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JPH06105317B2 - Decontamination method - Google Patents
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JPH06105317B2 - Decontamination method - Google Patents

Decontamination method

Info

Publication number
JPH06105317B2
JPH06105317B2 JP61024875A JP2487586A JPH06105317B2 JP H06105317 B2 JPH06105317 B2 JP H06105317B2 JP 61024875 A JP61024875 A JP 61024875A JP 2487586 A JP2487586 A JP 2487586A JP H06105317 B2 JPH06105317 B2 JP H06105317B2
Authority
JP
Japan
Prior art keywords
decontamination
cleaning
contaminants
decontaminated
electrolyte solution
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.)
Expired - Lifetime
Application number
JP61024875A
Other languages
Japanese (ja)
Other versions
JPS62182699A (en
Inventor
隆一 佐藤
義信 亀井
茂雄 新井
恒雄 渡辺
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.)
Mitsubishi Nuclear Fuel Co Ltd
Original Assignee
Mitsubishi Nuclear Fuel Co Ltd
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 Mitsubishi Nuclear Fuel Co Ltd filed Critical Mitsubishi Nuclear Fuel Co Ltd
Priority to JP61024875A priority Critical patent/JPH06105317B2/en
Publication of JPS62182699A publication Critical patent/JPS62182699A/en
Publication of JPH06105317B2 publication Critical patent/JPH06105317B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Immobilizing And Processing Of Enzymes And Microorganisms (AREA)
  • Cleaning By Liquid Or Steam (AREA)
  • Cleaning And De-Greasing Of Metallic Materials By Chemical Methods (AREA)

Description

【発明の詳細な説明】 「産業上の利用分野」 この発明は、例えば放射性物質などを収容した容器等の
内壁面に付着して残る放射性物質等の汚染物質を充分か
つ確実に除染することのできる除染方法に関するもので
ある。
DETAILED DESCRIPTION OF THE INVENTION "Industrial field of application" The present invention is to sufficiently and reliably decontaminate radioactive substances and other contaminants that remain on the inner wall surfaces of containers and the like that contain radioactive substances. The present invention relates to a decontamination method that can be performed.

「従来技術とその問題点」 容器等の内壁面から汚染物質を除去する方法には、除染
液としての電解質溶液に酸溶液やアルカリ溶液などを用
いた電解洗浄法、除染液としての洗浄液に酸溶液、アル
カリ溶液、有機溶剤などを用いた超音波洗浄法などがあ
る。
"Prior art and its problems" The method of removing contaminants from the inner wall surface of a container, etc., is an electrolytic cleaning method using an acid solution or alkaline solution as an electrolyte solution as a decontamination solution, and a cleaning solution as a decontamination solution. There is an ultrasonic cleaning method using an acid solution, an alkaline solution, an organic solvent, or the like.

ところが、これらの方法にあっては、いずれも電解質溶
液や洗浄液などの除染液中に汚染物質を溶解させて除去
する方法であるため、除染液中に溶解した汚染物質の濃
度が高い場合に除染効果が著しく低下する問題があっ
た。このため、従来の方法を用いて除染効果を向上させ
ようとするれば、除染液を絶えず新しいものに取り換え
なければならず、そのため除染に使用される除染液が大
量に必要となり、この大量の除染液をさらに凝集沈澱
法、蒸発法などの処理方法によって廃液処理しなければ
ならないなど洗浄コストが高くつき、しかも除染液の交
換に手間がかかって面倒であるなど新たな問題が生じて
いた。
However, in all of these methods, the contaminants are dissolved in the decontamination solution such as the electrolyte solution or the cleaning solution to be removed, so that the concentration of the dissolved contaminants in the decontamination solution is high. However, there was a problem that the decontamination effect was significantly reduced. Therefore, if the decontamination effect is to be improved by using the conventional method, the decontamination solution must be constantly replaced with a new one, and thus a large amount of the decontamination solution used for decontamination is required. However, this large amount of decontamination solution must be further treated by waste solution by a treatment method such as coagulation-sedimentation method or evaporation method, so that the cleaning cost is high, and replacement of the decontamination solution is time-consuming and troublesome. There was a problem.

