EP0486568A1 - Verfahren und vorrichtung zur zersetzung verbrauchter ionenaustauscherharze - Google Patents
Verfahren und vorrichtung zur zersetzung verbrauchter ionenaustauscherharzeInfo
- Publication number
- EP0486568A1 EP0486568A1 EP19900912270 EP90912270A EP0486568A1 EP 0486568 A1 EP0486568 A1 EP 0486568A1 EP 19900912270 EP19900912270 EP 19900912270 EP 90912270 A EP90912270 A EP 90912270A EP 0486568 A1 EP0486568 A1 EP 0486568A1
- Authority
- EP
- European Patent Office
- Prior art keywords
- reactor
- reactor chamber
- container
- end container
- filter
- 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- Withdrawn
Links
- 238000000034 method Methods 0.000 title claims abstract description 37
- 239000003456 ion exchange resin Substances 0.000 title claims abstract description 14
- 229920003303 ion-exchange polymer Polymers 0.000 title claims abstract description 14
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims abstract description 32
- 239000007788 liquid Substances 0.000 claims abstract description 29
- 238000006243 chemical reaction Methods 0.000 claims abstract description 17
- 239000003054 catalyst Substances 0.000 claims abstract description 14
- 230000000694 effects Effects 0.000 claims abstract description 5
- 230000001105 regulatory effect Effects 0.000 claims abstract description 5
- 238000009413 insulation Methods 0.000 claims abstract description 3
- 238000000354 decomposition reaction Methods 0.000 claims description 21
- 239000007787 solid Substances 0.000 claims description 14
- 239000000463 material Substances 0.000 claims description 12
- 230000001681 protective effect Effects 0.000 claims description 11
- 239000007789 gas Substances 0.000 claims description 10
- 239000007800 oxidant agent Substances 0.000 claims description 10
- 230000002285 radioactive effect Effects 0.000 claims description 10
- 239000003344 environmental pollutant Substances 0.000 claims description 9
- 231100000719 pollutant Toxicity 0.000 claims description 9
- 238000007254 oxidation reaction Methods 0.000 claims description 6
- 238000003860 storage Methods 0.000 claims description 6
- 238000010438 heat treatment Methods 0.000 claims description 5
- 229910052792 caesium Inorganic materials 0.000 claims description 4
- TVFDJXOCXUVLDH-UHFFFAOYSA-N caesium atom Chemical compound [Cs] TVFDJXOCXUVLDH-UHFFFAOYSA-N 0.000 claims description 4
- 229910000358 iron sulfate Inorganic materials 0.000 claims description 4
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 claims description 4
- 230000003647 oxidation Effects 0.000 claims description 4
- 239000003795 chemical substances by application Substances 0.000 claims description 3
- 238000001914 filtration Methods 0.000 claims description 3
- 229930195733 hydrocarbon Natural products 0.000 claims description 3
- 150000002430 hydrocarbons Chemical class 0.000 claims description 3
- 239000000376 reactant Substances 0.000 claims description 3
- 238000003756 stirring Methods 0.000 claims description 3
- 239000000654 additive Substances 0.000 claims description 2
- 230000001276 controlling effect Effects 0.000 claims description 2
- 239000011521 glass Substances 0.000 claims description 2
- 230000001590 oxidative effect Effects 0.000 claims description 2
- 229920000728 polyester Polymers 0.000 claims description 2
- 238000001556 precipitation Methods 0.000 claims description 2
- 230000000996 additive effect Effects 0.000 claims 1
- 239000012141 concentrate Substances 0.000 claims 1
- 150000002500 ions Chemical class 0.000 claims 1
- 238000001704 evaporation Methods 0.000 abstract description 2
- 230000008020 evaporation Effects 0.000 abstract description 2
- 239000010815 organic waste Substances 0.000 abstract 1
- 239000002699 waste material Substances 0.000 description 10
- NWUYHJFMYQTDRP-UHFFFAOYSA-N 1,2-bis(ethenyl)benzene;1-ethenyl-2-ethylbenzene;styrene Chemical compound C=CC1=CC=CC=C1.CCC1=CC=CC=C1C=C.C=CC1=CC=CC=C1C=C NWUYHJFMYQTDRP-UHFFFAOYSA-N 0.000 description 5
- 238000004380 ashing Methods 0.000 description 5
- 239000002253 acid Substances 0.000 description 4
- 239000006260 foam Substances 0.000 description 4
- 239000000941 radioactive substance Substances 0.000 description 4
- 239000002901 radioactive waste Substances 0.000 description 4
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- 238000010276 construction Methods 0.000 description 3
- 238000012545 processing Methods 0.000 description 3
- 239000012857 radioactive material Substances 0.000 description 3
- 239000011347 resin Substances 0.000 description 3
- 229920005989 resin Polymers 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 2
- 150000007513 acids Chemical class 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 238000001784 detoxification Methods 0.000 description 2
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 2
- 230000002349 favourable effect Effects 0.000 description 2
