WO2007118904A1 - Separation groupee des actinides a partir d'une phase aqueuse fortement acide - Google Patents
Separation groupee des actinides a partir d'une phase aqueuse fortement acide Download PDFInfo
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- WO2007118904A1 WO2007118904A1 PCT/EP2007/053849 EP2007053849W WO2007118904A1 WO 2007118904 A1 WO2007118904 A1 WO 2007118904A1 EP 2007053849 W EP2007053849 W EP 2007053849W WO 2007118904 A1 WO2007118904 A1 WO 2007118904A1
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- G—PHYSICS
- G21—NUCLEAR PHYSICS; NUCLEAR ENGINEERING
- G21C—NUCLEAR REACTORS
- G21C19/00—Arrangements for treating, for handling, or for facilitating the handling of, fuel or other materials which are used within the reactor, e.g. within its pressure vessel
- G21C19/42—Reprocessing of irradiated fuel
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- G—PHYSICS
- G21—NUCLEAR PHYSICS; NUCLEAR ENGINEERING
- G21C—NUCLEAR REACTORS
- G21C19/00—Arrangements for treating, for handling, or for facilitating the handling of, fuel or other materials which are used within the reactor, e.g. within its pressure vessel
- G21C19/42—Reprocessing of irradiated fuel
- G21C19/44—Reprocessing of irradiated fuel of irradiated solid fuel
- G21C19/46—Aqueous processes, e.g. by using organic extraction means, including the regeneration of these means
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- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E30/00—Energy generation of nuclear origin
- Y02E30/30—Nuclear fission reactors
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- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
Definitions
- the present invention relates to a process for separating together all the actinides (III), (IV), (V) and (VI) present in a strongly acidic aqueous phase, fission products, and in particular lanthanides, also finding in this phase, by means of two extractants operating in disjoint chemical domains.
- This process is likely to be used in the field of the reprocessing of irradiated nuclear fuels, in particular for recovering plutonium, neptunium, americium, curium and possibly uranium, in a grouped but selective manner with respect to fission products, from a solution for dissolving an irradiated nuclear fuel, downstream of a uranium extraction cycle.
- the strategy for the reprocessing of irradiated nuclear fuels is based on the PUREX process which makes it possible to separate uranium and plutonium, not only from the other chemical elements present in these fuels, but also from one another, and to purify them.
- a method based on the use of two extractants operating in disjoint chemical domains namely: a first extractant, of malonamide type, which is capable of extracting actinides (III) and lanthanides (III) together from an aqueous phase with a high nitric acidity and a second extractant, of acid type, which is capable of extracting actinides (III) and lanthanides (III) from an aqueous phase with low nitric acidity (Baron P.
- the subject of the present invention is a process for the grouped separation of actinides (III),
- (IV), (V) and (VI) present in a strongly acidic aqueous phase, also containing fission products including lanthanides which process comprises the following steps: a) the coextraction of actinides, lanthanides, yttrium and possibly some other fission products, of the strongly acidic aqueous phase by bringing this phase into contact with an immiscible organic phase, which contains a first extractant capable of extracting these elements from a strongly acidic aqueous phase and a second extractant capable of extracting these same elements from a weakly acidic aqueous phase; and b) the selective desextraction of the actinides from the organic phase by contacting this organic phase with a weakly acidic aqueous phase containing at least one complexing agent.
- strongly acid aqueous phase and “weakly acid aqueous phase” are taken in their usual acceptance in the field of the reprocessing of the irradiated nuclear fuels, namely that a strongly acidic aqueous phase presents generally a pH at most equal to 0, which corresponds, for example, to an aqueous solution of nitric acid of molarity at least equal to 1 M, whereas a weakly acidic aqueous phase generally has a pH strictly greater than 0, which corresponds, for example, to an aqueous solution of nitric acid of molarity strictly less than 1 M.
- the organic phase used in the process according to the invention contains two different extractants: a first extractant whose function is to allow the actinides to be extracted from the strongly acidic aqueous phase when, in step a), this aqueous phase is brought into contact with the organic phase and, to the extent that this extraction is accompanied by that of lanthanides and possibly that of some other fission products such as molybdenum, zirconium, yttrium, ruthenium, palladium, strontium or iron,
- the first extractant is preferably a solvating extractant
- the second extractant is preferably a cation exchanger extractant, also called acid extractant.
