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JP2000144274A - Method and apparatus for electrolytic treatment of zirconium waste - Google Patents

Method and apparatus for electrolytic treatment of zirconium waste

Info

Publication number
JP2000144274A
JP2000144274A JP32910398A JP32910398A JP2000144274A JP 2000144274 A JP2000144274 A JP 2000144274A JP 32910398 A JP32910398 A JP 32910398A JP 32910398 A JP32910398 A JP 32910398A JP 2000144274 A JP2000144274 A JP 2000144274A
Authority
JP
Japan
Prior art keywords
zirconium
waste
electrolytic
electrolysis
oxide
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.)
Pending
Application number
JP32910398A
Other languages
Japanese (ja)
Inventor
Michitaka Mikura
通孝 三倉
Masaaki Kaneko
昌章 金子
Masaya Miyamoto
真哉 宮本
Yoshikazu Matsubayashi
義和 松林
Yasushi Yamaguchi
恭志 山口
Atsushi Nakajima
淳 中嶋
Nobuyuki Ikenaga
信之 池永
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Toshiba Engineering Corp
Toshiba Corp
Original Assignee
Toshiba Engineering Corp
Toshiba Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Toshiba Engineering Corp, Toshiba Corp filed Critical Toshiba Engineering Corp
Priority to JP32910398A priority Critical patent/JP2000144274A/en
Priority to GB9927217A priority patent/GB9927217D0/en
Priority to FR9914573A priority patent/FR2786205B1/en
Priority to GB9927452A priority patent/GB2343899B/en
Publication of JP2000144274A publication Critical patent/JP2000144274A/en
Pending legal-status Critical Current

Links

Classifications

    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21CNUCLEAR REACTORS
    • G21C19/00Arrangements 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
    • G21C19/42Reprocessing of irradiated fuel
    • G21C19/44Reprocessing of irradiated fuel of irradiated solid fuel
    • G21C19/46Aqueous processes, e.g. by using organic extraction means, including the regeneration of these means
    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21CNUCLEAR REACTORS
    • G21C19/00Arrangements 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
    • G21C19/34Apparatus or processes for dismantling nuclear fuel, e.g. before reprocessing ; Apparatus or processes for dismantling strings of spent fuel elements
    • G21C19/38Chemical means only
    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21FPROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
    • G21F9/00Treating radioactively contaminated material; Decontamination arrangements therefor
    • G21F9/28Treating solids
    • G21F9/30Processing
    • 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
    • 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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  • Physics & Mathematics (AREA)
  • Engineering & Computer Science (AREA)
  • General Engineering & Computer Science (AREA)
  • High Energy & Nuclear Physics (AREA)
  • Plasma & Fusion (AREA)
  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Electrolytic Production Of Non-Metals, Compounds, Apparatuses Therefor (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

(57)【要約】 【課題】ジルコニウム廃棄物を処分環境に適した酸化物
とする電解処理方法で、処理速度を低下させない処理方
法を提供する。 【解決手段】硝酸溶液を電解液として用いた電解におい
て、ジルコニウム廃棄物の酸化処理に関し、電解液を
加熱し、電解速度を促進する、超音波照射を行いなが
らジルコニウム廃棄物表面に生成する電気伝導度の非常
に低い酸化ジルコニウム薄膜層を連続的に剥離させる、
ジルコニウムまたはジルコニウム合金全体に上部から
圧力を加え、表面に生成する酸化ジルコニウム薄膜層の
剥離を加速させる、ジルコニウムまたはジルコニウム
合金全体に連続的に衝撃を与え、表面に生成する酸化ジ
ルコニウム薄膜層の剥離を加速させる。また、ジルコニ
ウム廃棄物が比較的小さく、表面が酸化物で覆われてい
る場合、酸化ジルコニウムの薄片を電解用セル内から除
去するために、電解液を撹拌する、廃棄物収納セル
内へ電解液を送液する。
(57) [Summary] [PROBLEMS] To provide an electrolytic treatment method for converting zirconium waste into an oxide suitable for a disposal environment, without decreasing the treatment speed. Kind Code: A1 Abstract: In electrolysis using a nitric acid solution as an electrolytic solution, regarding the oxidation treatment of zirconium waste, electric conduction generated on the surface of the zirconium waste while heating the electrolytic solution to accelerate the electrolysis speed, and performing ultrasonic irradiation. Continuous peeling of a very low degree zirconium oxide thin film layer,
Apply pressure from above to the entire zirconium or zirconium alloy to accelerate the peeling of the zirconium oxide thin film layer formed on the surface.Continuously impact the entire zirconium or zirconium alloy to separate the zirconium oxide thin film layer formed on the surface. Accelerate. When the zirconium waste is relatively small and the surface is covered with oxide, the electrolyte is stirred to remove the zirconium oxide flakes from the electrolysis cell. Is sent.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、ジルコニウム廃棄
物の処理方法及び処理装置に係り、特に、使用済み燃料
被覆管やプルトニウム濃縮缶等のジルコニウム金属また
はその合金等で構成されるジルコニウム廃棄物の処理方
法及び処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for treating zirconium waste, and more particularly to a method for treating zirconium waste such as spent fuel cladding tubes and plutonium concentrators. The present invention relates to a processing method and a processing apparatus.

【0002】[0002]

【従来の技術】原子力発電所で使用した使用済み燃料
は、再処理工場に運ばれ、ここで、ジルコニウムで構成
される燃料被覆管を切断し、硝酸により溶解処理され
る。硝酸溶液中に溶解されたウラン・プルトニウムは分
離精製され、再利用される。
2. Description of the Related Art Spent fuel used in a nuclear power plant is transported to a reprocessing plant, where a fuel cladding tube made of zirconium is cut and dissolved in nitric acid. Uranium and plutonium dissolved in the nitric acid solution are separated, purified, and reused.

【0003】一方、切断された燃料被覆管は、未処理の
まま水槽中に貯蔵される。燃料被覆管の水槽内保管は、
暫定的であると共に、保管に膨大な貯蔵スペースが必要
となる。また、水槽内の水質保持のための装置が必要で
ある。このため、切断された燃料被覆管の減容・固化処
理の開発が求められている。
[0003] On the other hand, the cut fuel cladding tubes are stored in a water tank without any treatment. Storage of fuel cladding in a water tank
It is provisional and requires enormous storage space for storage. In addition, a device for maintaining water quality in the water tank is required. For this reason, there is a demand for the development of volume reduction and solidification treatment of the cut fuel cladding tubes.

【0004】また、再処理工場では、硝酸を高温で取り
扱うプルトニウム濃縮缶、溶解槽、よう素追出槽等の機
器は、ジルコニウム金属で構成される。これらの機器
は、一定期間使用した後、廃棄される予定である。これ
らの機器を固体のジルコニウム廃棄物として減容し固化
処理する方法の開発が求められている。ジルコニウム金
属の処理方法としては、切断、圧縮、溶融等の方法が報
告されている。
[0004] In a reprocessing plant, equipment such as a plutonium concentrator, a dissolution tank, and an iodine ejection tank that handle nitric acid at a high temperature are made of zirconium metal. These devices will be disposed of after a period of use. Development of a method for reducing the volume of these devices as solid zirconium waste and solidifying it is required. As methods for treating zirconium metal, methods such as cutting, compression, and melting have been reported.

【0005】しかしながら、これらの方法では、比較的
活性の高い金属を取り扱うため雰囲気制御や、処理時に
発生する放射性ガスの処理を行う必要がある。また、ジ
ルコニウムにより構成される金属廃棄物の最終的な処分
には地層中に埋設する処分方法が考えられる。
[0005] However, in these methods, it is necessary to control the atmosphere and treat the radioactive gas generated during the treatment in order to handle relatively active metals. For the final disposal of zirconium-containing metal waste, a method of burying it in the stratum can be considered.

