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JP4451966B2 - Cleaning method of organic solvent for spent nuclear fuel reprocessing - Google Patents
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JP4451966B2 - Cleaning method of organic solvent for spent nuclear fuel reprocessing - Google Patents

Cleaning method of organic solvent for spent nuclear fuel reprocessing Download PDF

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Publication number
JP4451966B2
JP4451966B2 JP2000184780A JP2000184780A JP4451966B2 JP 4451966 B2 JP4451966 B2 JP 4451966B2 JP 2000184780 A JP2000184780 A JP 2000184780A JP 2000184780 A JP2000184780 A JP 2000184780A JP 4451966 B2 JP4451966 B2 JP 4451966B2
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Prior art keywords
organic solvent
dissolved
spent
solvent
carbon dioxide
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JP2002006079A (en
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隆 島田
安弘 石田
信哉 小雲
伸夫 石原
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Mitsubishi Heavy Industries Ltd
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Mitsubishi Heavy Industries Ltd
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E30/00Energy generation of nuclear origin
    • Y02E30/30Nuclear fission reactors
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/54Improvements relating to the production of bulk chemicals using solvents, e.g. supercritical solvents or ionic liquids
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies

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Description

【0001】
【発明の属する技術分野】
本発明は、有機溶媒の洗浄再生方法に関し、特に使用済核燃料の再処理に使用される有機溶媒の洗浄方法に関する。
【0002】
【従来の技術】
軽水冷却型原子炉は現在広く使用されているが、その使用済燃料の再処理は、一般にピューレックス法で行われ、硝酸水溶液を用いて使用済燃料の細片を溶かす。硝酸水溶液に溶かされたウランやプルトニウムなどの有用物は、有機溶媒を用いて抽出され、再使用のため回収される。有機溶媒としては、例えばリン酸トリブチル(TBP)を溶かした炭化水素混合物が使用される。このような有機溶媒は一般に再生して循環使用されるが、前述のウランの抽出時等において、加水分解、放射線分解が生じ、これによる分解生成物を含んでいる。このような分解生成物は再処理工程において、ウラン、プルトニウムの回収率の低下、除染係数の低下、クラッド、エマルジョンの生成など、悪影響を及ぼすので例えば図5に示すように処理され、再生された有機溶媒が再使用される。即ち、図において、使用済燃料の再処理工程1から排出された使用済有機溶媒3に洗浄水溶液5a、5bを接触させ、分解生成物(以下劣化溶媒という。)を洗浄水溶液5a、5bに溶解させて廃液9a、9bとして分離する。再生有機溶媒11は、使用済燃料の再処理工程1へ戻されて使用される。洗浄水溶液5a、5bとしては、炭酸ナトリウム水溶液、水酸化ナトリウム水溶液などのアルカリ洗浄液ゃ、シュウ酸ヒドラジン水溶液、炭酸ヒドラジン水溶液などのソルトフリー試薬などが使用される。
【0003】
【発明が解決しようとする課題】
以上のように、使用済核燃料再処理工程において、有機溶媒中に生成される劣化溶媒は、種々あるためこれを洗浄水溶液を用いて除去しようとすると、そのための抽出操作が4回も必要となる。このため、処理操作が煩雑になると共に抽出器も4個必要となって装置も大型になるから、有機溶媒の洗浄処理コストも大きなものであった。
従って、本発明の課題は、処理操作も簡単で、シンプルな設備でも実施できる使用済核燃料再処理用有機溶媒の洗浄方法を提供することである。
【0004】
【課題を解決するための手段】