- the solvating extractant may especially be chosen from: malonamides such as N, N '-dimethyl-
- N, N'-dibutyltetradecylmalonamide or DMDBTDMA N, N '-dimethyl-N, N' -dioctylhexylethoxymalonamide or DMDOHEMA and N, N '-dimethyl-N, N' -dibutyldodecylmalonamide or DMDBDDEMA
- the trialkylphosphine oxides as trioctylphosphine oxide or TOPO and tributylphosphine oxide or TBPO
- carbamoylphosphine oxides such as diisobutylphenyloctylcarbamoylmethylphosphine oxide or CMPO
- triisobutylphosphine sulfides carbamoylphosphonates, and mixtures thereof.
- the cation exchanger extractant may, in particular, be chosen from:
- Phosphorus-containing acids such as monoalkyl- and dialkylphosphoric acids (for example, di- (2-ethylhexyl) phosphoric acid or HDEHP, dihexylphosphoric acid or HDHP, di- (1, 3- dimethylbutyl) phosphoric acid or HBDMBP and diisodecylphosphoric acid or DIDPA), monoalkyl- and dialkylphosphonic acids (for example, 2-ethylhexyl-ethylhexylphosphonic acid or HEHEHP), monoalkyl- and dialkylphosphinic acids, thiophosphoric acids, thiophosphonic acids thiophosphinic acids, thiophosphorus acids,
- monoalkyl- and dialkylphosphoric acids for example, di- (2-ethylhexyl) phosphoric acid or HDEHP, dihexylphosphoric acid or HDHP, di- (1, 3- dimethylbutyl) phosphoric acid or HBDMBP and
- Sulphonic acids such as dinonylnaphthalene sulphonic acid or HDNNS,
- the organic diluent it can be chosen from all the polar or aliphatic organic diluents whose use has been proposed for carrying out liquid-liquid extractions in the field of the reprocessing of irradiated nuclear fuels such as toluene, xylene t-butylbenzene, triisopropylbenzene, n-dodecane, hydrogenated tetrapropylene or TPH, or kerosene.
- the second extractant is then capable of acting as a phase modifier during step a) and substantially raising the acid value of the strongly acidic aqueous phase. for which demixing (i.e., the appearance of a third phase subsequent to cation saturation of the organic phase) is likely to occur and, thus, the loading capacity of the organic phase.
- step a) the coextraction of certain fission products such as, for example, palladium, as well as that of other undesirable cations, can be advantageously avoided or, at least limited by adding at least one complexing agent to the strongly acidic aqueous phase.
- This complexing agent may in particular be chosen from pyridine polycarboxylic acids
- polyamino carboxylic acids e.g. 2,6-pyridine dicarboxylic acid
- polyamino carboxylic acids e.g. 2,6-pyridine dicarboxylic acid
- polyamino carboxylic acids e.g. 2,6-pyridine dicarboxylic acid
- HEDTA diethylene triamine pentaacetic acid
- DTPA DTPA
- carboxylic acids hydroxycarboxylic acids
- hydrophilic polypyridines dithio-phosphonic acids
- amines C 1 -C 8 alkyl chain grafted polyazines
- hydroxyoximes hydroxyoximes
- sulphonic acids hydroxamic acids and ⁇ - diketones.
- reducing agents capable of reducing neptunium (V) to neptunium (IV) and to stabilize it in this form and to make it more easily extractable.
- reducing agents that may be used, mention may be made in particular of hydrazine derivatives, hydroxylamine derivatives and ferrous sulphamate.
- step b) of the process is carried out using a weakly acidic aqueous phase in which there is at least one complexing agent, which can be chosen from any of the complexing agents mentioned above.
- a weakly acidic aqueous phase in which there is at least one complexing agent, which can be chosen from any of the complexing agents mentioned above.