【0006】現在想定される地層環境での地下水中で
は、ジルコニウムはIV価の形態が最も安定である。圧
縮、切断、溶融した後、容器に詰めたような処理方法で
は、長期的に水の浸入が考えられ、この場合、浸入した
水との反応によりジルコニウムは酸化され、水素ガスな
どが発生すると考えられる。この場合、金属廃棄物が酸
化物に化学変化し、容積変化、発生したガスの蓄積など
が原因となり、処分施設の健全性を損なうことが懸念さ
れる。
[0006] In groundwater in the currently assumed formation environment, zirconium is most stable in the form of IV valence. In the treatment method of compressing, cutting, melting, and then filling in a container, water infiltration is considered for a long time, and in this case, zirconium is oxidized by the reaction with the infiltrated water and hydrogen gas is generated. Can be In this case, there is a concern that the soundness of the disposal facility may be impaired due to a chemical change of the metal waste into an oxide, a change in volume, an accumulation of generated gas, and the like.

【0007】ジルニウム金属の自然発火性を押さえる方
法や、また、最終処分との適合性、即ち処分施設の健全
性の確保を考えるための電解処理方法が知られている。
しかし、この電解処理方法では、電解反応が進むにつれ
ジルコニウム廃棄物表面に生成する電気伝導度の非常に
低い酸化ジルコニウム層が生成し、電解時の電流が低下
し、処理速度が遅くなる。
[0007] A method for suppressing the spontaneous ignition of zirnium metal and an electrolytic treatment method for considering compatibility with final disposal, that is, ensuring the integrity of the disposal facility, are known.
However, in this electrolytic treatment method, as the electrolytic reaction proceeds, a zirconium oxide layer having a very low electric conductivity is generated on the surface of the zirconium waste, and the current during electrolysis is reduced, and the treatment speed is reduced.

【0008】また、タンクの構造を持つような廃棄物に
関しては、使用の目的から内容面内のみ放射性物質に汚
染されていると考えられる。廃棄物を合理的に処分する
上で、放射性物質のみを除去することは、更に安価な廃
棄物処分が適用できる。しかしながら、前記電解方法で
は、すべてを酸化物に処理する方法についてしか言及し
ていない。
[0008] Further, it is considered that waste having a tank structure is contaminated with radioactive material only in the contents for the purpose of use. In order to dispose of waste efficiently, removing only radioactive materials can be applied to waste disposal at lower cost. However, the above-mentioned electrolysis method only mentions a method of processing everything into an oxide.

【0009】[0009]

【発明が解決しようとする課題】従来のジルコニウム金
属の処理(圧縮、切断、溶融)の問題点である、発火を
おさえるためのガス系の制御や最終処分した際にその環
境条件下で化学変化を起こすことは避けられない。これ
を避けるための前述の電解技術では、電解時の処理速度
の低下を招くという課題がある。
The problem of the conventional treatment (compression, cutting, and melting) of zirconium metal is the control of the gas system for suppressing ignition and the chemical change under the environmental conditions at the time of final disposal. Inevitable. In the above-described electrolysis technique for avoiding this, there is a problem that the processing speed during electrolysis is reduced.

【0010】また、タンクの構造を持つような廃棄物に
関しては、放射性物質による汚染は内面のみであるた
め、これを除去することで、当該廃棄物を非放射性廃棄
物として扱える。このような処理を行うことで合理的で
安価な処理方法が検討可能となるが、従来の方法は全量
を酸化物へと処理する方法であり、汚染部分であるタン
ク内表面だけを処理する方法については検討がなされな
い課題がある。
[0010] Further, regarding waste having a tank structure, since the radioactive material is contaminated only on the inner surface, by removing this, the waste can be treated as non-radioactive waste. By performing such treatment, a reasonable and inexpensive treatment method can be examined, but the conventional method is a method of treating the entire amount into oxide, and a method of treating only the inner surface of the tank which is a contaminated portion. There are issues that are not considered.

【0011】本発明は上記課題を解決するためになされ
たもので、ジルコニウム廃棄物を処分環境に適した酸化
物とする電解処理方法で、処理速度を低下させることな
く酸化処理できるジルコニウム廃棄物の電解処理方法及
びその装置を提供することにある。
SUMMARY OF THE INVENTION The present invention has been made to solve the above-mentioned problems, and is an electrolytic treatment method for converting zirconium waste into an oxide suitable for a disposal environment. An object of the present invention is to provide an electrolytic treatment method and an apparatus therefor.

【0012】また、本発明は、ジルコニウム廃棄物の表
面に生成する酸化物の剥離を促進させることができるジ
ルコニウム廃棄物の電解処理方法及びその装置を提供す
ることにある。
Another object of the present invention is to provide a method and an apparatus for electrolytically treating zirconium waste, which can promote the separation of oxides generated on the surface of zirconium waste.

【0013】[0013]

【課題を解決するための手段】請求項1の発明は、電解
によるジルコニウムまたはジルコニウム合金で構成され
るジルコニウム廃棄物の酸化処理方法において、硝酸溶
液を電解液として用いた場合、電解速度を向上させるた
め電解液を加熱することを特徴とする。
According to a first aspect of the present invention, in a method for oxidizing zirconium waste composed of zirconium or a zirconium alloy by electrolysis, when a nitric acid solution is used as an electrolytic solution, the electrolysis speed is improved. Therefore, the electrolyte is heated.

【0014】請求項2の発明は、電解によるジルコニウ
ムまたはジルコニウム合金で構成される固体廃棄物の酸
化処理方法において、電解時の処理速度を維持するた
め、超音波照射を行いながらジルコニウムまたはジルコ
ニウム合金表面に生成する電気伝導度の非常に低い酸化
ジルコニウム薄膜層を連続的に剥離させることを特徴と
する。
According to a second aspect of the present invention, there is provided a method for oxidizing a solid waste composed of zirconium or a zirconium alloy by electrolysis, in order to maintain the processing speed during electrolysis, while performing ultrasonic irradiation while applying zirconium or zirconium alloy surface. Is characterized in that the zirconium oxide thin film layer having very low electric conductivity is continuously peeled off.

【0015】請求項3の発明は、ジルコニウム廃棄物が
比較的小さく、また表面が酸化物で覆われている場合、
電流効率を高めるため、前記廃棄物だけを電解液中に配
置し、電解時の処理速度を維持するため、ジルコニウム
及びジルコニウム合金全体に上部から圧力を加え、前記
廃棄物の表面に生成する酸化ジルコニウム薄膜層の剥離
を加速させることを特徴とする。
According to a third aspect of the present invention, when the zirconium waste is relatively small and the surface is covered with an oxide,
In order to increase the current efficiency, only the waste is placed in the electrolytic solution, and in order to maintain the processing speed during the electrolysis, pressure is applied to the entire zirconium and zirconium alloy from above, and zirconium oxide generated on the surface of the waste It is characterized in that the peeling of the thin film layer is accelerated.

【0016】請求項4の発明は、ジルコニウム廃棄物が
比較的小さく、また表面が酸化物で覆われている場合、
電流効率を高めるため、前記廃棄物だけを電解液中に配
置し、電解時の処理速度を維持するため、ジルコニウム
及びジルコニウム合金全体に連続的に衝撃を与え、表面
に生成する酸化ジルコニウム薄膜層の剥離を加速させる
ことを特徴とする。
According to a fourth aspect of the present invention, when the zirconium waste is relatively small and the surface is covered with an oxide,
In order to increase the current efficiency, only the waste is placed in the electrolytic solution, and in order to maintain the processing speed during the electrolysis, the whole zirconium and the zirconium alloy are continuously impacted, and the zirconium oxide thin film layer generated on the surface is It is characterized in that peeling is accelerated.