- 239000002920 hazardous waste Substances 0.000 description 2
- 238000005342 ion exchange Methods 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- 238000004886 process control Methods 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 239000012429 reaction media Substances 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 238000007086 side reaction Methods 0.000 description 2
- 238000007711 solidification Methods 0.000 description 2
- 230000008023 solidification Effects 0.000 description 2
- 239000011593 sulfur Substances 0.000 description 2
- 231100000331 toxic Toxicity 0.000 description 2
- 230000002588 toxic effect Effects 0.000 description 2
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 238000007792 addition Methods 0.000 description 1
- 239000002518 antifoaming agent Substances 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 238000002144 chemical decomposition reaction Methods 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 238000007596 consolidation process Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000000151 deposition Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- TXKMVPPZCYKFAC-UHFFFAOYSA-N disulfur monoxide Inorganic materials O=S=S TXKMVPPZCYKFAC-UHFFFAOYSA-N 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000010881 fly ash Substances 0.000 description 1
- 238000005187 foaming Methods 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 230000001771 impaired effect Effects 0.000 description 1
- 239000006193 liquid solution Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000011159 matrix material Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 125000002081 peroxide group Chemical group 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 230000001376 precipitating effect Effects 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 238000003904 radioactive pollution Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 239000000523 sample Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000000057 synthetic resin Substances 0.000 description 1
- 229920003002 synthetic resin Polymers 0.000 description 1
- 238000004056 waste incineration Methods 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Classifications
-
- A—HUMAN NECESSITIES
- A62—LIFE-SAVING; FIRE-FIGHTING
- A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
- A62D3/00—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
- A62D3/30—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
- A62D3/38—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents by oxidation; by combustion
-
- 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
-
- A—HUMAN NECESSITIES
- A62—LIFE-SAVING; FIRE-FIGHTING
- A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
- A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
- A62D2101/20—Organic substances
-
- A—HUMAN NECESSITIES
- A62—LIFE-SAVING; FIRE-FIGHTING
- A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
- A62D2203/00—Aspects of processes for making harmful chemical substances harmless, or less harmful, by effecting chemical change in the substances
- A62D2203/10—Apparatus specially adapted for treating harmful chemical agents; Details thereof
Definitions
- the invention relates to a process for the continuous decomposition of solid pollutant materials, e.g. spent radioactive ion exchange resins, which are continuously fed to a reactor room, by oxidation by means of a liquid oxide guarantee.
- solid pollutant materials e.g. spent radioactive ion exchange resins
- ion exchange resins for the treatment of radioactive materials. After use, these resins form a large part of the low and medium contaminated nuclear waste, depending on their radioactive content. Most of the commercially used ion exchange materials are synthetic resins. In view of the growing need for additional hazardous waste absorption capacity and its limited availability, volume and weight-concentrating pretreatment of the used ion exchange resins is necessary and economical before further storage preparation for safe depositing of the waste takes place.
- the object of the invention is to disclose a simplified and effective and economical process for the decomposition for the purpose of volume reduction of spent, radioactively contaminated, ion exchange resin and to provide a device for its simple, safe and reliable implementation under easily controllable temperature and pressure conditions.
- the solution to the problem is that the oxidant is hydrogen peroxide, which is continuously metered into the reactor chamber after introduction of a starting energy, and that the resulting residual liquid is continuously removed in a final container that the decomposition of the solid pollutant materials in a temperature range between 100 C. C and 140 ° C takes place, the introduction of the starting energy and the Oxydentien-Dosage controlled or regulated so that this temperature range is reached quickly and then maintained.