- it may especially be an aminopolyacetic acid such as HEDTA or DTPA, which is used in combination with an acid capable of acting as a buffer at a pH of 1 to 5, for example a hydroxycarboxylic acid such as glycolic or citric acid, and a base of the soda, hydrazine, amine or carbonate type, such that said aqueous phase has a pH ranging from 1.5 to 4.5 and, more preferably, from 2.5 to 3 5.
- This weakly acidic aqueous phase may, in addition, comprise at least one reducing agent, also for the purpose of reducing neptunium (VI) and to facilitate its removal if a reducing agent has not already been used in step a) .
- the reducing agent is advantageously chosen from hydrazine derivatives, hydroxylamine derivatives, oxime derivatives and hydroxyurea.
- the process comprises, in addition, a step of extracting the lanthanides and yttrium from the organic phase, which it is carried out after step b).
- the organic phase is brought into contact with an acidic aqueous phase, preferably free of any complexing agent such as a dilute nitric acid solution, for example with a molarity ranging from 0.1 to 1, or, on the contrary, concentrated , i.e. of molarity equal to or greater than 4.
- aqueous solution (weakly or strongly) containing a complexing agent such as a polyaminocarboxylic acid, a phosphorus acid, a sulfonic acid or a hydrophilic polyazine. If fission products other than lanthanides and yttrium have also been extracted from the strongly acidic aqueous phase in step a), then the process also includes one or more steps of removing these fission products.
- a complexing agent such as a polyaminocarboxylic acid, a phosphorus acid, a sulfonic acid or a hydrophilic polyazine.
- step a) a step of selectively separating the molybdenum from the organic phase
- the process according to the invention comprises, lastly, a step of purification of the organic phase which is intended to remove impurities and degradation products which accumulated therein during the previous steps.
- This purification step may comprise, as already described in the state of the art, one or more operations for washing the organic phase with aqueous phases containing compounds capable of selectively complexing the impurities and the degradation products it contains. , and to allow, thus, their transfer in these phases without deextracting so far the first and second extractants, and one or more filtration operations if the organic phase contains a precipitate.
- the invention also relates to a process for reprocessing an irradiated nuclear fuel, which comprises the implementation of a group separation process of the actinides (III), (IV), (V) and (VI) such that previously defined, and its use for recovering plutonium, neptunium, americium, curium and possibly uranium, in a grouped but selective manner with respect to fission products from a solution of dissolution of an irradiated nuclear fuel, downstream of a uranium extraction cycle.
- Figure 1 is a block diagram of an exemplary implementation of the method of the invention.
- 1, 2, 3, 4 and 5 show schematically extractors of the type conventionally used in the reprocessing of irradiated nuclear fuels such as, for example, multiple mixer-settler extractors.
- the solvent phase flows in and out of these extractors are symbolized by a double line, while the aqueous phase flows in and out of these extractors are symbolized by a single line.
- Figure 1 schematically illustrates an example of implementation of the method of the invention, designed to separate in a group manner plutonium, neptunium, americium, curium and uranium, possibly present at the same time. trace state, fission products from a solution of dissolution of an irradiated nuclear fuel, after extraction of the uranium it contains.
- This solution is a strongly acidic aqueous solution, for example a solution of nitric acid 2 to 5 M, which contains actinides, lanthanides (lanthanum, cerium, praseodymium, neodymium, samarium, europium, etc.), fission products which are not lanthanides such as yttrium, molybdenum, zirconium, rubidium, ruthenium, rhodium, palladium, strontium and rhodium, and cations that are not fission products such as iron and chromium.
- lanthanides lanthanum, cerium, praseodymium, neodymium, samarium, europium, etc.
- fission products which are not lanthanides such as yttrium, molybdenum, zirconium, rubidium, ruthenium, rhodium, palladium, strontium and rhodium
- the first and second extractants are respectively:
- a malonamide such as N, N '-dimethyl-N, N' -dibutyltetradecylmalonamide (DMDBTDMA) or the
- DMDOHEMA N, N 'dimethyl-N, N' -dioctylhexylethoxymalonamide
- an acid extractant containing phosphorus of the monoalkyl- or dialkylphosphoric acid type such as bis (2-ethylhexyl) phosphoric acid (HDEHP), or of the monoalkyl- or dialkylphosphonic acid type such as 2-ethylhexyl- 2-ethylhexylphosphonic acid (HEHEHP), which is used at a concentration of, for example, 0.3 to 0.6 mol / L.
