advantageously, in an amount sufficient to minimize or even avoid the formation of metal within said glass bath and to ensure moderate stirring of said glass bath.
  • Said oxygen, introduced, in an original way, in the molten glass bath, is introduced into the treatment reactor, in addition to the latter, conventionally delivered as oxidant in the gas phase surmounting said bath, intended to ensure the waste incineration.
  • the oxygen injected into the glass bath to minimize or even avoid the formation of metal is advantageously in an amount sufficient to also ensuring a certain agitation of said glass bath.
  • Those skilled in the art are able to optimize the quantity of oxygen necessary for these purposes. In any event, this must be sufficient to obtain the expected effect as regards the value of the redox potential, or even expected effects as to the value of said potential and as to the effect d agitation sought but must not be excessive insofar as the glass bath, certainly stirred, stirred, must remain a glass bath and not turn into a foam ...
  • the oxygen delivered as an oxidizer in the gas phase, it intervenes advantageously, for an optimization of the incineration in question, in an amount greater than the stoichiometric amount, theoretically required. It intervenes advantageously in an amount corresponding to 1.25 to 1.5 times said stoichiometric amount.
  • Said amount is. in any event, controlled and does not affect the vacuum, maintained in the reactor, conventionally, for obvious safety reasons.
  • Said depression is maintained by a suction of combustion gases, suction implemented under conditions such that the entrainment of waste and especially of ash is minimized.
  • the reactor contains at start-up an initial glass bath of small volume (a bottom) and it is then supplied, on the one hand with waste, on the other hand with components of a glass bath.
  • Said waste and said constituent elements are moreover advantageously introduced as a mixture ... the waste can in fact be assimilated to precursors of constituent elements of said glass bath.
  • the reactor is thus continuously supplied with waste and with elements constituting the glass bath, or even additives to said elements. When a certain level is reached, the two types of feeding are stopped and the glass bath thus formed can be drained.
  • the oxygen injected into the glass bath is introduced into the reactor below the surface of said glass bath.
  • the means for injecting said oxygen do not pass through the gas phase of said reactor, do they have to undergo only one type of corrosion: that inherent to said glass bath.
  • any device intended to penetrate said glass bath to deliver any element there (we have just invoked the injection of oxygen) or to measure any parameter (such as temperature, redox potential ).
  • any device intended to penetrate said glass bath is advantageously introduced into the reactor below the surface of said glass bath, so as to avoid any contact with the gas phase.
  • the process of the invention which comprises injecting oxygen into the glass bath, is advantageously carried out with cooling of the walls of the reactor and / or. preferably and, means introduced into said reactor, both at said gas phase and in the glass bath, means introduced in particular for supplying said reactor with the waste to be incinerated and vitrified, feeding it with oxygen , both in terms of its gaseous phase (said oxygen acting as oxidant) as in the glass bath (said oxygen then acting as an oxidant to adjust the redox potential of said glass bath and advantageously as means of agitation).
  • means for measuring the temperature of the gas phase means for measuring the temperature of the glass bath, means for measuring the redox potential of said glass bath, means for measurement of the level of said glass bath ...
  • Such cooling is intended above all to protect said walls and said means from corrosion. It is also appropriate to preserve the sealing devices installed at the crossings of said walls.
  • a second cooling of this same device generally independent of the first, on the arrival side of said waste (internal face side).
  • the first of said coolings is primarily intended to protect said device from corrosion, developed by the gas phase in contact with it; the second of said cooling is above all intended to minimize the calories transferred to the incoming waste, this in order to minimize the vaporization of the liquid waste, to avoid sticking of solid waste, bonding liable to cause clogging of said supply device .
  • heat transfer fluids generally heat transfer liquids.
  • the aim is to avoid any condensation of said gas phase on said walls and on the external surfaces of said means. This condensation phenomenon is obviously harmful, with reference to corrosion problems. It is moreover likely to generate electric arcs, and therefore to pose serious problems, when implementing a heating of the glass bath by induction.
  • the double cooling, mentioned above, advantageously implemented within the device for supplying waste to the reactor is, according to a particularly preferred variant, implemented with such a fluid "hot” (which has a temperature higher than the dew point of the gas phase passed through), at least as regards the cooling of said device, on the gas phase side (the first of the coolings, mentioned above).