前述の課題を解決するため、本発明の使用済核燃料再処理用有機溶媒の洗浄方法によれば、使用済核燃料再処理工程の抽出に使用された劣化溶媒含有使用済有機溶媒から劣化溶媒を分離するため、有機溶媒を選択溶解する二酸化炭素などの超臨界流体を使用する。即ち、本発明の一態様において、劣化溶媒含有使用済有機溶媒に超臨界流体を接触させて該使用済有機溶媒を該超臨界流体に溶解させ、該使用済有機溶媒を溶解した該超臨界流体洗浄水溶液向流接触させて劣化溶媒を洗浄水溶液に溶解させかつ有機溶媒を超臨界二酸化炭素に溶解された儘とし、劣化溶媒を含む前記水溶液を廃液として分離し、しかる後前記有機溶媒を溶解した前記超臨界流体に減圧分離操作を施して超臨界流体と有機溶媒とに分離する。分離された有機溶媒は再生されたもので、使用済核燃料再処理工程の抽出に再使用できる。
【0005】
【発明の実施の形態】
以下、添付の図面を参照して本発明の実施形態を説明する。尚、従来の技術に関する図面を含め、全図にわたり同一部分(物質、工程など)には、同一の符号を付している。
図1を参照するに、使用済燃料の再処理工程1から出た使用済有機溶媒3に、洗浄水溶液21を加えて混合23する。この混合により、使用済有機溶媒3中の劣化溶媒は洗浄水溶液に溶け、有機溶媒と劣化溶媒を溶解した水溶液との混合液25が得られる。次に、混合液25に超臨界状態(圧力12〜20MPa、温度40〜60℃)のCO2(以下超臨界二酸化炭素という。)27を作用させ、有機溶媒を超臨界二酸化炭素に溶解29させる。この有機溶媒の溶解29により、劣化溶媒を溶解した水溶液は廃液31として分離される。有機溶媒を溶解した超臨界二酸化炭素33は次いで減圧分離操作35により10MPa以下の圧力に減圧され、有機溶媒は析出し、二酸化炭素37と再生有機溶媒11とに分離される。再生有機溶媒11は、図示されるように使用済燃料の再処理工程1に戻されて再使用され、又図示されていないが二酸化炭素37は再圧縮され、超臨界流体状態の超臨界二酸化炭素27に戻される。尚、前記実施形態においては、超臨界流体として二酸化炭素を用いたが、これに限定されるものではなく他の超臨界流体を用いても良い。
【0006】
図2には、前述の工程を持つ有機溶媒洗浄再生方法を実施する設備の系統図が示されている。反応槽41は、使用済有機溶媒3と洗浄水溶液21を受け入れ、これらを混合すると共に超臨界二酸化炭素27を受け入れる。反応槽41は又、液体状態の廃液31をしかるべき設備に排出すると共に有機溶媒を溶解した超臨界二酸化炭素33を減圧弁47を介してブレークベッセル43へ送る。そして、低圧のブレークベッセル43内において、再生有機溶媒11と気体又は液体の二酸化炭素37とに分離される。二酸化炭素37は貯槽45に戻され、再使用される。
【0007】
次に、本発明の別の実施形態を図3を参照して説明する。図3を参照するに、使用済燃料の再処理工程1から前記実施形態と同様に出た使用済有機溶媒3に、超臨界状態(圧力12〜20MPa、温度40〜60℃)の超臨界二酸化炭素27を作用させ、使用済有機溶媒3を超臨界二酸化炭素に溶解51させる。使用済有機溶媒3を溶解した超臨界二酸化炭素53に更に洗浄水溶液21を混合55する。この混合55により、使用済有機溶媒3中の劣化溶媒は洗浄水溶液21に溶け、劣化溶媒を溶解した水溶液からなる廃液57が分離される。このようにして得られた、有機溶媒を溶解した超臨界二酸化炭素33は、次いで減圧分離操作35により10MPa以下の圧力に減圧され、有機溶媒は析出し、二酸化炭素37と再生有機溶媒11とに分離される。再生有機溶媒11と二酸化炭素37は、その後、前述の実施形態と同様に処理される。尚、本実施形態においても、二酸化炭素以外の超臨界流体が使用できる。
【0008】
図4には、前述の第2の実施形態として説明された有機溶媒洗浄再生方法を実施する設備の系統図が示されている。反応槽61は使用済有機溶媒(劣化溶媒含有)3を受け入れ、これに超臨界二酸化炭素27を作用させて溶解する。使用済有機溶媒3を溶解した超臨界二酸化炭素53は更に反応槽63に送られ、ここで超臨界二酸化炭素53と洗浄水溶液2とが向流接触される。この向流接触により、劣化溶媒は洗浄水溶液2に溶解し、有機溶媒は超臨界二酸化炭素に溶解された儘となる。劣化溶媒含有洗浄水溶液2は、廃液57として分離して取り出され、又有機溶媒を溶解した超臨界二酸化炭素33は減圧弁47を介してブレークベッセル43へ送られる。その後の処理は図2の場合と同様である。
【0009】
【発明の効果】
以上説明したように、本発明によれば、リン酸トリブチル、n−ドデカンなどの有機溶媒は溶解するが水溶液は溶解しないという選択溶解性を有する超臨界流体を使用するので、劣化溶媒の分離洗浄が単純になると共に超臨界流体は再使用が可能であるので、廃液処理量が減少し、コストが低減できる。
【図面の簡単な説明】
【図1】本発明の実施形態を示す工程図である。
【図2】前記実施形態に係る方法を実施するための設備の系統図である。
【図3】本発明の別の実施形態を示す工程図である。
【図4】前記別の実施形態に係る方法を実施するための設備の系統図である。
【図5】従来の方法を示す工程図である。
【符号の説明】
1 使用済燃料の再処理工程
3 使用済有機溶媒
11 再生有機溶媒
21 洗浄水溶液
23 混合
25 混合液
27 超臨界二酸化炭素
31 廃液
33 有機溶媒を溶解した超臨界二酸化炭素
35 減圧・分離操作
37 二酸化炭素
41 反応槽
43 ブレークベッセル
45 貯槽
47 減圧弁
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for cleaning and regenerating an organic solvent, and more particularly to a method for cleaning an organic solvent used for reprocessing spent nuclear fuel.