- the method includes the following steps:
- a step of selective removal of the molybdenum from the organic phase a step of selective extraction of the actinides from the organic phase; a step of desextraction of the lanthanides and yttrium from the organic phase;
- the strongly acidic aqueous solution called "CHARGE” in FIG. 1
- an organic phase immiscible with water, which contains the two extractants mentioned above in an organic diluent, advantageously hydrogenated tetrapropylene.
- This strongly acidic aqueous solution may optionally be supplemented with one or more complexing agents capable of preventing or, at least limiting, the coextraction of certain fission products (palladium for example) or other undesirable cations, as well as one or several reducing agents suitable for reducing neptunium (V) to neptunium (IV) and stabilizing it in this form.
- one or more complexing agents capable of preventing or, at least limiting, the coextraction of certain fission products (palladium for example) or other undesirable cations, as well as one or several reducing agents suitable for reducing neptunium (V) to neptunium (IV) and stabilizing it in this form.
- the complexing agent (s) may especially be chosen from pyridine-polycarboxylic acids such as 2,6-pyridine dicarboxylic acid, which is used at a concentration of, for example, 0.3 mol / L, and polyamino acids.
- carboxylic acids such as N- (2-hydroxyethyl) ethylene diamine triacetic acid (HEDTA) or diethylene triamine pentaacetic acid (DTPA), which is used at a concentration of, for example, 0.01 mol / L.
- HEDTA N- (2-hydroxyethyl) ethylene diamine triacetic acid
- DTPA diethylene triamine pentaacetic acid
- they can also be selected from the acids carboxylic acids, hydroxycarboxylic acids, amines, polyazines, hydroxyoximes, sulfonic acids, hydroxamic acids and ⁇ -diketones.
- the reducing agent (s) may, in turn, be chosen from hydrazine nitrates,
- the first step also comprises washing operations of the organic phase, which can be carried out, as is well known in the state of the art, by bringing this organic phase into contact with various aqueous acid solutions, for example a first solution of nitric acid at 2.8 mol / L and HEDTA at 0.015 mol / L, and a second solution of nitric acid at 0.5 mol / L.
- various aqueous acid solutions for example a first solution of nitric acid at 2.8 mol / L and HEDTA at 0.015 mol / L, and a second solution of nitric acid at 0.5 mol / L.
- an aqueous phase which contains the fission products (PF) which can not be extracted by the organic phase, and on the other hand an organic phase in which find plutonium, neptunium, americium, curium, any traces of uranium, lanthanides, yttrium, molybdenum, zirconium and iron.
- PF fission products
- the organic phase is contacted countercurrently with a weakly acidic aqueous solution and containing one or more compounds capable of selectively complexing molybdenum at a pH equal to or greater than 1.
- a weakly acidic aqueous solution is, for example, a 0.5 mol / L citric acid solution. neutralized at a pH of about 3 by a base such as sodium hydroxide.
- the organic phase is brought into contact, against the current, with a weakly acidic aqueous solution and containing one or more compounds capable of selectively complexing the actinides at a pH equal to or greater than 1
- a weakly acidic aqueous solution and containing one or more compounds capable of selectively complexing the actinides at a pH equal to or greater than 1
- Such a solution is, for example, a solution of 0.5 mol / L citric acid and 0.01 mol / L diethylene triamine pentaacetic acid (DTPA), of pH 3.
- DTPA diethylene triamine pentaacetic acid
- an aqueous phase is obtained in which are the plutonium, neptunium, americium, curium and any traces of uranium, and an organic phase freed of these elements.
- the organic phase is brought into contact, against the current, with an acidic aqueous solution whose acidity is in a pH range in which the extracting power of the organic phase is minimal with respect to lanthanides and yttrium.
- an acidic aqueous solution whose acidity is in a pH range in which the extracting power of the organic phase is minimal with respect to lanthanides and yttrium.
- Such a solution is, for example, a 0.5-1 mol / L nitric acid solution.
