EP0028670A1 - Process for preparing bodies containing highly radioactive wastes - Google Patents
Process for preparing bodies containing highly radioactive wastes Download PDFInfo
- Publication number
- EP0028670A1 EP0028670A1 EP19800102963 EP80102963A EP0028670A1 EP 0028670 A1 EP0028670 A1 EP 0028670A1 EP 19800102963 EP19800102963 EP 19800102963 EP 80102963 A EP80102963 A EP 80102963A EP 0028670 A1 EP0028670 A1 EP 0028670A1
- Authority
- EP
- European Patent Office
- Prior art keywords
- glass
- ceramic
- mpa
- pressure
- sintered
- 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.)
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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
- G21F9/30—Processing
- G21F9/301—Processing by fixation in stable solid media
- G21F9/302—Processing by fixation in stable solid media in an inorganic matrix
-
- 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
- G21F9/04—Treating liquids
- G21F9/06—Processing
- G21F9/16—Processing by fixation in stable solid media
- G21F9/162—Processing by fixation in stable solid media in an inorganic matrix, e.g. clays, zeolites
-
- 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
- G21F9/30—Processing
- G21F9/301—Processing by fixation in stable solid media
- G21F9/302—Processing by fixation in stable solid media in an inorganic matrix
- G21F9/305—Glass or glass like matrix
Definitions
- the invention relates to a method for producing molded articles containing highly radioactive waste materials, in which the waste materials are embedded in a glass, glass ceramic or ceramic matrix.
- the glass state is an imbalance state, crystallization can be expected with long-term storage. According to previous knowledge, this begins with the macroscopically inhomogeneously distributed, heterogeneous inclusions, which act as nuclei. Crystallized areas with chemically different composition and fine structure are formed, which are arranged macroscopically inhomogeneous in the remaining glass phase. The highly active fission products are - in varying amounts - mainly concentrated in the crystallized areas. Because of their different composition and structure, these have different coefficients of thermal expansion, which leads to mechanical stresses in a glass block during final storage. In particular, the macroscopically inhomogeneous distribution of the different crystal areas, ultimately based on the macroscopically inhomogeneous distribution of the heterogeneous inclusions, increases the risk of cracking and brittle fracture in the glass block.
- the object of the invention is to provide improved solidification products made of highly radioactive waste and a glass, glass ceramic or ceramic matrix in their properties, in which a homogeneous distribution of the incorporated waste is ensured both during production and during long-term storage. It is a further object of the invention to: •) (DE-OS 26 57 265)
- the object is also achieved in a different way, namely in that the waste materials are first melted in a known manner into a glass, glass ceramic or ceramic matrix, then mechanically comminuted or ground, the comminuted material or the ground material mixed and pressed at a pressure in the range of 5o MPa to 5oo MPa and then sintered below the melting range of the matrix in the devitrification area or pressure sintered in the range of lo to 5o MPa.
- the sludge which contains the waste materials and is thickened with glass, glass ceramic or ceramic powder, is compressed in the slip casting prior to drying.
- According to the invention is sintered at a temperature in the range of 5oo K to 8 00 K or pressure sintered.
- the first solution also offers the advantage that the glass or glass ceramic / ceramic waste mixture does not have to be melted, the processing temperatures can therefore be reduced to about two thirds of the temperatures required by melting technology, viscosity-related flow problems are avoided and crucible Reactions and signs of segregation of the heterogeneous inclusions (segregation, inhomogeneous distribution) are reduced. In addition, the evaporation of highly active components, which was previously unavoidable when melting, is greatly reduced.
- radioactive powder can be introduced into the end products solidified by the process according to the invention.
- a simulated, denitrified waste solution of the following composition was prepared with inactive components:
- this solution was evaporated to dryness and the residue was ground to a particle size of on average lo to 50 ⁇ m (waste powder).
- powder fractions can also be used, but powder fractions that are too finely ground will not be used in order to rule out dust formation as far as possible.