- the oxidant is hydrogen peroxide, which is continuously metered into the reactor chamber after introduction of a starting energy, and that the resulting residual liquid is continuously removed in a final container that the decomposition of the solid pollutant materials in a temperature range between 100 C. C and 140 ° C takes place, the introduction of the starting energy and the Oxydentien-Dosage controlled or regulated so that this temperature range is reached quickly and then maintained.
- the reaction temperature is maintained at a level between 105 ° C and 135 ⁇ C depending on the desired decomposition speed of the system dimensions, the foam level and the predetermined amount of feed of the reactants and of the residual solution dosage.
- the advantages of the invention are, in particular, that the operating costs, the construction costs and the maintenance costs of a system required therefor are low and the exhaust gas can be treated quite simply in a closed dispensing treatment device.
- a process control is advantageously provided in which the oxidizing agent is used so sparingly that there is only decomposition but no complete oxidation of the ion exchange resin.
- Fig. 1 shows a decomposition device, schematically, with a vertical section of the reactor.
- Fig. 2 shows a detail section with replaceable filter.
- Fig. 1 shows the functionally essential modules and a reactor schematically; its dimensions and dimensional relationships are typical but changeable, whereby the function is not impaired.
- the decomposition device consists of a hopper reactor (1) which is surrounded by an outer protective jacket (2).
- a hydrogen peroxide tank
- the bottom of the reactor (1) and the protective jacket (2) are releasably connected by a releasable closure (120) to an end container (5) which absorbs both liquid residues during operation and the solid residues after the end of an operating period.
- the bottom end (12) of the reactor (1) is advantageously a filter disk made of sintered glass, which only allows the liquid residues to pass through and only when the solid residues are open can it pass into the end container (5).
- the introduction of catalytic material is provided to start the reaction.
- This is preferably iron sulfate.
- the catalyst (61) is advantageously on a long arm Shovel (6) brought into the reactor (1), namely under the outlet (23) of the oxidizing agent, which is advantageously designed as a nozzle assembly.
- the shovel (6) can be moved to the shovel handle (62) with an adjusting drive (63) to different heights; this influences the course of the reaction.
- the blade handle (62) is designed as a tube which ends at the bottom in the spoon-like recessed blade (6) and at the top carries a funnel attachment or a metering device (64) for introducing the catalyst material.
- the reactor (1) is surrounded directly and on the protective jacket (2) with a thermal insulating jacket (20), so that the decomposition energy released heats up the matrix used to a favorable reaction temperature.
- the process control takes place via one or more temperature measuring probes (7) whose signal or signals are fed to the control device (ST), the metering devices (13, 14, 15), the catalyst feed device (64) and the catalyst adjustment drive (63) controls that a favorable predetermined temperature range is quickly reached in the decomposition reaction and then maintained.
- the exhaust gas is passed through the outlet (11) on the jacket (2) into a cooled condenser (8) and then through a HEPA filter (9).
- the condensate accumulating in the condenser (8) is collected in a receiver (10) and disposed of from there.
- the decomposition process is started with the exothermic decomposition reaction of preferably 60% hydrogen oxide using solid iron sulfate. A physical energy supply is therefore not required, which keeps the device simple.
- the Decomposing hydrogen peroxide attacks the resin used, the decomposition of which follows is also exothermic, so that more heat is released in the reaction medium. This heat collected in the reaction medium decomposes the hydrogen peroxide solution which is fed in and which in turn attacks more ion exchange resin.
- This reaction continues depending on the supply of the two components, which is ultimately limited by the dimensions of the reactor vessel.
- the reaction products are solid residues, liquid solution residues and exhaust gas as well as exhaust steam.
- the solid residues that collect at the bottom of the shaft reactor contain most radioactive substances.
- the cesium, if any, which is highly soluble, is largely contained in the residue liquid.
- the residue liquid, which has been collected in each of the end containers (5), is advantageously returned through the reactor (1) for evaporation so that its volume decreases due to the use of the reactor heat.
- the treatment of the residual liquid depends on its quantity and its level of activity, which in turn depends on the type and composition of the waste that has been decomposed and on the type and quantity of the radioactive substances therein, in the following way:
- the residual liquid has a relatively very low radioactivity, then regardless of its amount, it is directed to the condensate container (10) outside the control zone (17) through a first route of the controllable two-way valve (16).