【0017】請求項5の発明は、ジルコニウム廃棄物が
比較的小さく、また表面が酸化物で覆われている場合、
電解を阻害せず、電解処理により発生した酸化物を回収
できるよう電解槽内の電解液正常を均一に保つため、電
解液を攪拌することを特徴とする。
According to a fifth aspect of the present invention, when the zirconium waste is relatively small and the surface is covered with an oxide,
The method is characterized in that the electrolyte is agitated in order to keep the electrolyte normal in the electrolytic bath even so that the oxide generated by the electrolysis treatment can be recovered without inhibiting the electrolysis.

【0018】請求項6の発明は、ジルコニウム廃棄物が
比較的小さく、また表面が酸化物で覆われている場合、
電解処理により発生した酸化物を連続的に廃棄物収納セ
ルから落下させるため、前記廃棄物収納セルの底面に多
数の細孔を設けて電解液を前記廃棄物収納セル内に循環
させることを特徴とする。
According to a sixth aspect of the present invention, when the zirconium waste is relatively small and the surface is covered with an oxide,
In order to continuously drop the oxide generated by the electrolytic treatment from the waste storage cell, a large number of pores are provided on the bottom surface of the waste storage cell, and the electrolyte is circulated in the waste storage cell. And

【0019】請求項7の発明は、ジルコニウム廃棄物が
比較的小さく、また表面が酸化物で覆われている場合、
電流効率を高めるため、前記廃棄物だけを電解槽内の電
解液中に配置し、前記廃棄物表面の酸化ジルコニウム薄
膜層の剥離を加速させるために加熱し、かつ前記加熱部
と、電解槽全体を超音波照射し、更に前記廃棄物全体に
圧力を与えかつ衝撃を与えることを特徴とする。
According to a seventh aspect of the present invention, when the zirconium waste is relatively small and the surface is covered with an oxide,
In order to increase the current efficiency, only the waste is placed in the electrolytic solution in the electrolytic cell, heated to accelerate the peeling of the zirconium oxide thin film layer on the surface of the waste, and the heating section and the entire electrolytic cell are heated. Is irradiated with ultrasonic waves, and further, pressure and impact are applied to the entire waste.

【0020】請求項8の発明は、ジルコニウム廃棄物が
タンクのような構造を持つ場合、タンク内面に付着して
いる放射性物質のみを除去するため、タンク内に電解液
を注入し、内部に陰極を配置し、廃棄物を陽極にしてタ
ンク内面のみ電解し、放射性物質を除染することを特徴
とする。
According to the invention of claim 8, when the zirconium waste has a structure like a tank, an electrolytic solution is injected into the tank to remove only radioactive substances adhering to the inner surface of the tank, and a cathode is inserted therein. And decontamination of radioactive substances by using only waste as an anode and electrolyzing only the inner surface of the tank.

【0021】請求項9の発明は、電解液を収納する電解
槽と、この電解槽内に設置され前記電解液の流路孔を有
しジルコニウム廃棄物を収納する電解用セルと、前記ジ
ルコニウム廃棄物に接触する陽極と、前記電解槽内の電
解液に接触する陰極と、この陰極および前記陽極に直流
電圧を印加する直流電源と、前記電解液を加熱する前記
電解槽に取付けた加熱媒体用ラインと、前記電解液を攪
拌する攪拌子または超音波振動子とを具備したことを特
徴とする。
According to a ninth aspect of the present invention, there is provided an electrolytic cell containing an electrolytic solution, an electrolytic cell provided in the electrolytic cell, having a flow path hole for the electrolytic solution and containing zirconium waste, and an electrolytic cell containing the zirconium waste. An anode in contact with an object, a cathode in contact with the electrolytic solution in the electrolytic cell, a DC power supply for applying a DC voltage to the cathode and the anode, and a heating medium attached to the electrolytic cell for heating the electrolytic solution. A stirrer or an ultrasonic vibrator for stirring the electrolytic solution.

【0022】請求項10の発明は、前記電解槽に酸化処理
時に発生する水素ガス,二酸化炭素ガスまたは窒素酸化
物などを回収する機能を持ったオフガス処理機器を設け
てなることを特徴とする。
According to a tenth aspect of the present invention, the electrolytic cell is provided with an off-gas processing device having a function of recovering hydrogen gas, carbon dioxide gas, nitrogen oxide, or the like generated during the oxidation process.

【0023】[0023]

【発明の実施の形態】図1により本発明に係るジルコニ
ウム廃棄物の電解処理装置の実施の形態を説明する。図
1中、符号1は電解槽で、電解槽1の上端開口には上蓋
2が着脱自在に取付けられる。電解槽1内には電解用セ
ル3が支持体4を介して設置され、電解用セル3内の底
部には電解液の流路孔となる多数の細孔を有する目皿板
5が取付けられている。
DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of an apparatus for electrolytically treating zirconium waste according to the present invention will be described with reference to FIG. In FIG. 1, reference numeral 1 denotes an electrolytic cell, and an upper lid 2 is detachably attached to an upper end opening of the electrolytic cell 1. An electrolytic cell 3 is installed in the electrolytic cell 1 via a support 4, and a perforated plate 5 having a large number of pores serving as electrolyte flow holes is attached to the bottom of the electrolytic cell 3. ing.

【0024】電解用セル3内には目皿板5上に被電解処
理対象物としてのジルコニウム廃棄物6が収納されると
ともに、ジルコニウム廃棄物6上に板状陽極7が載置さ
れる。ジルコニウム廃棄物6としては例えば使用済み燃
料被覆管の細断片,プルトニウム濃縮缶4の細断片等で
ジルコニウム金属またはその合金である。
In the electrolysis cell 3, zirconium waste 6 as an object to be electrolyzed is stored on a perforated plate 5, and a plate-shaped anode 7 is placed on the zirconium waste 6. The zirconium waste 6 is, for example, zirconium metal or an alloy thereof such as a small fragment of a spent fuel cladding tube, a small fragment of a plutonium concentrating can 4, or the like.

【0025】電解槽1内には例えば硝酸溶液などの電解
液8が貯留され、電解槽1の内面と電解用セル3の外面
との間の電解液8中に陰極9が没入浸漬されている。陽
極7と陰極9はそれぞれ上蓋2を貫通するリード線10,
11により直流電源12に接続している。リード線10,11は
上蓋2に取付けた絶縁物13を貫通して電解槽1との間で
電気的な絶縁が保持されている。
An electrolytic solution 8 such as a nitric acid solution is stored in the electrolytic bath 1, and a cathode 9 is immersed and immersed in the electrolytic solution 8 between the inner surface of the electrolytic bath 1 and the outer surface of the electrolytic cell 3. . An anode 7 and a cathode 9 are respectively connected to a lead wire 10 penetrating the upper lid 2,
11 connects to a DC power supply 12. The lead wires 10 and 11 penetrate the insulator 13 attached to the upper lid 2 to maintain electrical insulation between the lead wires 10 and 11 and the electrolytic cell 1.