- Example 1 For the production of blocks having a diameter of 2 mm 0 o and 15o mm height by means of cold isostatic pressing in a flexible container, which is for isostatic molding condition, was first described in Example 1, Method. The powder mixture was pressed at a pressure of about 5oo MPa. Thereafter the compacts were lo to 15 hours at 00 6 8 00 K to K sintered and then tempered. The desired macroscopic homogeneity was also achieved with these samples. The density was about 95% of the melt density.
- Example 1 The waste described in Example 1 and glass powder mixture was filled in a graphite mold with graphite stamp and without a preceding continuous cold pressing with simultaneous task a pressure of from lo to 4o MPa at about 6 00 K (indirect heating) hot pressing or pressure-sintered.
- a treatment time of 10 minutes was sufficient for the blocks with a diameter of 20 mm and a height of 25 mm.
- a density of 97% of the solid density on the blocks and the desired macroscopic homogeneity were found.
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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)
- Compositions Of Oxide Ceramics (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
Die Erfindung betrifft ein Verfahren zur Herstellung von hochradioaktive Abfallstoffe enthaltenden Formkörpern, bei welchem die Abfallstoffe in eine Glas- ,Glaskeramik- oder Keramik-Matrix eingebettet werden.The invention relates to a method for producing molded articles containing highly radioactive waste materials, in which the waste materials are embedded in a glass, glass ceramic or ceramic matrix.
Aus der Notwendigkeit einer Langzeitlagerung von hochradioaktiven Abfall enthaltenden Verfestigungsprodukten in beispielsweise Salzstöcken ergeben sich folgende Forderungen an derartige Endlagerungsprodukte:
- Das Produkt muß weitgehend im inneren thermochemischen Gleichgewicht sein, d.h. es muß sich in einem energetischen Minimalzustand befinden, da dies die z.Z. bestmögliche Gewähr für thermochemische Stabilität ist.
- Das Produkt muß so beschaffen sein, daß Wechselwirkungen mit der Umgebung nicht zu einem Sicherheitsrisiko werden können. Solche Wechselwirkungen sind nicht ausschließbar, da den realen Zustandsbedingungen gemäß und den möglichen Änderungen der Zustandsbedingungen über einen langen Zeitraum entsprechend ein Gleichgewicht zwischen dem Endlagerungsprodukt und seiner Umgebung in der Lagerstätte nicht gewährleistet werden kann.
Werden diese Forderungen nicht erfüllt, so können
- durch Veränderungen im Produkt die Wechselwirkungen zwischen verschiedenen Kompcnenten oder Phasenumwandlungen oder dessen Eigenschaften, wie z.B. die Wärmeleitfähigkeit, Korrosionsresistenz oder Festigkeit, ungünstig verändert werden und durch chemische und/oder mechanische Wechselwirkung mit der Umgebung, wie Auslaugung oder mechanische Beanspruchung durch geologische Druck- und Scherkräfte, die Endlagerungsprodukte ganz oder teilweise zerstört werden.
- The product must be largely in the internal thermochemical equilibrium, ie it must be in an energetically minimal state, since this is currently the best possible guarantee for thermochemical stability.
- The product must be designed in such a way that interactions with the environment cannot become a safety risk. Such interactions cannot be ruled out, because according to the real state conditions and the possible changes in the state conditions over a long period of time, a balance between the final storage product and its surroundings in the deposit cannot be guaranteed.
If these requirements are not met, you can
- due to changes in the product, the interactions between different components or phase transformations or their properties, such as thermal conductivity, corrosion resistance or strength, are adversely changed and through chemical and / or mechanical interaction with the environment, such as leaching or mechanical stress due to geological pressure and shear forces , the disposal products are completely or partially destroyed.
In jedem Falle wäre damit aber der unkontrollierbare Übertritt von hochradioakiven Spaltprodukten in die Biosphäre verbunden.In any case, this would involve the uncontrollable transfer of highly radioactive fission products into the biosphere.