「問題点を解決するための手段」 発明者らは、上記の問題点を解決するために鋭意研究を
重ねたところ、次のような知見を得るに至った。
"Means for Solving Problems" The inventors of the present invention have conducted extensive studies to solve the above problems, and have obtained the following findings.

すなわち、上記のような容器等に付着する汚染物質が従
来の除染方法によっても充分除去できなかった原因とし
ては、汚染物質の容器等への再付着であると推定され
た。そこで、種々の方法を比較検討したところ、汚染物
質が付着している容器等に対して電解洗浄したのち、そ
の汚染物質に対する貧溶媒中で超音波洗浄する方法が従
来の方法に比べて大幅に除去効率が向上することを知る
に至った。これは、超音波洗浄によて除染された汚染物
質が除染液に溶解されにくいため、除染された被除染体
への再付着が少なく除染効果が大きいためと思われる。
That is, it was presumed that the reason why the contaminants adhering to the container or the like as described above could not be sufficiently removed by the conventional decontamination method was the re-adhesion of the contaminants to the container or the like. Therefore, when various methods were compared and examined, a method of electrolytically cleaning a container or the like to which a contaminant adheres and then ultrasonically cleaning in a poor solvent for the contaminant was significantly larger than the conventional method. We came to know that the removal efficiency was improved. It is considered that this is because the contaminants decontaminated by ultrasonic cleaning are less likely to be dissolved in the decontamination solution, so that re-adhesion to the decontaminated object is small and the decontamination effect is large.

この発明の除染方法は、上記の知見に基づいてなされた
もので、汚染物質が付着している被除染体(例えば容器
等)を電解洗浄したのち、これを上記汚染物質に対する
貧溶媒中で超音波洗浄することを特徴とするものであ
る。
The decontamination method of the present invention has been made based on the above findings. After the object to be decontaminated (for example, a container) to which contaminants are adhered is electrolytically cleaned, it is placed in a poor solvent for the contaminants. It is characterized by ultrasonic cleaning in.

「作用」 この発明に係る除染方法では、まず電解洗浄工程におい
て、ステンレス製の被除染体を陽極として電解質溶液に
通電することにより、被除染体の表面に付着している酸
化物系汚染物質を電解質溶液に溶解させる。このように
汚染物質を溶解させることにより、被除染体の表面から
汚染物質を速やかに分離して電解質溶液中に移行させる
ことができる。すなわち、効率の良い除染を行うには、
汚染物質を電解質溶液に溶解させることが必須である。
ただしこのままでは、上記通電を断った後に、電解質溶
液中の汚染物質濃度に応じた汚染物質の再付着は免れな
い。そこで次に、汚染物質に対する貧溶媒中で超音波洗
浄することにより、被除染体の表面に再付着した微粒子
状の汚染物質をキャビテーションで被除染体から離脱さ
せる。すると、離脱した汚染物質は貧溶媒に溶解するこ
とがないから、貧溶媒に取り囲まれた状態で微粒子状に
分散され、貧溶媒により被除染体からから隔離される。
このため、汚染物質が被染体に再付着しにくく、極めて
高い除染効率を得ることができる。
[Operation] In the decontamination method according to the present invention, first, in the electrolytic cleaning step, the stainless steel decontamination target is energized to the electrolyte solution as an anode, whereby the oxide system adhered to the surface of the decontamination target Dissolve the contaminant in the electrolyte solution. By dissolving the contaminant in this way, the contaminant can be rapidly separated from the surface of the article to be decontaminated and transferred into the electrolyte solution. That is, to perform efficient decontamination,
It is essential that the pollutants be dissolved in the electrolyte solution.
However, in this state, reattachment of the pollutant according to the concentration of the pollutant in the electrolyte solution is unavoidable after the power supply is cut off. Therefore, next, by performing ultrasonic cleaning in a poor solvent for the contaminant, the particulate contaminant reattached to the surface of the substance to be decontaminated is separated from the substance to be decontaminated by cavitation. Then, the separated contaminants are not dissolved in the poor solvent, and are dispersed in the form of fine particles in a state of being surrounded by the poor solvent and separated from the substance to be decontaminated by the poor solvent.
Therefore, contaminants are unlikely to reattach to the article to be dyed, and extremely high decontamination efficiency can be obtained.