- the organic phase is brought into contact, against the current, with a weakly acidic aqueous solution and containing one or more agents capable of selectively complexing zirconium and iron at a pH greater than 0.
- a weakly acidic aqueous solution and containing one or more agents capable of selectively complexing zirconium and iron at a pH greater than 0.
- Such a solution is, for example, a solution of 1 M nitric acid and 0.8 M oxalic acid, pH 0.
- the organic phase is purified, for example by one or more washings with an aqueous solution of a strong base, with a pH equal to or greater than 8, such as a solution of sodium carbonate or of sodium hydroxide (0.1 - 0.3 mol / l) and, incidentally by one or more filtrations in the case where it contains a precipitate.
- a strong base with a pH equal to or greater than 8
- a solution of sodium carbonate or of sodium hydroxide 0.1 - 0.3 mol / l
- the organic phase can be reused for the implementation of a next cycle.
- This step has been validated experimentally using: an organic phase containing 0.6 mol / l of DMDOHEMA as solvating extractant, and 0.3 mol / l of HDEHP as acid extractant in TPH; and * four aqueous phases consisting of 3M aqueous nitric solutions (which corresponds to the standard acidity of a solution for dissolving an irradiated nuclear fuel) and containing for the first: uranium (VI), for the second: neptunium (VI), for the third: neptunium (V) and plutonium (IV), and for the fourth: neptunium (IV), plutonium (III), americium (III) and curium (III) as actinides, and cerium (III) and europium (III) as lanthanides.
- 3M aqueous nitric solutions which corresponds to the standard acidity of a solution for dissolving an irradiated nuclear fuel
- uranium (VI) for
- the organic phase previously equilibrated in acid with 3M nitric acid, was brought into contact with each of the aqueous phases strictly under the same conditions, namely: 1 volume of organic phase for 1 volume of aqueous phase, stirring during 1 hour at 25 ° C.
- the distribution coefficient D M of an element M corresponds to the ratio between the activity or the concentration of this element in the organic phase and the activity or the concentration of this same element in the aqueous phase.
- the activities of plutonium, neptunium and curium were measured by ⁇ spectrometry.
- the activities of americium, cerium and europium were measured by ⁇ -spectrometry, while uranium concentrations were determined by fluorescence.
- Table I shows the distribution coefficients D M as obtained for the different elements initially present in the aqueous phases.
- uranium (VI), neptunium (IV) and plutonium (III and IV) were very strongly extracted by this mixture.
- Neptunium (V) which is generally very little extracted by most solvent extractants, has a distribution coefficient above 7 after 1 hour of agitation.
- a spectrophotometric study has shown that Np (V) dismutes and is extracted in the Np (IV) and Np (VI) form by the DMDOHEMA / HDEHP mixture.
- an increase in the nitric acid content of the aqueous phase, from 3 to 3.8 mol / L has a very favorable effect on the extraction of Np (V) since its coefficient
- the distribution range then increases from 7 to 32.
- the loading capacity of the DMDOHEMA / HDEHP mixture at 0.60 mol / L and 0.3 mol / L, respectively, in TPH was also evaluated at this stage, in the case of cerium.
- the organic phase was contacted several times with an aqueous phase consisting of a 3M nitric acid solution and containing 0.14 mol / L of cerium, by varying the ratio between the volumes of the aqueous phase and the organic phase from 1 to 4. No demixtion was observed even for amounts of cerium present in the organic phase of 0.11 mol / L.
- the loading capacity of the DMDOHEMA / HDEHP mixture is sufficient to tolerate actinide concentrations and lanthanides present in the dissolution solutions of future nuclear fuels.
- the demixing limit vis-à-vis the acidity of the aqueous phase was also evaluated using an organic phase containing 0.5 mol / L of DMDOHEMA and 0.3 mol / L of HDEHP in TPH. This experiment made it possible to show that HDEHP makes it possible to strongly push back the demixing limit in the presence of high concentrations of HNO 3 in the aqueous phase since this demixing occurs for HNO 3 concentrations greater than 7.5 M
- the acid extractant represented here by the HDEHP, therefore has phase-modifying properties at the actinide and lanthanide co-extraction step, which is carried out with high nitric acidity and in which the predominant extractant is the solvating extractant. , represented by DMDOHEMA.