Für die Endlagerung von hochradioaktivem Abfall ist dessen Einschmelzen in Glasblöcken vorgesehen. Dabei werden die im allgemeinen denitrierten Spaltproduktoxide zum Teil homogen im Glas gelöst. Der restliche Teil, vorwiegend Edelmetalle, liegt als heterogene Einschlüsse in der Glasmatrix vor. Die Verteilung dieser Einschlüsse ist bei dem derzeitigen Stand der Schmelztechnologie nicht reproduzierbar und makroskopisch meist nicht homogen.For the final storage of highly radioactive waste, it is intended to be melted down in glass blocks. The generally denitrified fission product oxides are partially dissolved homogeneously in the glass. The remaining part, mainly precious metals, is present as heterogeneous inclusions in the glass matrix. The distribution of these inclusions is not reproducible at the current state of melting technology and is usually not macroscopically homogeneous.
Da der Glaszustand ein Ungleichgewichtszustand ist, ist bei Langzeitlagerung mit Kristallisation zu rechnen. Diese beginnt nach bisherigen Erkenntnissen an den makroskopisch inhomogen verteilten, heterogenen Einschlüssen, die als Kristallisationskeime wirken. Es bilden sich kristallisierte Bereiche mit chemisch unterschiedlicher Zusammensetzung und Feinstruktur, die makroskopisch inhomogen in der verbleibenden Glasphase angeordnet sind. Die hochaktiven Spaltprodukte sind -- in unterschiedlicher Menge - vorwiegend in den kristallisierten Bereichen konzentriert. Diese haben wegen ihrer unterschiedlichen Zusammensetzung und Struktur, unterschiedliche thermische Ausdehnungskoeffizienten, was in einem Glasblock bei Endlagerung zu mechanischen Spannungen führt. Dabei erhöht insbesondere die makroskopisch inhomogene Verteilung der unterschiedlichen Kristallbereiche, letztlich ausgehend von der makroskopisch inhomogenen Verteilung der heterogenen Einschlüsse, die Gefahr von Rissbildung und Sprödbruch im Glasblock.Since the glass state is an imbalance state, crystallization can be expected with long-term storage. According to previous knowledge, this begins with the macroscopically inhomogeneously distributed, heterogeneous inclusions, which act as nuclei. Crystallized areas with chemically different composition and fine structure are formed, which are arranged macroscopically inhomogeneous in the remaining glass phase. The highly active fission products are - in varying amounts - mainly concentrated in the crystallized areas. Because of their different composition and structure, these have different coefficients of thermal expansion, which leads to mechanical stresses in a glass block during final storage. In particular, the macroscopically inhomogeneous distribution of the different crystal areas, ultimately based on the macroscopically inhomogeneous distribution of the heterogeneous inclusions, increases the risk of cracking and brittle fracture in the glass block.
Der Erfindung liegt die Aufgabe zugrunde, in ihren Eigenschaften verbesserte Verfestigungsprodukteaus hochradioaktiven Abfällen und einer Glas-,Glaskeramik- cder Keramik-Matrix bereitzustellen, bei denen sowchl während der Herstellung als auch während der Langzeitlagerung eine homogene Verteilung der inkorporierten Abfälle gewährleistet ist. Es ist weiterhin Aufgabe der Erfindung, ein •) (DE-OS 26 57 265)The object of the invention is to provide improved solidification products made of highly radioactive waste and a glass, glass ceramic or ceramic matrix in their properties, in which a homogeneous distribution of the incorporated waste is ensured both during production and during long-term storage. It is a further object of the invention to: •) (DE-OS 26 57 265)
Verfahren zu schaffen, mit welchem zwischen- und endlagerbare Formkörper solcher verbesserter Verfestigungsprodukte hergestellt werden können. Insbesondere sollen mechanische Spannungen, die die Gefahr von Rissbildung und Sprödbruch im Formkörper in sich bergen, vermieden werden.To create methods with which intermediate and final storage moldings of such improved solidification products can be produced. In particular, mechanical stresses which involve the risk of crack formation and brittle fracture in the molded body are to be avoided.