  • a fluid "hot” which has a temperature higher than the dew point of the gas phase passed through
  • the intervention of such a "hot” coolant can obviously only be envisaged with waste capable of withstanding the temperature of such a "hot” fluid.
  • the second of said cooling is carried out with a" cold "fluid, such as water at ambient temperature.
  • various techniques can be used for heating and keeping the molten glass bath at the appropriate temperature.
  • Said glass bath can thus be heated, by induction, with a flame, with a plasma torch or by means of plunging electrodes. It is not excluded to use several of said techniques, in combination. Induction heating is preferred; induction heating, used in a cold crucible is very particularly preferred.
  • Said method of the invention is generally implemented with a continuous supply of waste; said waste being introduced above the surface of the glass bath, possibly in admixture with elements constituting said glass bath. After the incineration of a charge and the digestion of the ash generated in the glass bath, said charged glass bath is drained. There is therefore generally a continuous supply (a constitution of the load continuously) and a batch discharge.
  • the supply of waste and oxygen to the reactor is obviously advantageously optimized to ensure maximum combustion of said waste and minimum entrainment of said waste, burned or not, by the combustion gases.
  • This optimization is based on control, combined, of numerous parameters, some of which have already been mentioned, and in particular through control:
  • At least one oxygen supply circuit is used in the structure of the device for supplying said waste.
  • the second object of the present invention namely a device for treatment, by incineration and vitrification, of organic waste, divided solids and / or liquids; device suitable for implementing the method described above.
  • Said device comprises, in a conventional manner, a reactor, on the one hand associated with heating means, capable of maintaining in the bottom of said reactor a bath of molten glass and on the other hand equipped with the following means:
  • a device for supplying the waste to be incinerated and vitrified said device opening out above the surface of said molten glass bath and its depth of introduction into said reactor being advantageously adjustable; - oxygen supply means, delivering said oxygen above the surface of said molten glass bath (for carrying out incineration);
  • At least one outlet for combustion gases provided in the upper part of said reactor, well above the surface of said bath of molten glass (the aim is to minimize the entrainment of ash).
  • Said device typically, is further equipped with means for injecting oxygen into said molten glass bath.
  • Said means are advantageously introduced into the lower part of the reactor, below the surface of the glass bath so that they do not contact the gas phase, they only undergo one type of corrosion (that developed by the bath of glass).
  • Said means are also advantageously arranged so that when their oxygen supply is stopped, a glass stopper does not form at their open end.
  • said means for injecting oxygen into said glass bath are advantageously arranged vertically, through the bottom (of the bottom hearth) of the reactor, with a mouth, arranged at 90 ° to their vertical axis.
  • the essential elements of the device of the invention necessary for implementing the targeted incineration and vitrification process, are those mentioned above. It can add to said elements other elements, such as means for measuring the temperature of the gas phase, means for measuring the temperature of the molten glass bath, means for measuring the level of said glass bath, means for measuring the redox potential of said molten glass bath ....
  • means for measuring the temperature of the gas phase means for measuring the temperature of the molten glass bath
  • means for measuring the level of said glass bath means for measuring the redox potential of said molten glass bath ....
  • all of said means introduced into the reactor include in their structure, at least one circuit for circulating a heat transfer fluid.
  • Said device for supplying said reactor with said waste includes, advantageously in its mass, at least two generally independent circuits of this type, at least one for ensuring the cooling of its mass and of its external surface (in order to minimize the corrosion problems) and at least one other to ensure the cooling of its internal surface (in order to transfer the minimum amount of calories to the incoming waste).
  • Said supply device generally has a tubular structure, delimited by an external surface and an internal surface.
  • the following can also be added. It also advantageously includes in its structure means for conveying and delivering oxygen at its through end (above the glass bath).