「実施例」 以下、この発明の除染方法を容器の例によってさらに詳
しく説明する。
"Example" Hereinafter, the decontamination method of the present invention will be described in more detail with reference to an example of a container.

この発明の除染方法は、汚染物質として酸化物が付着し
ているステンレス製の被除染体を、前記酸化物を溶解可
能な酸または過酸化水素の少なくとも一方を含有する電
解質溶液に浸漬し、前記被除染体を陽極として電解質溶
液に通電するとにより、前記汚染物質を前記電解質溶液
に溶解させて電解洗浄を行なう電解洗浄工程と、電解洗
浄後の前記被除染体を前記汚染物質に対する貧溶媒に浸
漬し、この貧溶媒中で超音波洗浄することにより、被除
染体の表面に残留する汚染物質を被除染体から剥離さ
せ、貧溶媒中に分散させる超音波洗浄工程とを具備する
ことを特徴としたものである。
The decontamination method of the present invention comprises immersing a stainless steel decontamination material having an oxide attached as a contaminant in an electrolyte solution containing at least one of an acid capable of dissolving the oxide and hydrogen peroxide. , An electrolytic cleaning step in which the contaminant is dissolved in the electrolyte solution to perform electrolytic cleaning by energizing the electrolyte solution with the decontamination target as an anode, and the decontamination target after the electrolytic cleaning is against the contaminant. By immersing in a poor solvent and ultrasonically cleaning in this poor solvent, the contaminants remaining on the surface of the object to be decontaminated are separated from the object to be decontaminated, and an ultrasonic cleaning step of dispersing in the poor solvent is performed. It is characterized by having.

上記の容器は、被除染体であって、このものは、通常、
汚染物質を除去する際に用いられる腐食性を有する酸類
などの薬剤に対して腐食されにくいステンレスからなる
ものである。
The above-mentioned container is an article to be decontaminated, which is usually
It is made of stainless steel which is not easily corroded by chemicals such as corrosive acids used for removing contaminants.

上記電解質溶液に使用可能な酸としては、 汚染物質である酸化物を溶解するものが選択され、具体
的には、蓚酸、硫酸、硝酸などが好適である。また、電
解水溶液中の酸または過酸化水素の濃度は、汚染物質で
ある酸化物の種類や濃度などを加味して決められ、例え
ば蓚酸溶液では通常10〜30g/l程度とされるが、これに
限定されるものではない。そして、このような電解質溶
液を使用した電解洗浄は、除染すべきステンレス容器を
陽極とし、電解槽を陰極として行なわれる。その電解条
件としては、電解槽内の電圧が10〜20V程度とされ、電
流密度が30〜60mA/cm2程度とされ、電解時間は、2〜10
分程度とされる。さらに、電解洗浄時の電解質溶液の液
温は、通常20〜50℃程度とされ、20℃未満では、低すぎ
て電解反応が不充分となり、50℃を越えた場合では、電
解反応が進み過ぎて不都合となる。
As the acid that can be used in the electrolyte solution, an acid that dissolves a pollutant oxide is selected, and specifically, oxalic acid, sulfuric acid, nitric acid and the like are preferable. Further, the concentration of acid or hydrogen peroxide in the electrolytic aqueous solution is determined in consideration of the type and concentration of oxides that are pollutants, for example, in an oxalic acid solution is usually about 10 ~ 30 g / l, It is not limited to. Then, electrolytic cleaning using such an electrolyte solution is performed using the stainless steel container to be decontaminated as the anode and the electrolytic cell as the cathode. As the electrolysis conditions, the voltage in the electrolytic cell is about 10 to 20 V, the current density is about 30 to 60 mA / cm 2 , and the electrolysis time is 2 to 10
It is said to be about a minute. Further, the temperature of the electrolyte solution during electrolytic cleaning is usually about 20 to 50 ° C. If the temperature is lower than 20 ° C, the electrolytic reaction becomes insufficient and the electrolytic reaction becomes insufficient. It becomes inconvenient.