Die Aufgabe wird in überraschend einfacher Weise erfindungsgemäß dadurch gelöst, daß die Abfallstoffe
- a) in Form eines trockenen oder nahezu trockenen Pulvers mit einer Glas-, Glaskeramik- cder Keramik-Matrix in Granulat-oder Pulver-Form oder
- b) in Form eines Schlammes mit Glas-, Glaskeramik- oder Keramik-Pulver verdickt,
mechanisch gemischt und im Falle von b) getrocknet werden, danach bei einem Druck im Bereich von 5o MPa bis 5oo MPa gepreßt und anschließend unterhalb des Schmelzbereiches der Matrix im Entglasungsbereich gesintert oder im Bereich von lo bis 5o MPa druckgesintert werden.The object is achieved in a surprisingly simple manner according to the invention in that the waste materials
- a) in the form of a dry or almost dry powder with a glass, glass ceramic or ceramic matrix in granule or powder form or
- b) thickened in the form of a slurry with glass, glass ceramic or ceramic powder,
mechanically mixed and dried in the case of b), then pressed at a pressure in the range from 5o MPa to 5oo MPa and then sintered below the melting range of the matrix in the devitrification area or pressure sintered in the range from lo to 5o MPa.
Erfindungsgemäß wird die Aufgabe aber auch in einer anderen Weise gelöst, nämlich dadurch, daß die Abfallstoffe zunächst in be-kannter Weise in eine Glas-, Glaskeramik- oder Keramik-Matrix eingeschmolzen werden, danach mechanisch zerkleinert oder gemahlen, das Zerkleinerungsgut bzw. das Mahlgut durchmischt und bei einem Druck im Bereich von 5o MPa bis 5oo MPa gepreßt und anschließend unterhalb des Schmelzbereiches der Matrix im Entglasungsbereich -gesintert oder im Bereich von lo bis 5o MPa druckgesintert werden.According to the invention, however, the object is also achieved in a different way, namely in that the waste materials are first melted in a known manner into a glass, glass ceramic or ceramic matrix, then mechanically comminuted or ground, the comminuted material or the ground material mixed and pressed at a pressure in the range of 5o MPa to 5oo MPa and then sintered below the melting range of the matrix in the devitrification area or pressure sintered in the range of lo to 5o MPa.
In einer besonderen Ausbildung des erfindungsgemäßen Verfahrens wird der mit Glas-,Glaskeramik- oder Keramik-Pulver verdickte, die Abfallstoffe enthaltende Schlamm vor dem Trocknen im Schlickerguß verdichtet.In a special embodiment of the method according to the invention, the sludge, which contains the waste materials and is thickened with glass, glass ceramic or ceramic powder, is compressed in the slip casting prior to drying.
Erfindungsgemäß wird bei einer Temperatur im Bereich von 5oo K bis 800 K gesintert oder druckgesintert.According to the invention is sintered at a temperature in the range of 5oo K to 8 00 K or pressure sintered.
Mit beiden Lösungswegen entsteht ein Endprodukt mit homogenisiertem Aufbau, mit reduzierten, mechanischen Spannungsgradienten bei Erwärmung, wie sie bei einer Endlagerung auftreten wird, und somit mit erhöhter, mechanischer Stabilität des Endlagerblocks. Während des abschließenden Sinterns tritt mit der Formgebung eine Verdichtung und gleichzeitig bei geeigneten technologischen Bedingungen vorteilhafte Teilkristallisation ein, die lediglich kleine Kristalle erzeugt und eine unkontrollierte, willkürliche Bildung größerer Kristalle während der Endlagerung vermeidet.Both solutions result in an end product with a homogenized structure, with reduced mechanical stress gradients when heated, as will occur during final storage, and thus with increased mechanical stability of the repository block. During the final sintering, the shaping leads to densification and, at the same time, advantageous partial crystallization under suitable technological conditions, which only produces small crystals and avoids an uncontrolled, arbitrary formation of larger crystals during final storage.