  • the delivery of said oxygen can in particular be ensured from a torus, arranged around the through end of said device, said torus being pierced with suitable orifices judiciously distributed. Waste / oxygen (oxidant) contact can thus be optimized.
  • the inlets and outlets of heat transfer fluids are connected to distribution units. and evacuation adequate.
  • the distribution of said fluids and said oxygen, in their respective circulation circuit (s), inside said supply device, is advantageously carried out by means of a set of distribution chambers and channels, judiciously arranged.
  • the reactor is also cooled. Its walls are advantageously of the double envelope type, to allow the circulation of a heat transfer fluid.
  • the heating means associated with said reactor can be of different types and in particular be suitable for the implementation of heating by induction, with a flame, with a plasma torch or by means of plunging electrodes.
  • the reactor used is a cold crucible and said heating means are induction heating means.
  • Figure 1 is a schematic view of the operation of a device of the invention.
  • Figure 2 is a more detailed sectional view of a device of the same type.
  • Figure 3 is a detailed sectional view of the oxygen injection means in the glass bath.
  • Figure 4 is a detailed sectional view of the waste supply device.
  • the device of the invention which is suitable for treating - by incineration and vitrification, by direct vitrification - waste D, comprises a reactor 1 associated with heating means 2. Said heating means 2 shown in Figures 1 and 2 are suitable for induction heating. Within said reactor 1, there is the molten glass bath V, surmounted by the gas phase G (FIG. 1).
  • the waste D is brought into the reactor 1 via the device 5 for supplying the said waste D. It is decomposed on the surface S of the molten glass bath V. The gases resulting from this decomposition burn on contact with oxygen, mainly delivered by means 6.
  • a single means 6 for the delivery in the gas phase of said oxygen mainly delivered by means 6.
  • the ash generated falls into the glass bath V.
  • an outlet 7 has been provided for the combustion gases.
  • Said means 4 are capable, alternatively, of closing and opening a drain orifice formed in the bottom of said reactor 1.
  • said bottom of said reactor 1 is traversed by means 8 for injecting oxygen into the glass bath V.
  • Said injection means 8 are arranged vertically and have a mouth 82, 90 ° from their vertical axis .
  • the walls 3 and 3 ′ of said reactor 1 are of the double-jacket type. Since the reactor 1 is designed in two parts, reference 3 is its wall in the lower part and 3 ′ its wall in the upper part. Within these two walls 3 and 3 ', the circulation of a heat transfer fluid is provided. For wall 3, said fluid arrives at 10 and exits at 11, for wall 3 ', it arrives at 12 and exits at 13.
  • FIG. 2 For a more detailed description of the device 5 for supplying waste D, reference is made to the comments developed below with reference to FIG. 4.
  • two means 6 are shown, provided for supplying oxygen (by oxidizing) to the gas phase. They are actually canes.
  • a circulation circuit 61 of a heat transfer fluid Within the structure of said rods 6, there is provided a circulation circuit 61 of a heat transfer fluid. Rods thus cooled are more resistant to corrosion. It will be recalled here that they are advantageously cooled by circulation of a "hot" heat transfer fluid (maintained at a temperature above the dew point of the gas phase passed through), to avoid any condensation on their external surface.
  • FIG 3 there is therefore shown a means 8 for injecting oxygen into the glass bath.
  • Said means 8 comprises a supply circuit 81 for said oxygen.
  • the circulation of said oxygen in said circuit 81 has been shown diagrammatically by the white arrows.
  • the oxygen is delivered at 82, mouth formed at 90 ° to the axis of said means 8.
  • Said means 8 includes in its structure a circulation circuit 83 + 83 ′ of a heat transfer fluid. Its part which enters the glass bath can thus be cooled. Said heat transfer fluid arrives in 83 and leaves, loaded with calories in 83 '. Its circulation is schematized by the black arrows.
  • FIG. 4 finally shows a particularly advantageous variant embodiment of the device 5 for supplying reactor 1 with the waste D.
  • Said device 5 has a tubular structure, delimited by an external surface 50 and an internal surface 50 ′.
  • the circulation of said heat transfer fluid is shown diagrammatically by the black arrows;
  • At least one circulation circuit 52 for a heat transfer fluid intended to cool said internal surface 50 ' At least one circulation circuit 52 for a heat transfer fluid intended to cool said internal surface 50 '.
  • the circulation of said heat transfer fluid is shown diagrammatically by the white arrows; as well as'
  • Said oxygen is thus delivered, all around said end 55, via a torus 54.
  • Said torus 54 has orifices of suitable dimensions, judiciously distributed to deliver said oxygen in an optimized manner.
  • the D / oxygen waste contact is thus further optimized.
  • Said oxygen, delivered via the device 5 for supplying waste D is in addition to the oxygen delivered by the means 6 (see FIGS. 1 and 2).