[0002]
[Prior art]
Light water-cooled nuclear reactors are currently widely used, but reprocessing of spent fuel is generally performed by the Purex method, and nitric acid aqueous solution is used to dissolve spent fuel debris. Useful substances such as uranium and plutonium dissolved in an aqueous nitric acid solution are extracted using an organic solvent and recovered for reuse. As the organic solvent, for example, a hydrocarbon mixture in which tributyl phosphate (TBP) is dissolved is used. Such an organic solvent is generally regenerated and recycled, but hydrolysis and radiolysis occur at the time of extraction of uranium as described above, and contain decomposition products. Such decomposition products are adversely affected in the reprocessing step, such as a decrease in the recovery rate of uranium and plutonium, a decrease in the decontamination coefficient, cladding, and the formation of emulsions. Organic solvent is reused. That is, in the figure, cleaning aqueous solutions 5a and 5b are brought into contact with the spent organic solvent 3 discharged from the spent fuel reprocessing step 1, and decomposition products (hereinafter referred to as deteriorated solvents) are dissolved in the cleaning aqueous solutions 5a and 5b. And separated as waste liquids 9a and 9b. The recycled organic solvent 11 is returned to the spent fuel reprocessing step 1 for use. As the cleaning aqueous solutions 5a and 5b, an alkaline cleaning solution such as a sodium carbonate aqueous solution or a sodium hydroxide aqueous solution, or a salt-free reagent such as an oxalic acid hydrazine aqueous solution or a carbonate hydrazine aqueous solution is used.
[0003]
[Problems to be solved by the invention]
As described above, in the spent nuclear fuel reprocessing step, there are various kinds of deteriorated solvents generated in the organic solvent. Therefore, if it is attempted to remove these using a cleaning aqueous solution, four extraction operations are required. . For this reason, the processing operation becomes complicated, and four extractors are required, which increases the size of the apparatus, resulting in a high cost for cleaning the organic solvent.
Accordingly, an object of the present invention is to provide a method for cleaning an organic solvent for spent nuclear fuel reprocessing which can be carried out with a simple facility and with a simple processing operation.