Der erste Lösungsweg bietet außerdem den Vorteil, daß die Glas-, bzw. Glaskeramik-/Keramik-Abfall-Mischung nicht aufgeschmolzen werden muß, die Bearbeitüngstemperaturen daher auf etwa zwei Drittel der schmelztechnelogisch notwendigen Temperaturen herabgesetzt werden können, viskositätsbedingte Fließprobleme vermieden werden und Tiegel-Reaktionen und Segregationserscheinungen der heterogenen Einschlüsse (Entmischung, inhomogene Verteilung) reduziert werden. Außerdem wird die bisher beim Erschmelzen unvermeidbare Abdampfung hochaktiver Bestandteile sehr stark reduziert.The first solution also offers the advantage that the glass or glass ceramic / ceramic waste mixture does not have to be melted, the processing temperatures can therefore be reduced to about two thirds of the temperatures required by melting technology, viscosity-related flow problems are avoided and crucible Reactions and signs of segregation of the heterogeneous inclusions (segregation, inhomogeneous distribution) are reduced. In addition, the evaporation of highly active components, which was previously unavoidable when melting, is greatly reduced.
Je nach Durchführbarkeit der Wärmeabfuhr aus den inkorporierten Radionukliden und je nach den hiermit in Zusammenhang stehenden Block- bzw. Formkörpergrößen können bis zu 4o Gew.-% an radioaktivem Pulver in die nach dem erfindungsgemäßen Verfahren verfestigten Endprodukte eingebracht werden.Depending on the feasibility of heat removal from the incorporated radionuclides and depending on the block or molded body sizes associated therewith, up to 40% by weight of radioactive powder can be introduced into the end products solidified by the process according to the invention.
Im folgenden wird die Erfindung anhand einiger Beispiele näher erläutert. Die Erfindung ist jedoch auf diese Beispiele nicht beschränkt.The invention is explained in more detail below with the aid of a few examples. However, the invention is not limited to these examples.
Mit inaktiven Bestandteilen wurde eine simulierte, denitrierte Abfall-Lösung der folgenden Zusammensetzung hergestellt:
Zur Verwendung im erfindungsgemäßen Verfahren wurde diese Lösung zur Trockne eingedampft und der Rückstand auf eine Partikelgröße von im Mittel lo bis 5oµm gemahlen (Abfallpulver). Grundsätzlich können auch andere Pulverfraktionen eingesetzt werden, doch wird man nicht zu fein gemahlene Pulverfraktionen nehmen, um eine Staubentwicklung möglichst auszuschließen.For use in the process according to the invention, this solution was evaporated to dryness and the residue was ground to a particle size of on average lo to 50 μm (waste powder). In principle, other powder fractions can also be used, but powder fractions that are too finely ground will not be used in order to rule out dust formation as far as possible.
Zur Herstellung der Probeblöcke (Formkörper) wurden jeweils 15 Gewichtsteile des so erhaltenen Abfallpulvers mit 85 Gewichtsteilen einer ebenfalls auf eine Partikelgröße von im Mittel lo bis 15/um gemahlenen Glasfritte aus Borosilikatglas der Zusammensetzung (in Gew.-%):
Zur Herstellung von Blöcken mit einem Durchmesser von 20o mm und 15o mm Höhe mit Hilfe von isostatischem Kaltpressen in einem flexiblen Gefäß, was für isostatische Formgebung Bedingung ist, wurde zunächst, wie in Beispiel 1 beschrieben, verfahren. Das Pulvergemisch wurde mit einem Druck von ca. 5oo MPa gepreßt. Danach wurden die Preßlinge lo bis 15 Stunden lang bei 600 K bis 800 K gesintert und anschließend getempert. Die angestrebte makroskopische Homogenität wurde auch bei diesen Proben erreicht. Die Dichte betrug etwa 95 % der Schmelzlingsdichte.For the production of blocks having a diameter of 2 mm 0 o and 15o mm height by means of cold isostatic pressing in a flexible container, which is for isostatic molding condition, was first described in Example 1, Method. The powder mixture was pressed at a pressure of about 5oo MPa. Thereafter the compacts were lo to 15 hours at 00 6 8 00 K to K sintered and then tempered. The desired macroscopic homogeneity was also achieved with these samples. The density was about 95% of the melt density.