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Physics & Mathematics (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Plasma & Fusion (AREA)
  • Electrochemistry (AREA)
  • High Energy & Nuclear Physics (AREA)
  • General Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Processing Of Solid Wastes (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Glass Melting And Manufacturing (AREA)
PCT/FR1999/002977 1998-12-01 1999-12-01 Procede et dispositif d'incineration et de vitrification de dechets, notamment radioactifs Ceased WO2000032524A1 (fr)

Priority Applications (7)

Application Number Priority Date Filing Date Title
JP2000585171A JP4048025B2 (ja) 1998-12-01 1999-12-01 廃棄物、特に放射性廃棄物を焼却し且つガラス化する方法と装置
DE69907507T DE69907507T2 (de) 1998-12-01 1999-12-01 Verfahren und vorrichtung zum verbrennen und verglasen von abfaellen, insbesondere radioaktiven abfaellen
EP99973006A EP1137603B1 (fr) 1998-12-01 1999-12-01 Procede et dispositif d'incineration et de vitrification de dechets, notamment radioactifs
CA002352107A CA2352107C (fr) 1998-12-01 1999-12-01 Procede et dispositif d'incineration et de vitrification de dechets, notamment radioactifs
KR10-2001-7006819A KR100501640B1 (ko) 1998-12-01 1999-12-01 폐기물, 특히 방사성 폐기물의 소각과 유리화 방법 및 장치
US09/856,684 US6815572B1 (en) 1998-12-01 1999-12-01 Method and device for incineration and vitrification of waste, in particular radioactive waste
AT99973006T ATE238970T1 (de) 1998-12-01 1999-12-01 Verfahren und vorrichtung zum verbrennen und verglasen von abfaellen, insbesondere radioaktiven abfaellen

Applications Claiming Priority (4)

Application Number Priority Date Filing Date Title
KR1019980052360A KR20000037710A (ko) 1998-12-01 1998-12-01 가연성 중·저준위 방사성 폐기물 직접투입 유리화 시스템
KR98/052360 1998-12-01
KR1019980052361A KR100305724B1 (ko) 1998-12-01 1998-12-01 가연성중·저준위방사성폐기물공급장치
KR98/052361 1998-12-01

Publications (1)

Publication Number Publication Date
WO2000032524A1 true WO2000032524A1 (fr) 2000-06-08

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ID=26634393

Family Applications (2)

Application Number Title Priority Date Filing Date
PCT/FR1999/002977 Ceased WO2000032524A1 (fr) 1998-12-01 1999-12-01 Procede et dispositif d'incineration et de vitrification de dechets, notamment radioactifs
PCT/FR1999/002978 Ceased WO2000032525A1 (fr) 1998-12-01 1999-12-01 Procede et dispositif d'incineration et de vitrification de dechets, notamment radioactifs

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Application Number Title Priority Date Filing Date
PCT/FR1999/002978 Ceased WO2000032525A1 (fr) 1998-12-01 1999-12-01 Procede et dispositif d'incineration et de vitrification de dechets, notamment radioactifs