【0026】電解槽1はベース14上に設置されており、
ベース14にはマグネチックスターラ15が設けられてい
る。このマグネチックスターラ15に対向する電解槽1内
の底面に攪拌子16が配置される。マグネチックスターラ
15の起動により攪拌子16は回転し、動き回って電解液8
を攪拌する。
The electrolytic cell 1 is set on a base 14,
The base 14 is provided with a magnetic stirrer 15. A stirrer 16 is arranged on the bottom surface in the electrolytic cell 1 facing the magnetic stirrer 15. Magnetic stirrer
The starter 15 rotates the stirrer 16 and moves around to move the electrolyte 8
Is stirred.

【0027】電解槽1の外面にほぼ中央部から下方にわ
たり電解液8を加熱するためのジャケット17が取付けら
れ、ジャケット17の右側上方から左側下方にわたって加
熱媒体用ライン18が接続され、加熱媒体用ライン18には
調温器19と循環ポンプ20が取付けられている。
A jacket 17 for heating the electrolytic solution 8 is attached to the outer surface of the electrolytic cell 1 from substantially the center to the lower part, and a heating medium line 18 is connected from the upper right to the lower left of the jacket 17. The line 18 is provided with a temperature controller 19 and a circulation pump 20.

【0028】調温器19で加熱媒体を所定の温度に維持し
て循環ポンプ20を駆動してジャケット17に加熱媒体を供
給して加熱媒体用ライン18を循環させる。加熱媒体によ
り電解槽1内の電解液8を加熱することにより、硝酸溶
液を電解液8として用いた場合、電解速度を向上させる
ことができる。
The heating medium is maintained at a predetermined temperature by the temperature controller 19 and the circulation pump 20 is driven to supply the heating medium to the jacket 17 and circulate the heating medium line 18. When the nitric acid solution is used as the electrolytic solution 8 by heating the electrolytic solution 8 in the electrolytic cell 1 with a heating medium, the electrolysis speed can be improved.

【0029】本実施の形態では、電解槽1内の電解用セ
ル3内は目皿板5を通して流入する電解液8で満たさ
れ、ジルコニウム廃棄物6は陰極9に電圧を印加する
と、電気化学反応が起こり、ジルコニウム廃棄物6の金
属(Zr)母材が電解液8中に溶解する。この金属を溶
解させることにより金属表面に付着した放射性物質を除
去することができる。
In this embodiment, the electrolytic cell 3 in the electrolytic cell 1 is filled with the electrolytic solution 8 flowing through the perforated plate 5, and the zirconium waste 6 is subjected to an electrochemical reaction when a voltage is applied to the cathode 9. Occurs, and the metal (Zr) base material of the zirconium waste 6 dissolves in the electrolytic solution 8. By dissolving the metal, the radioactive substance attached to the metal surface can be removed.

【0030】また、攪拌子16の代りに超音波振動子を使
用することもできる。超音波振動子を使用した場合に
は、超音波振動子を超音波発生器と接続して、超音波振
動子から超音波を電解液8中に照射する。これにより、
電解時の処理速度を維持でき、超音波照射を行いながら
ジルコニウム廃棄物6の表面に生成する電気伝導度の非
常に低い酸化ジルコニウム薄膜層を連続的に剥離させる
ことができる。
Further, an ultrasonic vibrator can be used instead of the stirrer 16. When an ultrasonic vibrator is used, the ultrasonic vibrator is connected to an ultrasonic generator, and the ultrasonic vibrator irradiates ultrasonic waves into the electrolytic solution 8. This allows
The processing speed during the electrolysis can be maintained, and the zirconium oxide thin film layer having extremely low electric conductivity generated on the surface of the zirconium waste 6 can be continuously peeled off while performing ultrasonic irradiation.

【0031】つぎに、本発明に係るジルコニウム廃棄物
の電解処理方法の実施の形態を実施例1〜6について説
明する。 (実施例1)図2および図3により本発明方法の実施例
1を説明する。
Next, embodiments of the electrolytic treatment method for zirconium waste according to the present invention will be described with reference to Examples 1 to 6. (Embodiment 1) Embodiment 1 of the method of the present invention will be described with reference to FIGS.

【0032】本実施例は請求項1の発明に対応し、電解
によるジルコニウムまたはジルコニウム合金で構成され
るジルコニウム廃棄物の酸化処理方法に関し、硝酸溶液
を電解液として用いた場合、電解反応速度を向上させる
ため、電解液を加熱することにある。
This embodiment corresponds to the invention of claim 1 and relates to a method for oxidizing zirconium waste composed of zirconium or a zirconium alloy by electrolysis. In the case of using a nitric acid solution as an electrolytic solution, the electrolytic reaction speed is improved. In this case, the electrolytic solution is heated.

【0033】図2においては電解処理試験装置を概略的
に示しており、符号21は電解槽,22は模擬廃棄物,23は
酸化ジルコニウム,24は陽極,25は陰極,26は電解液を
それぞれ概略的に示している。
FIG. 2 schematically shows an electrolytic treatment test apparatus, in which reference numeral 21 denotes an electrolytic cell, 22 denotes simulated waste, 23 denotes zirconium oxide, 24 denotes an anode, 25 denotes a cathode, and 26 denotes an electrolyte. It is shown schematically.

【0034】原子力発電所等の放射性物質取り扱い施設
を解体する際に発生するジルコニウムおよびジルコニウ
ム合金等のハルと称する模擬廃棄物22を図2に示す電解
処理槽21内にジルコニウムが下部のみを接液させるよう
に設置した。なお、模擬廃棄物22の表面は酸化処理され
二酸化ジルコニウムで覆われているものである。
Simulated waste 22 called hulls such as zirconium and zirconium alloy generated at the time of dismantling a radioactive material handling facility such as a nuclear power plant is placed in an electrolytic treatment tank 21 shown in FIG. It was set up to make it. Note that the surface of the simulated waste 22 is oxidized and covered with zirconium dioxide.

【0035】この電解処理試験装置を用い、ジルコニウ
ム合金を電解処理した。電解液26には、10規定の硝酸
(HNO3 )溶液を用いた。白金処理を施している陰極
25を電解液26中に浸し、白金処理を施している陽極24と
ジルコニウムとジルコニウム合金を液外にて接触させ、
電源部から15Vの直流電圧を1時間印加して電解処理を
行った。
The zirconium alloy was electrolytically treated using this electrolytic treatment test apparatus. As the electrolytic solution 26, a 10N nitric acid (HNO 3 ) solution was used. Cathode with platinum treatment
25 is immersed in an electrolytic solution 26, and the anode 24, which has been subjected to a platinum treatment, is brought into contact with zirconium and a zirconium alloy outside the liquid,
The electrolytic treatment was performed by applying a DC voltage of 15 V for 1 hour from the power supply unit.

【0036】常温による電解では電解が起こらなかった
が、40℃以上の温度で電解が起きた(図3参照)。ま
た、電解が開始される時間は温度の上昇とともに短くな
る傾向を示した。
Although electrolysis did not occur in the electrolysis at room temperature, electrolysis occurred at a temperature of 40 ° C. or higher (see FIG. 3). In addition, the time at which the electrolysis was started tended to become shorter as the temperature increased.