[0004]
[Means for Solving the Problems]
In order to solve the above-described problems, according to the cleaning method for spent nuclear fuel reprocessing organic solvent of the present invention, the degraded solvent is separated from the spent organic solvent-containing spent organic solvent used in the extraction of the spent nuclear fuel reprocessing step. Therefore, a supercritical fluid such as carbon dioxide that selectively dissolves an organic solvent is used. That is, in one embodiment of the present invention, the deterioration solvent-containing spent organic solvent by contacting the supercritical fluid dissolving the spent organic solvent for said use the supercritical fluid, the supercritical dissolving the spent organic solvent for said use and dissolved in fluid and cleaning solution to the cleaning solution deterioration solvent was countercurrent contact with the organic solvent and as one likes dissolved in supercritical carbon dioxide, separating the aqueous solution containing the deterioration solvent as waste, after which the organic The supercritical fluid in which the solvent is dissolved is subjected to a vacuum separation operation to separate it into a supercritical fluid and an organic solvent. The separated organic solvent has been regenerated and can be reused for extraction in the spent nuclear fuel reprocessing step.
[0005]
DETAILED DESCRIPTION OF THE INVENTION
Embodiments of the present invention will be described below with reference to the accompanying drawings. In addition, the same code | symbol is attached | subjected to the same part (substance, a process, etc.) over all drawings including drawing regarding a prior art.
Referring to FIG. 1, a cleaning aqueous solution 21 is added to and mixed 23 with the spent organic solvent 3 that has been output from the spent fuel reprocessing step 1. By this mixing, the deteriorated solvent in the used organic solvent 3 is dissolved in the cleaning aqueous solution, and a mixed solution 25 of the organic solvent and the aqueous solution in which the deteriorated solvent is dissolved is obtained. Next, CO 2 (hereinafter referred to as supercritical carbon dioxide) 27 in a supercritical state (pressure 12 to 20 MPa, temperature 40 to 60 ° C.) is allowed to act on the mixed solution 25 to dissolve the organic solvent 29 in the supercritical carbon dioxide 29. . Due to the dissolution 29 of the organic solvent, the aqueous solution in which the deteriorated solvent is dissolved is separated as the waste liquid 31. The supercritical carbon dioxide 33 in which the organic solvent is dissolved is then depressurized to a pressure of 10 MPa or less by the vacuum separation operation 35, and the organic solvent is precipitated and separated into the carbon dioxide 37 and the regenerated organic solvent 11. As shown in the figure, the regenerated organic solvent 11 is returned to the spent fuel reprocessing step 1 to be reused, and although not shown, the carbon dioxide 37 is recompressed to form supercritical carbon dioxide in a supercritical fluid state. Returned to 27. In the above embodiment, carbon dioxide is used as the supercritical fluid. However, the present invention is not limited to this, and other supercritical fluid may be used.
[0006]
FIG. 2 shows a system diagram of equipment for carrying out the organic solvent cleaning and regeneration method having the above-described steps. The reaction tank 41 receives the used organic solvent 3 and the cleaning aqueous solution 21, mixes them, and receives supercritical carbon dioxide 27. The reaction tank 41 also discharges the liquid waste liquid 31 to an appropriate facility and sends the supercritical carbon dioxide 33 in which the organic solvent is dissolved to the break vessel 43 through the pressure reducing valve 47. Then, in the low-pressure break vessel 43, the regenerated organic solvent 11 and the gas or liquid carbon dioxide 37 are separated. The carbon dioxide 37 is returned to the storage tank 45 and reused.
[0007]
Next, another embodiment of the present invention will be described with reference to FIG. Referring to FIG. 3, the spent organic solvent 3 produced in the same manner as in the above embodiment from the spent fuel reprocessing step 1 is supercritical (pressure 12-20 MPa, temperature 40-60 ° C.). Carbon 27 is allowed to act to dissolve 51 the used organic solvent 3 in supercritical carbon dioxide. The cleaning aqueous solution 21 is further mixed 55 with the supercritical carbon dioxide 53 in which the used organic solvent 3 is dissolved. By this mixing 55, the deteriorated solvent in the used organic solvent 3 is dissolved in the cleaning aqueous solution 21, and the waste liquid 57 composed of the aqueous solution in which the deteriorated solvent is dissolved is separated. The supercritical carbon dioxide 33 obtained by dissolving the organic solvent thus obtained is then depressurized to a pressure of 10 MPa or less by the vacuum separation operation 35, the organic solvent is precipitated, and the carbon dioxide 37 and the regenerated organic solvent 11 are separated. To be separated. The regenerated organic solvent 11 and the carbon dioxide 37 are then treated in the same manner as in the previous embodiment. In this embodiment, a supercritical fluid other than carbon dioxide can be used.