また、超音波洗浄に用いられる貧溶媒は、汚染物質の種
類などにより決められ、例えば、汚染物質がUO2、U3O8
等の酸化物などの場合、この酸化物に対する貧溶媒とし
て、UO2、U3O8を最大8.1×10-5重量%程度しか溶解しな
い水やほとんど溶解しないアルコールなどの極性溶媒が
用いられる。そして、このような貧溶媒を用いた超音波
洗浄の条件は、周波数が20〜40kHz程度とされ、出力が2
00〜350W程度とされ、洗浄時間は通常2〜10分程度とさ
れる。また、洗浄中の貧溶媒温度は、貧溶媒の種類など
に左右されるが、通常20〜50℃程度とされる。
Further, the poor solvent used for ultrasonic cleaning is determined by the type of contaminants, and for example, contaminants such as UO 2 and U 3 O 8
In the case of oxides such as, for example, polar solvents such as water and alcohols in which UO 2 and U 3 O 8 are dissolved at a maximum of only about 8.1 × 10 −5 wt% or less are used as a poor solvent for the oxides. The condition of ultrasonic cleaning using such a poor solvent is that the frequency is about 20 to 40 kHz and the output is 2
The cleaning time is usually about 2 to 10 minutes. The temperature of the poor solvent during washing depends on the kind of the poor solvent and the like, but is usually about 20 to 50 ° C.

そして、電解洗浄あるいは超音波洗浄から出る廃液は、
それぞれ電解質溶液あるいは超音波洗浄に使用される貧
溶媒が汚染物質に対する除染効果に優れていることから
少量となり、よってその廃液を蒸発法などの廃液処理法
により簡単に処分することができる。そして、廃液中の
汚染物質は、蒸発法により廃液が処理された際に固形分
として残るため、焼却処分されて灰となる。この焼却灰
は、セメント、アスファルトなどの内部に封じ込められ
て固化処理される。また、有機溶媒を貧溶媒として用い
た場合には、その有機溶媒は焼却処理するか、または貯
蔵容器に入れられて保管される。
And the waste liquid from electrolytic cleaning or ultrasonic cleaning is
Since the electrolyte solution or the poor solvent used for ultrasonic cleaning is excellent in decontaminating effect on contaminants, the amount becomes small, so that the waste liquid can be easily disposed by a waste liquid treatment method such as evaporation method. Then, the pollutants in the waste liquid remain as a solid content when the waste liquid is processed by the evaporation method, and therefore are incinerated to become ash. The incinerated ash is enclosed in cement, asphalt, etc. and solidified. When an organic solvent is used as a poor solvent, the organic solvent is incinerated or stored in a storage container.

なお、この方法において、除染対象となる容器の形状が
単純なものである場合には、電解洗浄したのち、あるい
は超音波洗浄したのちに容器に対してブラシなどによる
機械的な洗浄を行なうこともできる。また、容器の表面
にサビが発生していて、このサビの上に汚染物質が付着
している場合には、サビ除去剤などに20〜40分程度浸漬
してから、ブラシなどを用いて水洗を行なう洗浄操作を
前処理として実施することもできる。このような洗浄操
作を加えることにより、その除染効果をさらに向上させ
ることができる。
In this method, if the container to be decontaminated has a simple shape, perform electrolytic cleaning or ultrasonic cleaning and then mechanically clean the container with a brush or the like. You can also If rust is generated on the surface of the container and contaminants adhere to the rust, soak it in a rust remover for 20 to 40 minutes and then wash it with a brush. It is also possible to carry out the washing operation for carrying out as a pretreatment. By adding such a cleaning operation, the decontamination effect can be further improved.

なお、上記の実施例では、被除染体として例えばペレッ
トトレイなどの容器を用いたが、被除染体としてはこれ
に限定されるものではない。
Although the container to be decontaminated is, for example, a container such as a pellet tray in the above embodiment, the decontamination product is not limited to this.

以下、実施例を示してこの発明の除染方法の作用効果を
明確にする。
Hereinafter, working examples and effects of the decontamination method of the present invention will be clarified.