【0037】(実施例2)本実施例2は請求項1の発明
に対応する。実施例1と同様、図2に示す電解処理試験
装置を用いて電解を行った。電解液26の硝酸濃度をパラ
メータとし、常温及び電解液26を80℃に加熱したケース
についてそれぞれ電解を実施した。なお、14Vの定電圧
の直流電圧を1時間印加して電解処理を行った。それぞ
れのケースに関しての電解開始時間を図4に示す。常温
ではいずれの場合も一定時間経過後電解が開始されるの
に対し、80℃では通電直後に電解が開始され定常的に酸
化物が生成した。
(Embodiment 2) Embodiment 2 corresponds to the first aspect of the present invention. As in Example 1, electrolysis was performed using the electrolytic processing test apparatus shown in FIG. Using the nitric acid concentration of the electrolytic solution 26 as a parameter, electrolysis was performed at room temperature and in a case where the electrolytic solution 26 was heated to 80 ° C. respectively. The electrolytic treatment was performed by applying a constant DC voltage of 14 V for one hour. The electrolysis start time for each case is shown in FIG. At room temperature, electrolysis was started after a certain period of time in all cases, whereas at 80 ° C., electrolysis was started immediately after energization, and oxides were constantly generated.

【0038】(実施例3)本実施例3は請求項2及び4
の発明に対応する。すなわち、電解によるジルコニウム
廃棄物の酸化処理に関し、電解時の処理速度を維持する
ため、超音波照射を行いながらジルコニウム廃棄物の表
面に生成する電気伝導度の非常に低い酸化ジルコニウム
薄膜層を連続的に剥離させる。
(Embodiment 3) This embodiment 3 is characterized by claims 2 and 4.
Corresponding to the invention of the above. That is, regarding the oxidation treatment of zirconium waste by electrolysis, in order to maintain the processing speed during electrolysis, a zirconium oxide thin film layer with extremely low electrical conductivity generated on the surface of zirconium waste is continuously formed while performing ultrasonic irradiation. To peel off.

【0039】また、ジルコニウム廃棄物が比較的小さ
く、また表面が酸化物で覆われている場合、電流効率を
高めるため、廃棄物だけを液中に配置し、酸化処理させ
る構造を持つ酸化処理方法に関し、電解時の処理速度を
維持するため、ジルコニウム及びジルコニウム合金全体
に連続的に衝撃を与え、表面に生成する酸化ジルコニウ
ム薄膜層の剥離を加速させる。
When the zirconium waste is relatively small and the surface is covered with an oxide, an oxidizing method having a structure in which only the waste is disposed in a liquid and oxidized to improve the current efficiency. In order to maintain the processing speed during electrolysis, the impact is continuously applied to the entire zirconium and zirconium alloy to accelerate the peeling of the zirconium oxide thin film layer formed on the surface.

【0040】図1に示す電解処理装置を用いて電解を行
った。電解液8には、80℃に加熱した10規定の硝酸(H
NO3 )溶液を用い、直流電源12から14Vの直流電圧を
1時間印加して電解処理を行った。400 Wの超音波を照
射した場合の電流の経時変化を図5に示し、照射を行わ
なかった場合の電流の経時変化を図6に示す。
Electrolysis was performed using the electrolytic processing apparatus shown in FIG. The electrolyte solution 8 contains 10 N nitric acid (H
Using a NO 3 ) solution, a DC voltage of 14 V was applied from a DC power supply 12 for 1 hour to perform an electrolytic treatment. FIG. 5 shows the change with time of the current when the ultrasonic wave of 400 W was irradiated, and FIG. 6 shows the change with time of the current without irradiation.

【0041】電解開始直後の電流値は高いが、いずれの
場合も時間経過とともに電流値が低下している。但し、
超音波照射を行っている場合には電流の最小値は10Aで
あることに対し、照射を行わない場合は45分後に電流が
ほとんど流れなくなり、電解処理が停止した。
The current value immediately after the start of electrolysis is high, but in any case, the current value decreases with time. However,
In the case where the ultrasonic irradiation was performed, the minimum value of the current was 10 A, whereas in the case where the irradiation was not performed, almost no current flowed after 45 minutes, and the electrolytic treatment was stopped.

【0042】なお、超音波照射をしない場合に関して
は、電流が流れなくなった直後(45分間後)セル上部か
ら電解セルに30秒間10回にわたり0.98kg・m2 /sec 2
の衝撃を加えた。その結果、50分間後には電流が流れ、
再び電解が開始された。
In the case where ultrasonic irradiation was not performed, immediately after the current stopped flowing (after 45 minutes), the electrolytic cell was applied 0.98 kg · m 2 / sec 2 from the cell top to the electrolytic cell 10 times for 30 seconds.
Made a shock. As a result, current flows after 50 minutes,
Electrolysis was started again.

【0043】(実施例4)本実施例4は請求項3,4,
5、6及び7の発明に対応する。すなわち、ジルコニウ
ム廃棄物が比較的小さく、また表面が酸化物で覆われて
いる場合、電流効率を高めるため、廃棄物だけを液中に
配置し、酸化処理させる構造を持つ酸化処理装置に関
し、電解時の処理速度を維持するため、ジルコニウム及
びジルコニウム合金全体に上部から圧力を加え、表面に
生成する酸化ジルコニウム薄膜層の剥離を加速させる。
(Embodiment 4) This embodiment 4 is a third embodiment of the present invention.
This corresponds to the inventions of 5, 6, and 7. That is, when the zirconium waste is relatively small and the surface is covered with an oxide, in order to increase the current efficiency, only the waste is disposed in a liquid and an oxidation treatment apparatus having a structure for performing oxidation treatment is used. In order to maintain the processing speed at the time, pressure is applied to zirconium and the zirconium alloy as a whole from the top to accelerate the peeling of the zirconium oxide thin film layer formed on the surface.

【0044】ジルコニウム廃棄物が比較的小さく、また
表面が酸化物で覆われている場合、電解を阻害せず、電
解処理により発生した酸化物を回収できるような細孔構
造を持つ構造の酸化物回収容器に関し、電解槽内の電解
液性状を均一に保つため、電解液を攪拌する。
When the zirconium waste is relatively small and the surface is covered with an oxide, the oxide has a pore structure that does not hinder the electrolysis and allows the oxide generated by the electrolytic treatment to be recovered. Regarding the recovery container, the electrolytic solution is stirred to keep the properties of the electrolytic solution in the electrolytic cell uniform.

【0045】また、ジルコニウム廃棄物が比較的小さ
く、また表面が酸化物で覆われている場合、電解処理に
より発生した酸化物を下部から連続的に廃棄物収納セル
より落下させるため、底面に細孔構造を持つ構造の廃棄
物収納セルに関し、電解液を廃棄物収納セル内に循環さ
せる。
When the zirconium waste is relatively small and the surface is covered with an oxide, the oxide generated by the electrolytic treatment is continuously dropped from the lower part from the waste storage cell, so that the bottom is thin. For a waste storage cell having a hole structure, an electrolyte is circulated in the waste storage cell.

【0046】さらに、ジルコニウム廃棄物が比較的小さ
く、また表面が酸化物で覆われている場合、電流効率を
高めるため、廃棄物だけを液中に配置し、酸化処理させ
る構造を持つ酸化処理方法において、表面の酸化ジルコ
ニウム薄膜層の剥離を加速させるための加熱部と、電解
槽全体を超音波照射できるような構造を有し、更にジル
コニウム廃棄物全体に圧力を加えかつ衝撃を与える。実
施例3と同様、図1に示す電解処理装置を用いて電解を
行った。電解液にはの直流電圧を1時間印加し、350 W
の超音波を照射しながら電解処理を行った。なお、電解
槽1内部に攪拌子を投入し、電解槽1の外部からマグネ
チックスターラ15で電解液8を電解槽1内及び電解用セ
ル3内で均一になるように攪拌した。このとき、電解用
セル3内部の模擬廃棄物には5kgの加重を加えてある。
Furthermore, when the zirconium waste is relatively small and the surface is covered with an oxide, an oxidation treatment method having a structure in which only the waste is placed in a liquid and oxidized in order to increase current efficiency. , A heating section for accelerating the peeling of the zirconium oxide thin film layer on the surface, a structure capable of irradiating the entire electrolytic cell with ultrasonic waves, and further applying pressure and applying an impact to the entire zirconium waste. As in Example 3, electrolysis was performed using the electrolytic processing apparatus shown in FIG. A DC voltage of 350 W is applied to the electrolyte for 1 hour.
The electrolytic treatment was performed while irradiating the ultrasonic waves. In addition, a stirrer was put into the electrolytic cell 1, and the electrolytic solution 8 was stirred from outside the electrolytic cell 1 with a magnetic stirrer 15 so as to be uniform in the electrolytic cell 1 and the electrolytic cell 3. At this time, a load of 5 kg was applied to the simulated waste inside the electrolysis cell 3.