- the residue liquid has a high specific radioactivity and a large amount is produced, then it is chemically treated in the final container (5) for the purpose of precipitating the radioactive substances and returned via the second way of the two-way valve (16) to the reactor (1), where the precipitates are filtered out. - If the residue liquid has a high specific radioactivity and a large amount is produced, then it is chemically treated in the final container (5) for the purpose of precipitating the radioactive substances and returned via the second way of the two-way valve (16) to the reactor (1), where the precipitates are filtered out. - If the residue liquid has a high specific
- temperature, level and activity sensors (7, N1, N2, A1, A2) are arranged in the reactor (1) and 'in the end container (5), the signals of which are fed to the control device (ST).
- this controls the two-way valve (16) and the supply of the precipitants (F) and the additives (V), which are used for consolidation, into the end container (5) in accordance with predetermined limit values.
- Continuous operation is determined after the catalytic start by the continuous metering of the resin and the controlled supply of the oxidizing agent. If foam is formed, the metering of the reactants is regulated anew when the foam has reached a predetermined level in the reactor.
- the filter closure (12) can be pivoted by the control device (ST) with a controlled drive (12A), so that the solid residues can be emptied each time after the reaction space (1) has been filled a predetermined level and after a subsequent termination of the decomposition reaction and possibly after a precipitation reaction and the completion of the subsequent filtering of the precipitated material, by pivoting the filter closure into the final container.
- a precipitant for example, if radioactive cesium is contained in the residue liquid, concentrated tripotassium ferrohexacyanide is added, as a result of which the cesium is bound and can be filtered out and then compacted and brought into the final container as a solid residue.
- V solidification surcharge for the residues
- water-compatible polyester is suitable, which is brought to the setting in the end container (5).
- the exhaust gas and the exhaust steam are passed through the condenser (8) and then passed through a HEPA filter.
- This stage of the process depends primarily on the decomposition of the organic ion exchange resin. It is advantageously not necessary to carry out a complete oxidation in the zone controlled for radioactivity.
- the concentration of hydrocarbons in the condensate in the condensate container (10) is relatively high, it can be post-oxidized there or later, if necessary, for example also with hydrogen peroxide.
- the supply of hydrogen peroxide is provided with a controllable metering device (D) and an additional heater (H) is built into the condensate container (10).
- This is expediently thermally insulated.
- the resulting decomposition products of post-oxidation, namely carbon dioxide and water vapor leave the container (10) through the exhaust air duct (8A) of the cooler (8) and further through the filter (9).
- the main reactor in the control zone is then not burdened with this side reaction.
- FIG. 2 A section of the device is shown in FIG. 2 with a different, replaceable filter arrangement. It is envisaged that a replacement of the filter disc (12) is possible during operation if such fine residues occur that they clog the filter (12) and pivoting, as is provided in the device according to Fig.1, not is sufficient to clean the filter.
- a horizontal transport path (21) is led into the reactor (1) just above the filter (12) through the protective jacket (2) and the reactor jacket.
- a filter carrier (22) closed at the top with a replacement filter (12 ') can be inserted into the reactor (1) on the transport path.
- the used filter (12) is fastened in an externally detachable holder (28).
- the embodiments shown are preferred, very simple and easily controllable constructions, which have it modified professionally.
- another form of energy input can be selected, for example in the form of an electrical heating device, that is to say a heating wire.
- the filter is also possible to replace the filter from below in the end container area instead of from the side, which saves the lock and the transport device.
- several filters are pivotally arranged on the edge of the outlet of the reactor space, which can be swiveled in in a controlled manner and released from their holder. With such a change of the filter, however, the remaining contents of the reactor space are emptied into the final container. From there, the liquid can be pumped back into the reactor space if this should be necessary.
- the present invention offers a simple and comprehensive system for the decomposition of organic ion exchange resins, and has the following advantages in particular:
- the device is quite simple and space-saving, since it consists essentially of a reactor vessel and a protective jacket, which can be created and maintained with low construction and maintenance costs.
- the process can be extended to other types of hazardous waste, such as combustible, non-radioactive waste, and other nuclear, especially highly toxic, long-lived alpha waste, which is generated in various stages of fuel production.
- hazardous waste such as combustible, non-radioactive waste, and other nuclear, especially highly toxic, long-lived alpha waste, which is generated in various stages of fuel production.
- the process can be adapted and used for energy recovery if appropriate additional technical measures are taken.