(実験例) (実験例1) 汚染物質として酸化ウランが付着したステンレス製ペレ
ットトレイを被除染体とし、これを濃度が10g/lの蓚酸
溶液に浸漬させて電解洗浄したのち、汚染物質に対する
貧溶媒として水を用い、この水中で超音波洗浄し、さら
に水洗、乾燥した。そして、この実験例において除染
前、除染後に放射能強度を測定し、その測定結果を除染
係数や除去率と共に第1表に示した。なお、ペレットト
レイの大きさ、電解洗浄および超音波洗浄の洗浄条件
は、次のとおりである。
(Experimental Example) (Experimental Example 1) A stainless steel pellet tray to which uranium oxide is attached as a contaminant is used as a decontamination target, which is immersed in an oxalic acid solution having a concentration of 10 g / l for electrolytic cleaning, and then the contaminant is removed. Water was used as the poor solvent, ultrasonic cleaning was carried out in this water, and further washing and drying were carried out. Then, in this experimental example, the radioactivity intensity was measured before and after decontamination, and the measurement results are shown in Table 1 together with the decontamination coefficient and the removal rate. The size of the pellet tray and the cleaning conditions for electrolytic cleaning and ultrasonic cleaning are as follows.

ペレットトレイ トレイの大きさ…縦84〜100mm×横180〜189mm 電解洗浄条件 電圧…13〜16V、電流…6〜9A、時間…4分、トレイ間
隔…6mm 超音波洗浄条件 周波数…26kHz、出力…300W、陽極電流…15.5mA、時間
…6分 放射能強度の単位…cpm(cunt per minute) DF…除染前の放射能強度/除染後の放射能強度 (実験例2) 実験例1とほぼ同様にしてペレットトレイから汚染物質
を除染した。ただし、濃度が30g/lの蓚酸溶液を用いて
電解洗浄を行なった。そして、この実験例において除染
前、除染後に放射能強度を測定し、その測定結果を除染
係数や除去率と共に第2表に示した。なお、ペレットト
レイの大きさ、電解洗浄および超音波洗浄の洗浄条件
は、次のとおりである。
Pellet tray Size of tray… Vertical 84 to 100 mm × Horizontal 180 to 189 mm Electrolytic cleaning conditions Voltage… 13 to 16 V, current… 6 to 9 A, time… 4 minutes, tray interval… 6 mm Ultrasonic cleaning conditions Frequency… 26 kHz, output… 300W, anode current… 15.5mA, time… 6 minutes Unit of radioactivity intensity ... cpm (cunt per minute) DF ... Radioactivity intensity before decontamination / Radioactivity intensity after decontamination (Experimental example 2) Contaminants are decontaminated from the pellet tray in substantially the same manner as in Experimental example 1. did. However, electrolytic cleaning was performed using an oxalic acid solution having a concentration of 30 g / l. Then, in this experimental example, the radioactivity intensity was measured before and after decontamination, and the measurement results are shown in Table 2 together with the decontamination coefficient and the removal rate. The size of the pellet tray and the cleaning conditions for electrolytic cleaning and ultrasonic cleaning are as follows.

ペレットトレイ トレイの大きさ…縦94〜95mm×横172〜191mm 電解洗浄条件 電圧…9〜10V、電流…10A、時間…5分、トレイ間隔…
6mm 超音波洗浄条件 周波数…26kHz、出力…300W、陽極電流…15.5mA、時間
…6分 (実験例3) 実験例1とほぼ同様にしてペレットトレイから汚染物質
を除染した。ただし、ペレットトレイを濃度が25g/lの
蓚酸溶液中で電解洗浄した後、さらに超音波洗浄した。
そして、除染前、除染後に放射能強度を測定し、その測
定結果を除染係数や除去率と共に第3表に示した。な
お、ペレットトレイの大きさ、電解洗浄および超音波洗
浄の洗浄条件は、次のとおりである。
Pellet tray Size of tray: Vertical 94 to 95 mm x Horizontal 172 to 191 mm Electrolytic cleaning conditions Voltage: 9 to 10 V, current: 10 A, time: 5 minutes, tray interval:
6mm ultrasonic cleaning conditions Frequency… 26kHz, output… 300W, anode current… 15.5mA, time… 6 minutes (Experimental Example 3) Contaminants were decontaminated from the pellet tray in substantially the same manner as in Experimental Example 1. However, the pellet tray was electrolytically cleaned in an oxalic acid solution having a concentration of 25 g / l and then further ultrasonically cleaned.
Then, the radioactivity intensity was measured before and after decontamination, and the measurement results are shown in Table 3 together with the decontamination coefficient and the removal rate. The size of the pellet tray and the cleaning conditions for electrolytic cleaning and ultrasonic cleaning are as follows.