【0047】電流の経時変化を図7に示す。電解開始15
分間後に電流値は著しい低下を示した。電解開始16分後
に電解用セル3の上部から、電解用セル3に15秒間5回
にわたり0.98kg・m2 /sec 2 の衝撃を加えた。その直
後電流値は20Aでほぼ一定の値を示し、処理速度を低下
させることなく定常的に電解が起きた。
FIG. 7 shows the change over time of the current. Start of electrolysis 15
After one minute, the current value showed a remarkable decrease. Sixteen minutes after the start of electrolysis, an impact of 0.98 kg · m 2 / sec 2 was applied to the electrolysis cell 3 from the top of the electrolysis cell 3 for 15 seconds five times. Immediately after that, the current value was almost constant at 20 A, and the electrolysis occurred steadily without reducing the processing speed.

【0048】(実施例5)本実施例5は請求項8の発明
に対応する。すなわち、ジルコニウム廃棄物がタンクの
ような構造を持つ場合、タンク内面に付着している放射
性物質のみを除去するため、タンク内に電解液を注入
し、内部に陰極を配置し、廃棄物を陽極にしてタンク内
面のみ電解し、放射性物質の除染を可能にする。
(Embodiment 5) Embodiment 5 corresponds to the eighth aspect of the present invention. In other words, if the zirconium waste has a tank-like structure, an electrolyte is injected into the tank to remove only radioactive substances adhering to the tank inner surface, a cathode is placed inside, and the waste is treated as an anode. To electrolyze only the inner surface of the tank to enable decontamination of radioactive materials.

【0049】また、ジルコニウム廃棄物がタンクのよう
な構造を持つ場合、前記処理方法に関し、電流効率を高
めるため、タンク内表面の酸化ジルコニウム薄膜層の剥
離を加速させるための加熱部と、電解槽全体を超音波照
射できるような構造を設けて電解処理装置タンク内面の
み電解除染を可能にする。
In the case where the zirconium waste has a tank-like structure, a heating section for accelerating the peeling of the zirconium oxide thin film layer on the inner surface of the tank in order to enhance the current efficiency in the treatment method, and an electrolytic cell A structure capable of irradiating the whole with ultrasonic waves is provided so that only the inner surface of the tank of the electrolytic treatment device can be subjected to electro-release dyeing.

【0050】ジルカロイ製のパイプを切断し、下部を四
フッ化エチレン樹脂製シールで養生したシリコン栓で閉
塞させた模擬廃棄物中に電解液として10規定の硝酸溶液
を添加した。内部に白金線を配置し、模擬廃棄物が陽
極、白金線が陰極になるように直流電源を接続し、電源
部から14Vの直流電圧を10分間印加し電解を行った。
A 10 N nitric acid solution was added as an electrolytic solution to a simulated waste in which a pipe made of Zircaloy was cut and a lower part was closed with a silicon stopper cured with a seal made of tetrafluoroethylene resin. A platinum wire was placed inside, a DC power supply was connected so that the simulated waste became an anode, and the platinum wire became a cathode, and a DC voltage of 14 V was applied from the power supply for 10 minutes to perform electrolysis.

【0051】電解中は電解液に接している面全体から黒
色の薄片が連続的に剥離している状況が確認できた。電
解終了後の内部に蓄積した黒色の薄片状の物質を回収し
X線回折により組成分析したところ、二酸化ジルコニウ
ムであることがわかった。
During electrolysis, it was confirmed that black flakes were continuously peeled from the entire surface in contact with the electrolytic solution. The black flaky substance accumulated inside after completion of the electrolysis was recovered and analyzed for composition by X-ray diffraction. As a result, it was found that the substance was zirconium dioxide.

【0052】(実施例6)本実施例6は請求項10の発明
に対応する。すなわち、ジルコニウム廃棄物がタンクの
ような構造を持つ場合のオフガス系に関し、酸化処理時
に発生する水素ガス、二酸化炭素ガス、窒素酸化物など
を回収する機能を有するオフガス処理機器を設ける。
(Embodiment 6) Embodiment 6 corresponds to the tenth aspect of the present invention. That is, with respect to an off-gas system in which the zirconium waste has a tank-like structure, an off-gas processing device having a function of collecting hydrogen gas, carbon dioxide gas, nitrogen oxide, and the like generated during the oxidation treatment is provided.

【0053】実施例5に記載した模擬廃棄物の上部に10
規定の水酸化ナトリウム水溶液を250ml 入れた洗気ビン
を備えたオフガスラインを取付け、10規定の硝酸溶液を
電解液とし、内部に白金線を配置し、模擬廃棄物が陽
極、白金線が陰極になるように直流電源を接続し、電源
部から14Vの直流電圧を1時間で印加した。
In the upper part of the simulated waste described in Example 5, 10
An offgas line equipped with an air-washing bottle containing 250 ml of a specified sodium hydroxide aqueous solution was installed, a 10N nitric acid solution was used as an electrolyte, a platinum wire was placed inside, a simulated waste was used as the anode, and the platinum wire was used as the cathode. A DC power supply was connected so that a DC voltage of 14 V was applied from the power supply for one hour.

【0054】なお、内部に1l/min の流量で窒素のキ
ャリアガスを導入した。電解時にはNOx ガスが発生し
ていることが確認できた。但しオフガスライン出口での
NOx ガス濃度は検出限界以下であった。
Incidentally, a nitrogen carrier gas was introduced into the inside at a flow rate of 1 l / min. At the time of electrolytic NO x gas it was confirmed that has occurred. However, the NO x gas concentration at the off-gas line outlet was below the detection limit.

【0055】[0055]

【発明の効果】本発明によればジルコニウムまたはジル
コニウム合金で構成されるジルコニウム廃棄物の電解酸
化処理方法に関し、電解時に電解液の加熱、超音波照
射、ジルコニウム及びジルコニウム合金全体への上部か
ら加圧、ジルコニウム及びジルコニウム合金全体に連続
的に衝撃を与えることにより電解反応速度の低下を避け
ることができる。
According to the present invention, there is provided a method for electrolytically oxidizing zirconium waste composed of zirconium or a zirconium alloy. The present invention relates to a method for heating an electrolytic solution, irradiating ultrasonic waves, and applying pressure to the entire zirconium and zirconium alloy from above. , Zirconium and the entire zirconium alloy can be continuously impacted to avoid a reduction in the electrolytic reaction rate.