- an aqueous phase consisting of a 0.5 mol / l citric acid solution neutralized to pH 3 with sodium hydroxide.
- the aqueous phase was brought into contact with each of the organic phases under exactly the same conditions, namely: 5 volumes of aqueous phase per 1 volume of organic phase, stirring for 15 minutes at 25 ° C. After decantation and separation of the organic and aqueous phases, the activities or concentrations of the various elements were measured in the two phases, organic and aqueous, in order to determine their distribution coefficients D M.
- DMDOHEMA / HDEHP was also determined at this stage in the case of cerium.
- an organic phase containing 0.6 mol / l of DMDOHEMA and 0.3 mol / l of HDEHP in TPH, and 0.11 mol / l of cerium extract at an acidity of the aqueous phase of 3 mol. / L was brought into contact with an aqueous phase consisting of a solution of 0.5 M citric acid, pH 3 and containing 0.45 mol / L of tetramethylammonium hydroxide to neutralize the acidity nitric acid which tends to be extracted at this stage. No demixing was observed.
- the amount of cerium extracted by the organic phase has exceeded 0.06 mol / L, which is sufficient to extract actinides and lanthanides (the molybdenum passing in the aqueous phase).
- This aqueous phase was brought into contact with each of the organic phases strictly under the same conditions, namely: 1 volume of aqueous phase for 1 volume of organic phase, stirring for 1 hour at 25 ° C.
- the activities or the concentrations of the different elements were measured in the two phases, organic and aqueous, in order to determine their distribution coefficients D M , then the separation factors FS EU / A ⁇ and FS Ce / An-
- the separation factor between two elements M1 and M2, denoted FS M I / M2, is defined as being the ratio between the distribution coefficients, respectively D M i and D M2 , of these two elements. It is considered that the separation between the two elements M1 and M2 is satisfactory when the separation factor FS M i / M2 is greater than 10.
- Table III shows the distribution coefficients D M as obtained for the different elements, as well as the separation factors FS EU / A ⁇ and FS Ce / An.
- the lanthanides and yttrium can be quantitatively extracted from the organic phase by contacting with an aqueous phase consisting of a 0.5-1 mol / L nitric acid solution, a field of acidity in which the extractant DMDOHEMA / HDEHP is minimal to these elements.
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Priority Applications (5)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US12/297,651 US8557120B2 (en) | 2006-04-19 | 2007-04-19 | Grouped separation of actinides from a strongly acidic aqueous phase |
| EP07728308A EP2008284A1 (fr) | 2006-04-19 | 2007-04-19 | Separation groupee des actinides a partir d'une phase aqueuse fortement acide |
| CN2007800230073A CN101479808B (zh) | 2006-04-19 | 2007-04-19 | 从强酸性水相中分离锕系族元素 |
| JP2009505895A JP5174806B2 (ja) | 2006-04-19 | 2007-04-19 | 強酸性水相からのアクチニド類の群分離 |
| KR1020087028076A KR101475336B1 (ko) | 2006-04-19 | 2008-11-17 | 강산성 수상으로부터 악티니드류의 그룹화된 분리 |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| FR0651376 | 2006-04-19 | ||
| FR0651376A FR2900159B1 (fr) | 2006-04-19 | 2006-04-19 | Separation groupee des actinides a partir d'une phase aqueuse fortement acide |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2007118904A1 true WO2007118904A1 (fr) | 2007-10-25 |
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/EP2007/053849 Ceased WO2007118904A1 (fr) | 2006-04-19 | 2007-04-19 | Separation groupee des actinides a partir d'une phase aqueuse fortement acide |