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Country Link
US (2) US6576807B1 (https=)
EP (2) EP1144320B1 (https=)
JP (2) JP4048025B2 (https=)
KR (2) KR100501640B1 (https=)
AT (2) ATE238970T1 (https=)
CA (2) CA2352107C (https=)
DE (2) DE69907507T2 (https=)
ES (2) ES2197716T3 (https=)
WO (2) WO2000032524A1 (https=)

Families Citing this family (38)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
ATE238970T1 (de) * 1998-12-01 2003-05-15 Sgn Soc Gen Tech Nouvelle Verfahren und vorrichtung zum verbrennen und verglasen von abfaellen, insbesondere radioaktiven abfaellen
US6855123B2 (en) 2002-08-02 2005-02-15 Flow Cardia, Inc. Therapeutic ultrasound system
DE10202024B4 (de) * 2001-10-02 2010-04-08 Schott Ag Vorrichtung und Verfahren zum kontaminationsarmen Schmelzen einer Substanz
CN1278964C (zh) 2001-10-02 2006-10-11 肖特股份公司 用于使物质无沾染地熔化的装置和方法
US9955994B2 (en) 2002-08-02 2018-05-01 Flowcardia, Inc. Ultrasound catheter having protective feature against breakage
US7335180B2 (en) 2003-11-24 2008-02-26 Flowcardia, Inc. Steerable ultrasound catheter
US6942677B2 (en) 2003-02-26 2005-09-13 Flowcardia, Inc. Ultrasound catheter apparatus
KR100524825B1 (ko) * 2002-08-27 2005-10-28 한국수력원자력 주식회사 중·저준위 방사성폐기물 유리화 장치 및 공정
US7758510B2 (en) 2003-09-19 2010-07-20 Flowcardia, Inc. Connector for securing ultrasound catheter to transducer
GB0324831D0 (en) * 2003-10-24 2003-11-26 British Nuclear Fuels Plc Induction heating
US7132584B2 (en) * 2004-02-11 2006-11-07 Labeltek Inc. Method of using high temperature plasma to disintegrate waste containing titanyl phthalocyanine
US6971323B2 (en) 2004-03-19 2005-12-06 Peat International, Inc. Method and apparatus for treating waste
FR2870758B1 (fr) * 2004-05-26 2006-08-04 Commissariat Energie Atomique Procede permettant la combustion et l'oxydation complete de la fraction minerale d'un dechet traite dans un appareil de combustion-vitrification directe
US7540852B2 (en) 2004-08-26 2009-06-02 Flowcardia, Inc. Ultrasound catheter devices and methods
KR100735828B1 (ko) * 2004-11-03 2007-07-06 라춘기 열폭발 연소법에 의한 가연성 및 비가연성 방사성 폐기물의 유리화 방법
US8221343B2 (en) 2005-01-20 2012-07-17 Flowcardia, Inc. Vibrational catheter devices and methods for making same
US7832344B2 (en) * 2006-02-28 2010-11-16 Peat International, Inc. Method and apparatus of treating waste
US8246643B2 (en) 2006-11-07 2012-08-21 Flowcardia, Inc. Ultrasound catheter having improved distal end
WO2008100471A1 (en) * 2007-02-12 2008-08-21 Carestream Health, Inc. Renormalization of dual-energy images
US8199790B2 (en) * 2007-11-02 2012-06-12 Plasma Waste Recycling, Inc. Reactor vessel for plasma gasification
CN101983087B (zh) * 2008-02-08 2013-04-17 Peat国际公司 处理废物的方法和设备
JP4977916B2 (ja) * 2008-02-12 2012-07-18 独立行政法人日本原子力研究開発機構 放射性廃棄物処理装置
US8304358B2 (en) * 2008-11-21 2012-11-06 Ppg Industries Ohio, Inc. Method of reducing redox ratio of molten glass and the glass made thereby
US8671855B2 (en) 2009-07-06 2014-03-18 Peat International, Inc. Apparatus for treating waste
KR101100614B1 (ko) 2010-09-20 2011-12-29 한국수력원자력 주식회사 농축폐액 건조물의 펠렛화 장치 및 방법과 이를 이용한 유리조성개발 방법
KR101243198B1 (ko) * 2011-09-19 2013-03-13 한국수력원자력 주식회사 기체공급장치를 갖는 용융로
KR101247276B1 (ko) * 2011-09-19 2013-03-25 한국수력원자력 주식회사 용융유리 배출장치
KR101248940B1 (ko) 2011-09-19 2013-04-01 한국수력원자력 주식회사 용융로의 산소공급 장치
WO2013109269A1 (en) 2012-01-18 2013-07-25 Bard Peripheral Vascular, Inc. Vascular re-entry device
WO2014022716A2 (en) 2012-08-02 2014-02-06 Flowcardia, Inc. Ultrasound catheter system
US9932258B1 (en) 2014-04-17 2018-04-03 Owens-Brockway Glass Container Inc. Apparatus and process for making glass and glass gobs
US20180140321A1 (en) 2016-11-23 2018-05-24 C. R. Bard, Inc. Catheter With Retractable Sheath And Methods Thereof
US11596726B2 (en) 2016-12-17 2023-03-07 C.R. Bard, Inc. Ultrasound devices for removing clots from catheters and related methods
US10758256B2 (en) 2016-12-22 2020-09-01 C. R. Bard, Inc. Ultrasonic endovascular catheter
US10582983B2 (en) 2017-02-06 2020-03-10 C. R. Bard, Inc. Ultrasonic endovascular catheter with a controllable sheath
US10807896B2 (en) 2018-03-15 2020-10-20 Owens-Brockway Glass Container Inc. Process and apparatus for glass manufacture
FR3080707B1 (fr) 2018-04-25 2020-05-01 Seche Eco Services Procede de traitement de dechets bitumines radioactifs
CN113418398A (zh) * 2021-06-21 2021-09-21 中国原子能科学研究院 卸料阀及熔融系统