ペレットトレイ トレイの大きさ…縦98mm×横178mm 電解洗浄条件 電圧…12V、電流…10A、時間…5分、トレイ間隔…6mm 超音波洗浄条件 周波数…26kHz、出力…300W、陽極電流…15.5mA、時間
…5分 (従来例1) 放射性物質からなる汚染物質が付着した実験例1〜3で
使用したのとほぼ同様のペレットトレイを除染対象の容
器とし、これを濃度が30g/lの蓚酸溶液に浸漬させて電
解洗浄した。そして、除染前および除染後の放射能強度
を測定し、その測定結果を除染係数や除去率と共に第4
表に示した。なおペレットトレイの大きさおよび電解洗
浄の洗浄条件は、次のとおりである。
Pellet tray Size of tray: Vertical 98 mm x 178 mm Electrolytic cleaning conditions Voltage: 12 V, current: 10 A, time: 5 minutes, tray interval: 6 mm Ultrasonic cleaning conditions Frequency: 26 kHz, output: 300 W, anode current: 15.5 mA, Time ... 5 minutes (Conventional example 1) A pellet tray similar to that used in Experimental Examples 1 to 3 to which a pollutant composed of a radioactive substance was attached was used as a container for decontamination, and this was immersed in an oxalic acid solution having a concentration of 30 g / l. Electrolytically cleaned. Then, the radioactivity intensity before and after decontamination was measured, and the measurement result was measured with the decontamination coefficient and the removal rate.
Shown in the table. The size of the pellet tray and the cleaning conditions for electrolytic cleaning are as follows.

ペレットトレイ トレイの大きさ…縦97mm×横176〜183mm 電解洗浄条件 電圧…10V、電流…8A、時間…3〜8分、トレイ間隔…
6〜7.5mm (従来例2) 放射性物質からなる汚染物質が付着した実験例1〜3を
使用したのとほぼ同様のペレットトレイを除染対象の容
器とし、これを1中に200gの蓚酸と30mlの過酸化水素
を混合せしめた混合液に浸漬させて超音波洗浄した。そ
して、除染前および除染後の放射能強度を測定し、その
測定結果を除染係数や除去率と共に第5表および第6表
に示した。なお、ペレットトレイの大きさおよび超音波
洗浄の洗浄条件は、次のとおりである。
Pellet tray Size of tray: Vertical 97 mm × Horizontal 176 to 183 mm Electrolytic cleaning conditions Voltage: 10 V, current: 8 A, time: 3 to 8 minutes, tray interval:
6-7.5 mm (Conventional example 2) Almost the same pellet tray as used in Experimental Examples 1 to 3 to which a pollutant consisting of a radioactive substance was adhered was used as a container for decontamination, and 200 g of oxalic acid and 30 ml of peroxide were added to 1 container. It was immersed in a mixed solution containing hydrogen and ultrasonically cleaned. Then, the radioactivity intensities before and after decontamination were measured, and the measurement results are shown in Tables 5 and 6 together with the decontamination coefficient and the removal rate. The size of the pellet tray and the cleaning conditions for ultrasonic cleaning are as follows.