Country Status (9)
| Country | Link |
|---|---|
| US (1) | US8557120B2 (fr) |
| EP (1) | EP2008284A1 (fr) |
| JP (1) | JP5174806B2 (fr) |
| KR (1) | KR101475336B1 (fr) |
| CN (1) | CN101479808B (fr) |
| FR (1) | FR2900159B1 (fr) |
| RU (1) | RU2438200C2 (fr) |
| WO (1) | WO2007118904A1 (fr) |
| ZA (1) | ZA200808626B (fr) |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| WO2011009814A1 (fr) | 2009-07-21 | 2011-01-27 | Commissariat à l'énergie atomique et aux énergies alternatives | Composes utiles comme ligands des actinides, leur synthese et leurs utilisations |
| FR2954354A1 (fr) * | 2009-12-22 | 2011-06-24 | Commissariat Energie Atomique | Procede de purification de l'uranium d'un concentre d'uranium naturel |
| CN102473467A (zh) * | 2009-07-02 | 2012-05-23 | 阿海珐核循环公司 | 用于处理废弃核燃料的改进方法 |
| WO2012130902A1 (fr) | 2011-04-01 | 2012-10-04 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | Derives de la 2,9-dipyridyl-1,10-phenanthroline utiles comme ligands des actinides, leur procede de synthese et leurs utilisations |
| JP2013500485A (ja) * | 2009-07-27 | 2013-01-07 | コミッサリア ア レネルジー アトミーク エ オ ゼネルジ ザルタナテイヴ | 硝酸水相から選択的にアメリシウムを回収する方法 |
| CN106148696A (zh) * | 2016-07-08 | 2016-11-23 | 广东省稀有金属研究所 | 一种从氯化镧溶液中除放射性的方法 |
| WO2017067933A1 (fr) * | 2015-10-21 | 2017-04-27 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | Utilisation d'aldoximes comprenant au moins cinq atomes de carbone comme agents anti-nitreux dans des opérations de désextraction réductrice du plutonium |
| EP4290532A3 (fr) * | 2016-09-29 | 2024-03-20 | The Regents of the University of California | Séparation d'ions métalliques par extraction liquide-liquide |
| US12268678B2 (en) | 2016-09-06 | 2025-04-08 | The Regents Of The University Of California | Formulations of hydroxypyridonate actinide/lanthanide decorporation agents |
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| MY164109A (en) * | 2011-06-27 | 2017-11-30 | Shinetsu Chemical Co | Method for extracting and separating light rare earth element |
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| US10982136B2 (en) | 2016-02-26 | 2021-04-20 | The Regents Of The University Of California | Ligand-sensitized lanthanide nanocrystals as ultraviolet downconverters |
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| WO2018044812A2 (fr) | 2016-08-29 | 2018-03-08 | Fred Hutchinson Cancer Research Center | Plate-forme de chélation pour l'administration de radionucléides |
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| FR2845616A1 (fr) * | 2002-10-15 | 2004-04-16 | Commissariat Energie Atomique | Procede cyclique de separation d'elements chimiques presents dans une solution aqueuse |
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| CN102473467B (zh) * | 2009-07-02 | 2014-10-15 | 阿海珐核循环公司 | 用于处理废弃核燃料的改进方法 |
| CN102473467A (zh) * | 2009-07-02 | 2012-05-23 | 阿海珐核循环公司 | 用于处理废弃核燃料的改进方法 |
| WO2011009814A1 (fr) | 2009-07-21 | 2011-01-27 | Commissariat à l'énergie atomique et aux énergies alternatives | Composes utiles comme ligands des actinides, leur synthese et leurs utilisations |
| US8709129B2 (en) | 2009-07-21 | 2014-04-29 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | Compounds useful as ligands of actinides, their synthesis and their uses |
| JP2013500485A (ja) * | 2009-07-27 | 2013-01-07 | コミッサリア ア レネルジー アトミーク エ オ ゼネルジ ザルタナテイヴ | 硝酸水相から選択的にアメリシウムを回収する方法 |
| FR2954354A1 (fr) * | 2009-12-22 | 2011-06-24 | Commissariat Energie Atomique | Procede de purification de l'uranium d'un concentre d'uranium naturel |