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3607171A (en) * 1968-07-26 1971-09-21 Vvb Tech Glas Method for heating melting or softening glass in dispersed form
WO1995004004A1 (fr) * 1993-07-28 1995-02-09 Europlasma Procede d'inertage par torche a plasma de produits contenant des metaux, en particulier des metaux lourds et installation pour sa mise en ×uvre
EP0647598A1 (fr) * 1993-10-08 1995-04-12 Commissariat A L'energie Atomique Procédé d'incinération et de vitrification de déchets dans un creuset
DE4446576C1 (de) * 1994-12-25 1996-04-25 Sorg Gmbh & Co Kg Wannen-Schmelzofen zum Inertisieren von Schadstoffen durch Verglasen
US5643350A (en) * 1994-11-08 1997-07-01 Vectra Technologies, Inc. Waste vitrification melter

Family Cites Families (24)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3592151A (en) * 1970-03-09 1971-07-13 Morgan Construction Co Method and apparatus for refuse incineration
US3812620A (en) * 1973-03-22 1974-05-28 Gen Electric Apparatus and process for segregating and decomposing heterogeneous waste materials
US4449483A (en) * 1983-01-07 1984-05-22 Electrodyne Research Corporation Unfired drying and sorting apparatus for preparation of solid fuel as a feedstock for a combustor
DE3415198C1 (de) * 1984-04-21 1985-09-26 Deutsche Gesellschaft für Wiederaufarbeitung von Kernbrennstoffen mbH, 3000 Hannover Abgasrohr zur Fuehrung von radioaktivem Abgas aus einem Glasschmelzofen zu einem Nasswaescher
US4574714A (en) * 1984-11-08 1986-03-11 United States Steel Corporation Destruction of toxic chemicals
JPH0225577Y2 (https=) * 1985-02-05 1990-07-13
US4617042A (en) * 1985-10-04 1986-10-14 Gas Research Institute Method for the heat processing of glass and glass forming material
EP0493476B1 (en) * 1989-09-29 1998-12-02 Ausmelt Limited Top submerged injection with a shrouded lance
DE4130416C1 (https=) * 1991-09-10 1992-12-10 Thermoselect Ag, Vaduz, Li
US5585532A (en) * 1991-07-29 1996-12-17 Molten Metal Technology, Inc. Method for treating a gas formed from a waste in a molten metal bath
US5188649A (en) * 1991-08-07 1993-02-23 Pedro Buarque de Macedo Process for vitrifying asbestos containing waste, infectious waste, toxic materials and radioactive waste
IN181041B (https=) * 1991-09-20 1998-04-18 Ausmelt Ltd
US5548611A (en) * 1993-05-19 1996-08-20 Schuller International, Inc. Method for the melting, combustion or incineration of materials and apparatus therefor
JP2767187B2 (ja) * 1993-07-06 1998-06-18 動力炉・核燃料開発事業団 ガラス溶融処理方法
DE19512249C2 (de) * 1994-06-10 1996-11-07 Thermoselect Ag Verfahren zum Betreiben einer Sauerstofflanze bei der Hochtemperaturvergasung heterogener Abfälle