ペレットトレイ トレイの大きさ…縦98mm×横178mm 超音波洗浄条件 周波数…26kHz、出力…300W、陽極電流…15.5mA、時間
…30分(第5表)、45分(第6表) (比較例1) 放射性物質からなる汚染物質が付着した実験例1〜3で
使用したのとほぼ同様のペレットトレイを被除染体と
し、これを濃度が10g/lの蓚酸溶液に浸漬させて電解洗
浄したのち、汚染物質に対する良溶媒として2Nの硝酸を
用い、この良溶媒中で超音波洗浄した。そして、この比
較例において除染前、除染後に放射能強度を測定し、そ
の測定結果を除染係数や除去率と共に第7表に示した。
なお、ペレットトレイの大きさ、電解洗浄および超音波
洗浄の洗浄条件は、次のとおりである。
Pellet tray Size of tray: Vertical 98 mm x 178 mm Ultrasonic cleaning conditions Frequency: 26 kHz, output: 300 W, anode current: 15.5 mA, time: 30 minutes (Table 5), 45 minutes (Table 6) (Comparative Example 1) A pellet tray similar to that used in Experimental Examples 1 to 3 to which a pollutant composed of a radioactive substance was attached was used as a decontamination target, and this was immersed in an oxalic acid solution having a concentration of 10 g / l. After electrolytic cleaning, 2N nitric acid was used as a good solvent for contaminants, and ultrasonic cleaning was performed in this good solvent. Then, in this comparative example, the radioactivity intensity was measured before and after decontamination, and the measurement results are shown in Table 7 together with the decontamination coefficient and the removal rate.
The size of the pellet tray and the cleaning conditions for electrolytic cleaning and ultrasonic cleaning are as follows.

ペレットトレイ トレイの大きさ…縦84〜100mm×横180〜189mm 電解洗浄条件 電圧…13〜16V、電流…6〜9A、時間…4分、トレイ間
隔…6mm 超音波洗浄条件 周波数…26kHz、出力…300W、陽極電流…15.5mA、時間
6分 これらの結果から明らかなように、上記実験例1〜3
は、従来例1、2に比べて、高い除染係数および除去率
を示していることから、容器から汚染物質を除去する除
染能力に優れていることがわかる。
Pellet tray Size of tray… Vertical 84 to 100 mm × Horizontal 180 to 189 mm Electrolytic cleaning conditions Voltage… 13 to 16 V, current… 6 to 9 A, time… 4 minutes, tray interval… 6 mm Ultrasonic cleaning conditions Frequency… 26 kHz, output… 300W, anode current… 15.5mA, time 6 minutes As is clear from these results, Experimental Examples 1 to 3 above
Shows a higher decontamination coefficient and a higher removal rate than those of Conventional Examples 1 and 2, and thus it is clear that the decontamination ability of removing contaminants from the container is excellent.

「発明の効果」 以上説明したように、この発明の除染方法によれば、ま
ず電解洗浄工程において、ステンレス製の被除染体を陽
極として前記電解質溶液に通電し、被除染体の表面に付
着している酸化物系汚染物質を電解質溶液に溶解させる
ことにより、被除染体の表面から汚染物質を速やかに分
離して電解質溶液中に移行させる。続いて、被除染体を
汚染物質に対する貧溶媒中で超音波洗浄することによ
り、汚染物質の再付着の程度が軽度なうちに、被除染体
の表面に再付着した微粒子状の汚染物質をキャビテーシ
ョンで被除染体から離脱させる。離脱した汚染物質は貧
溶媒に溶解することがないため、貧溶媒に取り囲まれて
微粒子状に分散され、貧溶媒により被除染体から隔離さ
れて、被除染体への再付着が防止される。
"Effects of the Invention" As described above, according to the decontamination method of the present invention, in the electrolytic cleaning step, the stainless steel decontamination target is used as an anode to energize the electrolyte solution to decontaminate the surface of the decontamination target. By dissolving the oxide-based pollutants adhering to the electrolyte solution in the electrolyte solution, the pollutants are promptly separated from the surface of the article to be decontaminated and transferred to the electrolyte solution. Then, by ultrasonically cleaning the substance to be decontaminated in a poor solvent for contaminants, while the degree of reattachment of the contaminant is mild, the particulate contaminant reattached to the surface of the substance to be decontaminated. Cavitation is used to remove from the body to be decontaminated. The released contaminants are not dissolved in the poor solvent, so they are surrounded by the poor solvent and dispersed in fine particles, and are separated from the decontamination target by the poor solvent, preventing reattachment to the decontamination target. It