| WO2011076739A1 (fr) * | 2009-12-22 | 2011-06-30 | Commissariat à l'énergie atomique et aux énergies alternatives | Procede d'extraction liquide - liquide pour la purification de l'uranium issu de la dissolution nitrique d'un concentre d'uranium naturel |
| GB2488089A (en) * | 2009-12-22 | 2012-08-15 | Commissariat A L A Nergie Atomique Et Aux A Nergies Alternatives | Liquid/liquid extraction method for purifying uranium from nitric acid dissolution of natural uranium concentrate |
| GB2488089B (en) * | 2009-12-22 | 2013-02-27 | Commissariat A L A Nergie Atomique Et Aux A Nergies Alternatives | A method for purifying the uranium from a natural uranium concentrate |
| US8795611B2 (en) | 2009-12-22 | 2014-08-05 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | Method for purifying the uranium from a natural uranium concentrate |
| WO2012130902A1 (fr) | 2011-04-01 | 2012-10-04 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | Derives de la 2,9-dipyridyl-1,10-phenanthroline utiles comme ligands des actinides, leur procede de synthese et leurs utilisations |
| US9074266B2 (en) | 2011-04-01 | 2015-07-07 | Commissariat à l'énergie atomique et aux énergies alternatives | 2,9-dipyridyl-1,10-phenanthroline derivatives useful as actinide ligands, method for synthesizing same, and uses thereof |
| WO2017067933A1 (fr) * | 2015-10-21 | 2017-04-27 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | Utilisation d'aldoximes comprenant au moins cinq atomes de carbone comme agents anti-nitreux dans des opérations de désextraction réductrice du plutonium |
| FR3042904A1 (fr) * | 2015-10-21 | 2017-04-28 | Commissariat Energie Atomique | Utilisation d'aldoximes comprenant au moins cinq atomes de carbone comme agents anti-nitreux dans des operations de desextraction reductrice du plutonium |
| CN108369828A (zh) * | 2015-10-21 | 2018-08-03 | 原子能和替代能源委员会 | 含至少五个碳原子的醛肟在钚还原反萃取操作中作为抗亚硝酸化剂的应用 |
| RU2718437C2 (ru) * | 2015-10-21 | 2020-04-06 | Коммиссариат А Л' Энержи Атомик Э Оз Энержи Альтернатив | Применение альдоксимов, содержащих по меньшей мере пять атомов углерода, в качестве агентов противоазотистого действия в операциях восстановительной реэкстракции плутония |
| CN108369828B (zh) * | 2015-10-21 | 2022-05-24 | 原子能和替代能源委员会 | 含至少五个碳原子的醛肟在钚还原反萃取操作中作为抗亚硝酸化剂的应用 |
| CN106148696A (zh) * | 2016-07-08 | 2016-11-23 | 广东省稀有金属研究所 | 一种从氯化镧溶液中除放射性的方法 |
| US12268678B2 (en) | 2016-09-06 | 2025-04-08 | The Regents Of The University Of California | Formulations of hydroxypyridonate actinide/lanthanide decorporation agents |
| EP4290532A3 (fr) * | 2016-09-29 | 2024-03-20 | The Regents of the University of California | Séparation d'ions métalliques par extraction liquide-liquide |
| US12002595B2 (en) | 2016-09-29 | 2024-06-04 | The Regents Of The University Of California | Separation of metal ions by liquid-liquid extraction |
| US12479792B2 (en) | 2016-09-29 | 2025-11-25 | The Regents Of The University Of California | Compositions of chelating molecules |
Also Published As
| Publication number | Publication date |
|---|---|
| KR101475336B1 (ko) | 2014-12-22 |
| RU2008145593A (ru) | 2010-05-27 |
| FR2900159B1 (fr) | 2008-06-13 |
| EP2008284A1 (fr) | 2008-12-31 |
| KR20090007758A (ko) | 2009-01-20 |
| FR2900159A1 (fr) | 2007-10-26 |
| US8557120B2 (en) | 2013-10-15 |
| ZA200808626B (en) | 2009-11-25 |
| US20090184051A1 (en) | 2009-07-23 |
| CN101479808A (zh) | 2009-07-08 |
| JP5174806B2 (ja) | 2013-04-03 |
| CN101479808B (zh) | 2012-09-05 |
| RU2438200C2 (ru) | 2011-12-27 |
| JP2009534639A (ja) | 2009-09-24 |
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