US5615626A (en) * 1994-10-05 1997-04-01 Ausmelt Limited Processing of municipal and other wastes
US5798497A (en) * 1995-02-02 1998-08-25 Battelle Memorial Institute Tunable, self-powered integrated arc plasma-melter vitrification system for waste treatment and resource recovery
US5678244A (en) * 1995-02-14 1997-10-14 Molten Metal Technology, Inc. Method for capture of chlorine dissociated from a chlorine-containing compound
JPH09222219A (ja) * 1996-02-14 1997-08-26 Mitsui Eng & Shipbuild Co Ltd 飛灰供給装置及び廃棄物処理装置
DE19637195C2 (de) * 1996-02-16 1998-12-17 Thermoselect Ag Verfahren zum Betreiben eines Hochtemperaturreaktors zur Behandlung von Entsorgungsgütern
JP3668570B2 (ja) * 1996-09-27 2005-07-06 三菱レイヨン株式会社 膜処理装置
JP3380127B2 (ja) * 1996-11-25 2003-02-24 日立造船株式会社 ごみ処理施設における排ガス流路の壁面の冷却方法と冷却装置
US5809911A (en) * 1997-04-16 1998-09-22 Allied Technology Group, Inc. Multi-zone waste processing reactor system
ATE238970T1 (de) * 1998-12-01 2003-05-15 Sgn Soc Gen Tech Nouvelle Verfahren und vorrichtung zum verbrennen und verglasen von abfaellen, insbesondere radioaktiven abfaellen

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3607171A (en) * 1968-07-26 1971-09-21 Vvb Tech Glas Method for heating melting or softening glass in dispersed form
WO1995004004A1 (fr) * 1993-07-28 1995-02-09 Europlasma Procede d'inertage par torche a plasma de produits contenant des metaux, en particulier des metaux lourds et installation pour sa mise en ×uvre
EP0647598A1 (fr) * 1993-10-08 1995-04-12 Commissariat A L'energie Atomique Procédé d'incinération et de vitrification de déchets dans un creuset
US5643350A (en) * 1994-11-08 1997-07-01 Vectra Technologies, Inc. Waste vitrification melter
DE4446576C1 (de) * 1994-12-25 1996-04-25 Sorg Gmbh & Co Kg Wannen-Schmelzofen zum Inertisieren von Schadstoffen durch Verglasen

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JP4048025B2 (ja) 2008-02-13
EP1137603B1 (fr) 2003-05-02
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CA2352108A1 (fr) 2000-06-08
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US6815572B1 (en) 2004-11-09
ES2197716T3 (es) 2004-01-01
US6576807B1 (en) 2003-06-10
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DE69907507D1 (de) 2003-06-05
EP1144320B1 (fr) 2003-03-26
DE69906381D1 (de) 2003-04-30
ATE238970T1 (de) 2003-05-15
KR100501640B1 (ko) 2005-07-18
DE69906381T2 (de) 2004-03-25
ATE235429T1 (de) 2003-04-15
DE69907507T2 (de) 2004-03-25
ES2198167T3 (es) 2004-01-16
KR20010101107A (ko) 2001-11-14

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