このように、本願発明の除染方法では、電解洗浄工程で
被除染体の表面の汚染物質の大部分を溶解除去した後、
超音波洗浄工程では、前記溶解除去の後に再付着した汚
染物質を、さらなる再付着を阻止しつつ非溶解状態で除
去するため、処理効率を損なうことなく高い除染率を得
ることができるうえ、電解質溶液および超音波洗浄液を
除染中に頻繁に交換しなくてよいから、廃液量を極力少
なく抑えることが可能である。
Thus, in the decontamination method of the present invention, after most of the contaminants on the surface of the article to be decontaminated are dissolved and removed in the electrolytic cleaning step,
In the ultrasonic cleaning step, the contaminants redeposited after the dissolution removal are removed in a non-dissolved state while preventing further redeposition, so that a high decontamination rate can be obtained without impairing the processing efficiency. Since it is not necessary to frequently exchange the electrolyte solution and the ultrasonic cleaning liquid during decontamination, it is possible to suppress the amount of waste liquid to a minimum.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 渡辺 恒雄 茨城県那珂郡東海村大字舟石川622番地1 三菱原子燃料株式会社東海製作所内 (56)参考文献 特開 昭60−106998(JP,A) 特公 昭59−33877(JP,B2) ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Tsuneo Watanabe 622, Funaishikawa, Tokai-mura, Naka-gun, Ibaraki Prefecture Mitsubishi Nuclear Fuel Co., Ltd. Tokai Works (56) Reference JP-A-60-106998 (JP, A) Japanese Patent Publication Sho 59-33877 (JP, B2)

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】汚染物質として酸化物が付着しているステ
ンレス製の被除染体を、前記酸化物を溶融可能な酸また
は過酸化水素の少なくとも一方を含有する電解質溶液に
浸漬し、前記被除染体を陽極として前記電解質溶液に通
電することにより、前記汚染物質を前記電解質溶液に溶
解させて電解洗浄を行なう電解洗浄工程と、 電解洗浄後の前記被除染体を前記汚染物質に対する貧溶
媒に浸漬し、この貧溶媒中で超音波洗浄することによ
り、被除染体の表面に残留する汚染物質を被除染体から
剥離させ、貧溶媒中に分散させる超音波洗浄工程とを具
備することを特徴とする除染方法。
1. A stainless steel decontamination material to which an oxide adheres as a contaminant is immersed in an electrolyte solution containing at least one of an acid capable of melting the oxide and hydrogen peroxide, An electrolytic cleaning step in which the contaminants are dissolved in the electrolyte solution to perform electrolytic cleaning by energizing the electrolyte solution with the decontaminating body serving as an anode, and By immersing in a solvent and ultrasonically cleaning in this poor solvent, the contaminants remaining on the surface of the object to be decontaminated are separated from the object to be decontaminated, and an ultrasonic cleaning step of dispersing in a poor solvent is provided. A decontamination method characterized by:
JP61024875A 1986-02-06 1986-02-06 Decontamination method Expired - Lifetime JPH06105317B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61024875A JPH06105317B2 (en) 1986-02-06 1986-02-06 Decontamination method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61024875A JPH06105317B2 (en) 1986-02-06 1986-02-06 Decontamination method

Publications (2)

Publication Number Publication Date
JPS62182699A JPS62182699A (en) 1987-08-11
JPH06105317B2 true JPH06105317B2 (en) 1994-12-21

Family

ID=12150376

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61024875A Expired - Lifetime JPH06105317B2 (en) 1986-02-06 1986-02-06 Decontamination method

Country Status (1)

Country Link
JP (1) JPH06105317B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6336976B1 (en) * 1999-01-04 2002-01-08 Kabushiki Kaisha Sankyo Seiki Seisakusho Hole processing apparatus and method thereof and dynamic pressure bearings cleaning method
JP2004117149A (en) * 2002-09-26 2004-04-15 Hitachi Ltd Method and apparatus for electrodischarge dyeing of reprocessing waste

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58127000A (en) * 1982-01-25 1983-07-28 Toshiba Corp Electrolytic polishing decontamination device
JPS5933877A (en) * 1982-08-19 1984-02-23 Seiko Epson Corp Active matrix substrate
JPS60106998A (en) * 1983-11-16 1985-06-12 Mitsubishi Heavy Ind Ltd Electrolytic decontamination method

Also Published As

Publication number Publication date
JPS62182699A (en) 1987-08-11

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