【0056】また、特に固体廃棄物が比較的小さく、ま
た表面が酸化物で覆われている場合、電解液を攪拌、廃
棄物収納セル内へ電解液を送液を行うことで、電解液の
反応部分近傍での溶液性状の均一性を確保し、電気伝導
度の非常に低い酸化ジルコニウムの薄片を電解セル内か
ら除去することが可能となる。更に、タンクの構造を持
つような廃棄物に対しては、タンク内面に付着している
放射性物質のみを除去することができる。
In particular, when the solid waste is relatively small and the surface is covered with an oxide, the electrolytic solution is stirred and the electrolytic solution is fed into the waste storage cell, so that the electrolytic solution is discharged. It is possible to ensure uniformity of solution properties in the vicinity of the reaction portion, and to remove flakes of zirconium oxide having extremely low electric conductivity from the inside of the electrolytic cell. Further, for waste having a tank structure, only radioactive substances adhering to the tank inner surface can be removed.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明に係るジルコニウム廃棄物の電解処理装
置の実施の形態を一部概略的に示す縦断面図。
FIG. 1 is a longitudinal sectional view schematically showing a part of an embodiment of an apparatus for electrolytically treating zirconium waste according to the present invention.

【図2】本発明に係るジルコニウム廃棄物の電解処理方
法の実施の形態で使用する電解処理試験装置を概略的に
示す縦断面図。
FIG. 2 is a longitudinal sectional view schematically showing an electrolytic treatment test apparatus used in the embodiment of the electrolytic treatment method for zirconium waste according to the present invention.

【図3】本発明に係るジルコニウム廃棄物の電解処理保
法の実施例1における電解液の温度による酸化反応開始
時間依存性を示す特性図。
FIG. 3 is a characteristic diagram showing the dependence of the temperature of the electrolyte on the oxidation reaction start time in Example 1 of the electrolytic treatment and preservation of zirconium waste according to the present invention.

【図4】実施例2における加熱による電解開始時間への
効果を常温で対比して示す比較図。
FIG. 4 is a comparative diagram showing the effect of heating on electrolysis start time in Example 2 at room temperature.

【図5】実施例3における超音波照射(400 W)時の電
流値の変化を示す特性図。
FIG. 5 is a characteristic diagram showing a change in current value during ultrasonic irradiation (400 W) in Example 3.

【図6】実施例3における超音波非照射時の電流値の変
化を示す特性図。
FIG. 6 is a characteristic diagram showing a change in a current value when ultrasonic waves are not irradiated in Example 3.

【図7】実施例4における超音波照射(350 W)時の電
流値の変化を示す特性図。
FIG. 7 is a characteristic diagram showing a change in current value during ultrasonic irradiation (350 W) in Example 4.

【符号の説明】[Explanation of symbols]

1…電解槽、2…上蓋、3…電解用セル、4…支持体、
5…目皿板、6…ジルコニウム廃棄物、7…陽極、8…
電解液、9…陰極、10,11…リード線、12…直流電源、
13…絶縁物、14…ベース、15…マグネチックスターラ、
16…攪拌子または超音波振動子、17…ジャケット、18…
加熱媒体ライン、19…調温器、20…循環用ポンプ、21…
電解処理槽、22…模擬廃棄物、23…酸化ジルコニウム
(ZrO2)、24…陽極、25…陰極、26…電解液。
DESCRIPTION OF SYMBOLS 1 ... Electrolysis tank, 2 ... Top lid, 3 ... Electrolysis cell, 4 ... Support,
5 ... plate, 6 ... zirconium waste, 7 ... anode, 8 ...
Electrolyte, 9 ... Cathode, 10, 11 ... Lead wire, 12 ... DC power supply,
13 ... insulator, 14 ... base, 15 ... magnetic stirrer,
16… Stirrer or ultrasonic vibrator, 17… Jacket, 18…
Heating medium line, 19 ... temperature controller, 20 ... circulation pump, 21 ...
Electrolytic treatment tank, 22: simulated waste, 23: zirconium oxide (ZrO2), 24: anode, 25: cathode, 26: electrolytic solution.

フロントページの続き (72)発明者 金子 昌章 神奈川県川崎市幸区小向東芝町1番地 株 式会社東芝研究開発センター内 (72)発明者 宮本 真哉 神奈川県川崎市幸区小向東芝町1番地 株 式会社東芝研究開発センター内 (72)発明者 松林 義和 神奈川県横浜市磯子区新杉田町8番地 株 式会社東芝横浜事業所内 (72)発明者 山口 恭志 神奈川県横浜市磯子区新杉田町8番地 株 式会社東芝横浜事業所内 (72)発明者 中嶋 淳 神奈川県川崎市幸区堀川町66番の2 東芝 エンジニアリング株式会社内 (72)発明者 池永 信之 神奈川県川崎市幸区堀川町66番の2 東芝 エンジニアリング株式会社内 Fターム(参考) 4K001 AA31 DB05 DB15 Continuing from the front page (72) Inventor Masaaki Kaneko 1st Toshiba R & D Center, Komukai-ku, Kawasaki City, Kanagawa Prefecture (72) Inventor Shinya Miyamoto 1st Toshiba-cho, Komukai Toshiba-ku, Kawasaki-shi, Kanagawa Prefecture Inside the Toshiba Research and Development Center Co., Ltd. (72) Inventor Jun Nakajima 66-2 Horikawacho, Saiwai-ku, Kawasaki City, Kanagawa Prefecture Toshiba Engineering Corporation (72) Inventor Nobuyuki Ikenaga 66-2, Horikawacho, Saiwai-ku, Kawasaki City, Kanagawa Prefecture F-term in Toshiba Engineering Corporation (reference) 4K001 AA31 DB05 DB15

Claims (10)