Die in Beispiel 1 beschriebene Abfall- und Glas-Pulvermischung wurde in eine Graphit-Form mit Graphitstempel eingefüllt und ohne vorangehendes Kaltpressen unter gleichzeitiger Aufgabe eines Druckes von lo bis 4o MPa bei ca. 600 K (indirekte Beheizung) heißgepreßt bzw. druckgesintert. Für die Blöcke mit einem Durchmesser von 2o mm und einer Höhe von 25 mm war eine Behandlungsdauer von lo Minuten ausreichend. Es wurde eine Dichte von 97 % der Schmelzlingsdichte an den Blöcken festgestellt, sowie die gewünschte makroskopische Homogenität.The waste described in Example 1 and glass powder mixture was filled in a graphite mold with graphite stamp and without a preceding continuous cold pressing with simultaneous task a pressure of from lo to 4o MPa at about 6 00 K (indirect heating) hot pressing or pressure-sintered. A treatment time of 10 minutes was sufficient for the blocks with a diameter of 20 mm and a height of 25 mm. A density of 97% of the solid density on the blocks and the desired macroscopic homogeneity were found.
Claims (4)
mechanisch gemischt und im Falle b) getrocknet werden, danach bei einem Druck im Bereich von 5o MPa bis 5oo MPa gepreßt und anschließend unterhalb des Schmelzbereiches der Matrix im Entglasungsbereich gesintert oder im Bereich von lo bis 5o MPa druckgesintert werden.1. A process for the production of moldings containing highly radioactive waste materials, in which the waste materials are embedded in a glass, glass ceramic or ceramic matrix, characterized in that the waste materials
mechanically mixed and dried in case b), then pressed at a pressure in the range from 5o MPa to 5oo MPa and then sintered below the melting range of the matrix in the devitrification area or pressure sintered in the range from lo to 5o MPa.
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE2945006 | 1979-11-08 | ||
DE19792945006 DE2945006C2 (en) | 1979-11-08 | 1979-11-08 | Process for the production of molded bodies containing highly radioactive waste |
Publications (2)
Publication Number | Publication Date |
---|---|
EP0028670A1 true EP0028670A1 (en) | 1981-05-20 |
EP0028670B1 EP0028670B1 (en) | 1983-09-28 |
Family
ID=6085400
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP19800102963 Expired EP0028670B1 (en) | 1979-11-08 | 1980-05-28 | Process for preparing bodies containing highly radioactive wastes |
Country Status (4)
Country | Link |
---|---|
EP (1) | EP0028670B1 (en) |
JP (1) | JPS5682499A (en) |
BR (1) | BR8007001A (en) |
DE (1) | DE2945006C2 (en) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2525381A1 (en) * | 1982-04-17 | 1983-10-21 | Kernforschungsz Karlsruhe | PROCESS FOR IMPROVING THE PROPERTIES NECESSARY FOR LONG-TERM STORAGE OF SOLIDIFIED RADIOACTIVE WASTE |
EP0136401A2 (en) * | 1983-05-30 | 1985-04-10 | Hitachi, Ltd. | Method and apparatus for processing radioactive waste resin |
EP0156001A2 (en) * | 1983-12-01 | 1985-10-02 | Forschungszentrum Jülich Gmbh | Process for conditioning contaminated waste by coating with cement |
US4855082A (en) * | 1983-09-09 | 1989-08-08 | Willy De Roode | Process for rendering harmless dangerous chemical waste |
WO2018152290A1 (en) * | 2017-02-16 | 2018-08-23 | GeoRoc International, Inc. | Composition and method for the processing of hazardous sludges and ion exchange media |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4778626A (en) * | 1985-11-04 | 1988-10-18 | Australian Nat'l Univ. of Acton | Preparation of particulate radioactive waste mixtures |
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US3000072A (en) * | 1959-08-20 | 1961-09-19 | Ca Atomic Energy Ltd | Process of containing and fixing fission products |