- Radioactive substances do not evaporate due to the low operating temperature and therefore they are not spread, which, on the contrary, is a disadvantage of the previously known ashing method.
- the process can be easily controlled by controlling the amount of hydrogen peroxide.
- the device is so simple and small that it can be built on the type of waste generation, which saves extensive handling, storage and an expensive transport of the waste materials there.
Landscapes
- Physics & Mathematics (AREA)
- Engineering & Computer Science (AREA)
- General Engineering & Computer Science (AREA)
- High Energy & Nuclear Physics (AREA)
- Health & Medical Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Toxicology (AREA)
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Business, Economics & Management (AREA)
- Emergency Management (AREA)
- Processing Of Solid Wastes (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE3926252 | 1989-08-09 | ||
DE19893926252 DE3926252A1 (de) | 1989-08-09 | 1989-08-09 | Verfahren und vorrichtung zur zersetzung verbrauchter ionentauscherharze |
Publications (1)
Publication Number | Publication Date |
---|---|
EP0486568A1 true EP0486568A1 (de) | 1992-05-27 |
Family
ID=6386764
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP19900912270 Withdrawn EP0486568A1 (de) | 1989-08-09 | 1990-08-08 | Verfahren und vorrichtung zur zersetzung verbrauchter ionenaustauscherharze |
Country Status (6)
Country | Link |
---|---|
EP (1) | EP0486568A1 (enrdf_load_stackoverflow) |
AU (1) | AU6163990A (enrdf_load_stackoverflow) |
CA (1) | CA2066741A1 (enrdf_load_stackoverflow) |
DE (1) | DE3926252A1 (enrdf_load_stackoverflow) |
EG (1) | EG19766A (enrdf_load_stackoverflow) |
WO (1) | WO1991002362A1 (enrdf_load_stackoverflow) |
Families Citing this family (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE4126971A1 (de) * | 1991-08-14 | 1993-02-18 | Siemens Ag | Verfahren und einrichtung zur entsorgung einer organischen substanz |
DE4137947C2 (de) * | 1991-11-18 | 1996-01-11 | Siemens Ag | Verfahren zur Behandlung von radioaktivem Abfall |
DE19707982A1 (de) * | 1997-02-27 | 1998-09-03 | Siemens Ag | Produkt zur Endlagerung radioaktiv kontaminierter Ionenaustauscherharze |
DE102008005336A1 (de) | 2008-01-17 | 2009-07-30 | Areva Np Gmbh | Verfahren zur Konditionierung radioaktiver Ionenaustauscherharze |
DE102016116575B4 (de) | 2016-05-30 | 2023-12-21 | Samir Basha Eskander | Integriertes System und Verfahren zur Bearbeitung von infektiös belastetem, medizinischem Abfall |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US3669631A (en) * | 1970-01-08 | 1972-06-13 | Us Atomic Energy Commission Th | Removal of materials from ion exchange resins |
JPS59226898A (ja) * | 1983-06-08 | 1984-12-20 | 日揮株式会社 | 放射性有機廃棄物の処理法 |
US4624792A (en) * | 1983-12-12 | 1986-11-25 | Jgc Corporation | Method for treating radioactive organic wastes |
-
1989
- 1989-08-09 DE DE19893926252 patent/DE3926252A1/de active Granted
-
1990
- 1990-08-08 CA CA 2066741 patent/CA2066741A1/en not_active Abandoned
- 1990-08-08 AU AU61639/90A patent/AU6163990A/en not_active Abandoned
- 1990-08-08 WO PCT/EP1990/001299 patent/WO1991002362A1/de not_active Application Discontinuation
- 1990-08-08 EP EP19900912270 patent/EP0486568A1/de not_active Withdrawn
- 1990-08-09 EG EG47190A patent/EG19766A/xx active
Non-Patent Citations (1)
Title |
---|
See references of WO9102362A1 * |
Also Published As
Publication number | Publication date |
---|---|
AU6163990A (en) | 1991-03-11 |
EG19766A (en) | 1996-01-31 |
WO1991002362A1 (de) | 1991-02-21 |
DE3926252A1 (de) | 1991-02-14 |
DE3926252C2 (enrdf_load_stackoverflow) | 1992-07-16 |
CA2066741A1 (en) | 1991-02-10 |
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