[0008]
FIG. 4 shows a system diagram of equipment for carrying out the organic solvent cleaning and regeneration method described as the second embodiment. The reaction tank 61 receives the used organic solvent (containing a deteriorated solvent) 3, and supercritical carbon dioxide 27 acts on this to dissolve it. Spent organic solvent 3 supercritical carbon dioxide 53 which was dissolved is fed further into the reaction vessel 63, where it is contacted with supercritical carbon dioxide 53 washing solution 2 1 TogaMuko stream. The countercurrent contacting, degradation solvent dissolves in the cleaning solution 2 1, the organic solvent becomes as one likes dissolved in supercritical carbon dioxide. Degradation solvent-containing cleaning solution 2 1 is taken in isolation as waste 57, also supercritical carbon dioxide 33 dissolved organic solvent is fed to break the vessel 43 through a pressure reducing valve 47. The subsequent processing is the same as in FIG.
[0009]
【The invention's effect】
As described above, according to the present invention, a supercritical fluid having selective solubility in which an organic solvent such as tributyl phosphate and n-dodecane is dissolved but an aqueous solution is not dissolved is used. However, since the supercritical fluid can be reused, the amount of waste liquid treated can be reduced and the cost can be reduced.
[Brief description of the drawings]
FIG. 1 is a process diagram showing an embodiment of the present invention.
FIG. 2 is a system diagram of equipment for carrying out the method according to the embodiment.
FIG. 3 is a process diagram showing another embodiment of the present invention.
FIG. 4 is a system diagram of equipment for carrying out the method according to another embodiment.
FIG. 5 is a process diagram showing a conventional method.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Reprocessing process of spent fuel 3 Used organic solvent 11 Recycled organic solvent 21 Washing aqueous solution 23 Mixture 25 Mixture 27 Supercritical carbon dioxide 31 Waste liquid 33 Supercritical carbon dioxide 35 dissolved organic solvent Depressurization and separation operation 37 Carbon dioxide 41 Reaction tank 43 Break vessel 45 Storage tank 47 Pressure reducing valve

Claims (1)

使用済核燃料再処理工程の抽出に使用された劣化溶媒含有使用済有機溶媒に超臨界流体を接触させて該使用済有機溶媒を該超臨界流体に溶解させ、該使用済有機溶媒を溶解した該超臨界流体洗浄水溶液向流接触させて劣化溶媒を洗浄水溶液に溶解させかつ有機溶媒を超臨界二酸化炭素に溶解された儘とし、劣化溶媒を含む前記水溶液を廃液として分離し、しかる後前記有機溶媒を溶解した前記超臨界流体に減圧分離操作を施して超臨界流体と有機溶媒とに分離する使用済核燃料再処理用有機溶媒の洗浄方法。The supercritical fluid is brought into contact with the spent organic solvent containing the deteriorated solvent used in the extraction of the spent nuclear fuel reprocessing step, the spent organic solvent is dissolved in the supercritical fluid, and the spent organic solvent is dissolved. and as one likes dissolved and dissolving the washed aqueous solution with a supercritical fluid to the cleaning solution deterioration solvent was countercurrent contact with the organic solvent in the supercritical carbon dioxide, separating the aqueous solution containing the deterioration solvent as waste, thereafter A method of cleaning an organic solvent for reprocessing spent nuclear fuel, wherein the supercritical fluid in which the organic solvent is dissolved is subjected to a vacuum separation operation to separate it into a supercritical fluid and an organic solvent.
JP2000184780A 2000-06-20 2000-06-20 Cleaning method of organic solvent for spent nuclear fuel reprocessing Expired - Lifetime JP4451966B2 (en)

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KR101016348B1 (en) 2008-08-14 2011-02-25 주식회사 대영기공 Refining method and purification device for waste oil using supercritical solvent and separator

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