DE2534014A1 (en) * | 1975-07-30 | 1977-02-17 | Kernforschung Gmbh Ges Fuer | THERMODYNAMICALLY STABLE CERAMIC GLASS PRODUCT OR CERAMIC GLASS PRODUCT FOR THE FINAL DISPOSAL OF HIGHLY RADIOACTIVE WASTE |
DE2747951A1 (en) * | 1976-11-02 | 1978-05-11 | Asea Ab | PROCESS FOR BINDING RADIOACTIVE SUBSTANCES IN A BODY THAT IS RESISTANT TO LEAKAGE BY WATER |
Family Cites Families (2)
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DE2627265A1 (en) * | 1976-06-18 | 1977-12-29 | Krauss Maffei Ag | Decanter type centrifuge with cake washing - having inserts inside bowl to cause break up of cake |
FR2375695A1 (en) * | 1976-12-21 | 1978-07-21 | Asea Ab | PROCESS FOR THE TREATMENT OF RADIOACTIVE WASTE |
-
1979
- 1979-11-08 DE DE19792945006 patent/DE2945006C2/en not_active Expired
-
1980
- 1980-05-28 EP EP19800102963 patent/EP0028670B1/en not_active Expired
- 1980-10-30 BR BR8007001A patent/BR8007001A/en unknown
- 1980-11-07 JP JP15673880A patent/JPS5682499A/en active Pending
Patent Citations (5)
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US3000072A (en) * | 1959-08-20 | 1961-09-19 | Ca Atomic Energy Ltd | Process of containing and fixing fission products |
DE2534014A1 (en) * | 1975-07-30 | 1977-02-17 | Kernforschung Gmbh Ges Fuer | THERMODYNAMICALLY STABLE CERAMIC GLASS PRODUCT OR CERAMIC GLASS PRODUCT FOR THE FINAL DISPOSAL OF HIGHLY RADIOACTIVE WASTE |
US4097401A (en) * | 1975-07-30 | 1978-06-27 | Gesellschaft Fur Kernforschung M.B.H. | Thermodynamically stable product for permanent storage and disposal of highly radioactive liquid wastes |
DE2747951A1 (en) * | 1976-11-02 | 1978-05-11 | Asea Ab | PROCESS FOR BINDING RADIOACTIVE SUBSTANCES IN A BODY THAT IS RESISTANT TO LEAKAGE BY WATER |
FR2369659A1 (en) * | 1976-11-02 | 1978-05-26 | Asea Ab | PR |
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2525381A1 (en) * | 1982-04-17 | 1983-10-21 | Kernforschungsz Karlsruhe | PROCESS FOR IMPROVING THE PROPERTIES NECESSARY FOR LONG-TERM STORAGE OF SOLIDIFIED RADIOACTIVE WASTE |
GB2121232A (en) * | 1982-04-17 | 1983-12-14 | Kernforschungsz Karlsruhe | Method for solidifying radioactive wastes |
EP0136401A2 (en) * | 1983-05-30 | 1985-04-10 | Hitachi, Ltd. | Method and apparatus for processing radioactive waste resin |
EP0136401A3 (en) * | 1983-05-30 | 1986-03-26 | Hitachi, Ltd. | Method and apparatus for processing radioactive waste resin |
US4855082A (en) * | 1983-09-09 | 1989-08-08 | Willy De Roode | Process for rendering harmless dangerous chemical waste |
EP0156001A2 (en) * | 1983-12-01 | 1985-10-02 | Forschungszentrum Jülich Gmbh | Process for conditioning contaminated waste by coating with cement |
EP0156001A3 (en) * | 1983-12-01 | 1986-10-15 | Kernforschungsanlage Julich Gesellschaft Mit Beschrankter Haftung | Process for conditioning contaminated waste by coating with cement |
WO2018152290A1 (en) * | 2017-02-16 | 2018-08-23 | GeoRoc International, Inc. | Composition and method for the processing of hazardous sludges and ion exchange media |
CN110291593A (en) * | 2017-02-16 | 2019-09-27 | 乔罗克国际股份有限公司 | For handling the composition and method of harmful sludge and Ion Exchange Medium |
CN110291593B (en) * | 2017-02-16 | 2024-04-16 | 乔罗克国际股份有限公司 | Compositions and methods for treating hazardous sludge and ion exchange media |
Also Published As
Publication number | Publication date |
---|---|
DE2945006C2 (en) | 1987-01-15 |
DE2945006A1 (en) | 1981-05-21 |
EP0028670B1 (en) | 1983-09-28 |
BR8007001A (en) | 1981-05-12 |
JPS5682499A (en) | 1981-07-06 |
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