【特許請求の範囲】[Claims] 【請求項1】 電解によるジルコニウムまたはジルコニ
ウム合金で構成されるジルコニウム廃棄物の酸化処理方
法において、硝酸溶液を電解液として用いた場合、電解
速度を向上させるため前記電解液を加熱することを特徴
とするジルコニウム廃棄物の電解処理方法。
1. A method for oxidizing zirconium waste composed of zirconium or zirconium alloy by electrolysis, wherein a nitric acid solution is used as an electrolytic solution, wherein the electrolytic solution is heated in order to improve the electrolysis speed. Of electrolytic treatment of waste zirconium waste.
【請求項2】 電解によるジルコニウムまたはジルコニ
ウム合金で構成されるジルコニウム廃棄物の酸化処理方
法において、電解時の処理速度を維持するため、超音波
照射を行いながら前記ジルコニウム廃棄物の表面に生成
する電気伝導度の非常に低い酸化ジルコニウム薄膜層を
連続的に剥離させることを特徴とするジルコニウム廃棄
物の電解処理方法。
2. In the method for oxidizing zirconium waste composed of zirconium or zirconium alloy by electrolysis, in order to maintain the processing speed during electrolysis, electricity generated on the surface of the zirconium waste while performing ultrasonic irradiation. A method for electrolytically treating zirconium waste, comprising continuously peeling a zirconium oxide thin film layer having a very low conductivity.
【請求項3】 電解によるジルコニウムまたはジルコニ
ウム合金で構成されるジルコニウム廃棄物の酸化処理方
法において、前記ジルコニウム廃棄物が比較的小さく、
また表面が酸化物で覆われている場合、電流効率を高め
るため、前記ジルコニウム廃棄物だけを電解液中に配置
し、電解時の処理速度を維持するため、前記ジルコニウ
ム廃棄物全体に上部から圧力を加え、前記ジルコニウム
廃棄物の表面に生成する酸化ジルコニウム薄膜層の剥離
を加速させることを特徴とするジルコニウム廃棄物の電
解処理方法。
3. The method for oxidizing zirconium waste composed of zirconium or zirconium alloy by electrolysis, wherein the zirconium waste is relatively small,
When the surface is covered with an oxide, only the zirconium waste is placed in an electrolytic solution in order to increase current efficiency, and a pressure is applied to the entire zirconium waste from above in order to maintain a processing speed during electrolysis. And accelerating the separation of the zirconium oxide thin film layer formed on the surface of the zirconium waste.
【請求項4】 電解によるジルコニウムまたはジルコニ
ウム合金で構成されるジルコニウム廃棄物の酸化処理方
法において、前記ジルコニウム廃棄物が比較的小さく、
また表面が酸化物で覆われている場合、電流効率を高め
るため、前記ジルコニウム廃棄物だけを電解液中に配置
し、電解時の処理速度を維持するため、前記ジルコニウ
ム廃棄物全体に連続的に衝撃を与え、表面に生成する酸
化ジルコニウム薄膜層の剥離を加速させることを特徴と
するジルコニウム廃棄物の電解処理方法。
4. A method for oxidizing zirconium waste composed of zirconium or a zirconium alloy by electrolysis, wherein the zirconium waste is relatively small,
When the surface is covered with an oxide, only the zirconium waste is disposed in an electrolytic solution in order to increase current efficiency, and in order to maintain a processing speed during electrolysis, the zirconium waste is continuously dispersed throughout the zirconium waste. A method for electrolytically treating zirconium waste, comprising applying an impact to accelerate the separation of a zirconium oxide thin film layer formed on a surface.
【請求項5】 電解によるジルコニウムまたはジルコニ
ウム合金で構成されるジルコニウム廃棄物の酸化処理方
法において、前記ジルコニウム廃棄物が比較的小さく、
また表面が酸化物で覆われている場合、電解を阻害せ
ず、電解処理により発生した酸化物を回収できるよう電
解槽内の電解液正常を均一に保つため、電解液を攪拌す
ることを特徴とするジルコニウム廃棄物の電解処理方
法。
5. The method for oxidizing zirconium waste composed of zirconium or zirconium alloy by electrolysis, wherein the zirconium waste is relatively small,
When the surface is covered with oxide, the electrolyte is agitated to keep the normality of the electrolyte in the electrolytic cell uniform so that the oxide generated by the electrolytic treatment is not hindered and the oxide generated by the electrolytic treatment is recovered. Method for electrolytic treatment of zirconium waste.
【請求項6】 電解によるジルコニウムまたはジルコニ
ウム合金で構成されるジルコニウム廃棄物の酸化処理方
法において、前記ジルコニウム廃棄物が比較的小さく、
また表面が酸化物で覆われている場合、電解処理により
発生した酸化物を連続的に廃棄物収納セルから落下させ
るため、前記廃棄物収納セルの底面に多数の細孔を設け
て電解液を前記廃棄物収納セル内に循環させることを特
徴とするジルコニウム廃棄物の電解処理方法。
6. A method for oxidizing zirconium waste composed of zirconium or a zirconium alloy by electrolysis, wherein the zirconium waste is relatively small,
When the surface is covered with oxide, the oxide generated by the electrolytic treatment is continuously dropped from the waste storage cell. A method for electrolytically treating zirconium waste, wherein the method is circulated in the waste storage cell.
【請求項7】 電解によるジルコニウムまたはジルコニ
ウム合金で構成されるジルコニウム廃棄物の酸化処理方
法において、前記ジルコニウム廃棄物が比較的小さく、
また表面が酸化物で覆われている場合、電流効率を高め
るため、前記ジルコニウム廃棄物だけを電解槽内の電解
液中に配置し、前記ジルコニウム廃棄物表面の酸化ジル
コニウム薄膜層の剥離を加速させるために加熱し、かつ
前記加熱部と、電解槽全体を超音波照射し、更に前記ジ
ルコニウム廃棄物全体に圧力を与えかつ衝撃を与えるこ
とを特徴とするジルコニウム廃棄物の電解処理方法。
7. A method for oxidizing zirconium waste composed of zirconium or a zirconium alloy by electrolysis, wherein the zirconium waste is relatively small,
When the surface is covered with an oxide, only the zirconium waste is placed in the electrolytic solution in the electrolytic cell to increase the current efficiency, and the peeling of the zirconium oxide thin film layer on the zirconium waste surface is accelerated. And heating the heating section and the entire electrolytic cell with ultrasonic waves, and further applying pressure and impact to the entire zirconium waste.
【請求項8】 電解によるジルコニウムまたはジルコニ
ウム合金で構成されるジルコニウム廃棄物の酸化処理方
法において、前記ジルコニウム廃棄物がタンクのような
構造を持つ場合、前記タンク内面に付着している放射性
物質のみを除去するため、前記タンク内に電解液を注入
するとともに陰極を配置し、前記ジルコニウム廃棄物を
陽極にして前記タンク内面のみ電解し、前記放射性物質
を除染することを特徴とするジルコニウム廃棄物の電解
処理方法。
8. A method for oxidizing zirconium waste composed of zirconium or a zirconium alloy by electrolysis, wherein when the zirconium waste has a tank-like structure, only radioactive substances adhering to the tank inner surface are removed. In order to remove the zirconium waste, the electrolyte is injected into the tank and a cathode is arranged, the zirconium waste is used as an anode, and only the inner surface of the tank is electrolyzed to decontaminate the radioactive material. Electrolytic treatment method.
【請求項9】 電解液を収納する電解槽と、この電解槽
内に設置され前記電解液の流路孔を有しジルコニウム廃
棄物を収納する電解用セルと、前記ジルコニウム廃棄物
に接触する陽極と、前記電解槽内の電解液に接触する陰
極と、この陰極および前記陽極に直流電圧を印加する直
流電源と、前記電解液を加熱する前記電解槽に取付けた
加熱媒体用ラインと、前記電解液を攪拌する攪拌子また
は超音波振動子とを具備したことを特徴とするジルコニ
ウム廃棄物の電解処理装置。
9. An electrolytic cell containing an electrolytic solution, an electrolytic cell installed in the electrolytic cell, having a flow path hole for the electrolytic solution, and containing zirconium waste, and an anode in contact with the zirconium waste. A cathode for contacting the electrolytic solution in the electrolytic cell, a DC power supply for applying a DC voltage to the cathode and the anode, a heating medium line attached to the electrolytic cell for heating the electrolytic solution, An electrolyzer for zirconium waste, comprising a stirrer or an ultrasonic vibrator for stirring a liquid.
【請求項10】 前記電解槽に前記酸化処理時に発生す
る水素ガス,二酸化炭素ガスまたは窒素酸化物などを回
収する機能を持ったオフガス処理機器を設けてなること
を特徴とする請求項9記載のジルコニウム廃棄物の電解
処理装置。
10. The apparatus according to claim 9, wherein the electrolytic cell is provided with an off-gas processing device having a function of recovering hydrogen gas, carbon dioxide gas, nitrogen oxide, or the like generated during the oxidation treatment. Electrolytic treatment equipment for zirconium waste.
JP32910398A 1998-11-19 1998-11-19 Method and apparatus for electrolytic treatment of zirconium waste Pending JP2000144274A (en)

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JP32910398A JP2000144274A (en) 1998-11-19 1998-11-19 Method and apparatus for electrolytic treatment of zirconium waste
GB9927217A GB9927217D0 (en) 1998-11-19 1999-11-17 Electrolytic treatment method of zirconium and apparatus therefor
FR9914573A FR2786205B1 (en) 1998-11-19 1999-11-19 PROCESS FOR ELECTROLYTIC TREATMENT OF ZIRCONIUM AND APPARATUS THEREFOR
GB9927452A GB2343899B (en) 1998-11-19 1999-11-19 Electrolytic treatment method of zirconium and apparatus therefor

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