JP2000056087A - Chemical decontaminating method and device therefor - Google Patents

Chemical decontaminating method and device therefor

Info

Publication number
JP2000056087A
JP2000056087A JP10222626A JP22262698A JP2000056087A JP 2000056087 A JP2000056087 A JP 2000056087A JP 10222626 A JP10222626 A JP 10222626A JP 22262698 A JP22262698 A JP 22262698A JP 2000056087 A JP2000056087 A JP 2000056087A
Authority
JP
Japan
Prior art keywords
decontamination
agent
oxalic acid
chemical
reactor
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
JP10222626A
Other languages
Japanese (ja)
Inventor
Makoto Nagase
誠 長瀬
Fumito Nakamura
文人 中村
Kazumi Anazawa
和美 穴沢
博雄 ▲吉▼川
Hiroo Yoshikawa
Seiji Furukawa
清治 古川
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.)
Hitachi Ltd
Kurita Water Industries Ltd
Kurita Engineering Co Ltd
Original Assignee
Hitachi Ltd
Kurita Water Industries Ltd
Kurita Engineering 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 Hitachi Ltd, Kurita Water Industries Ltd, Kurita Engineering Co Ltd filed Critical Hitachi Ltd
Priority to JP10222626A priority Critical patent/JP2000056087A/en
Publication of JP2000056087A publication Critical patent/JP2000056087A/en
Pending legal-status Critical Current

Links

Classifications

    • 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

Landscapes

  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PROBLEM TO BE SOLVED: To make the water in the outlet of a resin tower satisfy a drainable quality condition and simultaneously attain the reduction in concentration of a decontaminating agent and the regulation of water level by decomposing a reductive decontaminating agent guided from a part to be intended and passing water to a mix bed resin tower. SOLUTION: In decontamination process, a reactor recirculating pump 3 is started, and the temperature is raised by use of a circulating pump 5 and a heater 6. When the temperature reaches a prescribed temperature (90±5 deg.C), oxalic acid as reductive decontaminating agent any hydrazine as pH regulating agent are injected from a chemical tank 26 to a reactor 1 by use of a chemical injection pump 27. When the oxalic acid concentration reaches a prescribed concentration (0.2%), the chemical injection pump 27 is stopped to end the injection of oxalic acid, and reductive decontamination is performed. The cracked gas generated in a reducing agent decomposing device 16 is separated in a surge tank 17 and returned to the reactor 1 through a degassing line 24. Since most of oxalic acid of the decontaminating solution flowing from the tank 17 is decomposed, the decontaminating solution is cooled to 80 deg.C or lower by a cooler 18 and then guided to a mix bed ion exchange resin 19 to remove the undecomposed oxalic acid, metal ions and the like.

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、水冷却型原子力発
電プラントに係わり、特に放射性核種に汚染された一次
冷却系の機器,配管およびこれらを含む系統の金属部材
表面から放射性核種を化学的に除去する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a water-cooled nuclear power plant. It relates to the method of removing.

【0002】[0002]

【従来の技術】従来の化学除染に関する技術としては、
特開平3−10919号公報に示されるように、酸化処理剤と
して過マンガン酸を、還元剤として有機酸の一種である
ジカルボン酸を用いて原子炉の金属製構造部品を化学的
に汚染除去する方法があり、ここで用いられた有機酸の
分解方法として特表平9−510784 号公報に鉄錯体と紫外
線を用いて二酸化炭素と水に分解する方法が記載されて
いる。
2. Description of the Related Art Conventional techniques relating to chemical decontamination include:
As shown in Japanese Patent Application Laid-Open No. 3-10919, a metal structural component of a nuclear reactor is chemically decontaminated using permanganic acid as an oxidizing agent and dicarboxylic acid which is a kind of organic acid as a reducing agent. As a method for decomposing the organic acid used here, Japanese Patent Application Laid-Open No. 9-510784 describes a method of decomposing the organic acid into carbon dioxide and water using an iron complex and ultraviolet rays.

【0003】この方法によれば、鉄錯体が触媒として作
用し、酸化剤である過酸化水素と有機酸が反応して二酸
化炭素と水を生成するため、有機酸を除去するためのイ
オン交換樹脂が多量の二次廃棄物となることを防いでい
る。
According to this method, an iron complex acts as a catalyst, and hydrogen peroxide as an oxidizing agent reacts with an organic acid to produce carbon dioxide and water. Therefore, an ion exchange resin for removing the organic acid is used. Is prevented from becoming a large amount of secondary waste.

【0004】[0004]

【発明が解決しようとする課題】上記の除染技術を原子
炉の系統除染に適用する場合、除染剤を注入することに
より水量が増大していく。また、原子炉再循環ポンプに
代表される既設ポンプを用いて除染液の循環を行う場合
には、シール水が系外より流入することによっても水量
が増大する。この水量を十分に貯えられる空間を除染系
統に有すれば問題はないが、多くの場合には途中で水を
ドレンする必要が生じる。
When the above-mentioned decontamination technology is applied to the decontamination of a nuclear system, the amount of water increases by injecting a decontamination agent. When the decontamination liquid is circulated using an existing pump typified by a reactor recirculation pump, the amount of water also increases due to the inflow of seal water from outside the system. There is no problem if the decontamination system has a space that can sufficiently store this amount of water, but in many cases it is necessary to drain the water on the way.

【0005】これに対し、前記特表平9−510784 号公報
に記載の分解方法を用いた場合、系統中の有機酸は徐々
に濃度が低下するため、十分な分解処理が終了しないま
ま混床イオン交換樹脂塔に通水すれば、イオン交換樹脂
への負荷が大きくなり分解する意味が薄れる。一方、十
分に分解した後に通水すればイオン交換樹脂への負荷は
小さくなるが、除染液全量を一定のレベルにまで分解す
るために時間を要する上、ドレン工程を分解工程終了後
にシリーズに実施する必要があるため、さらに除染時間
が長くなるという問題がある。
On the other hand, when the decomposition method described in Japanese Patent Application Laid-Open No. 9-510784 is used, the concentration of the organic acid in the system gradually decreases. If water is passed through the ion-exchange resin tower, the load on the ion-exchange resin increases and the meaning of decomposition is reduced. On the other hand, if water is passed after sufficient decomposition, the load on the ion exchange resin will be small, but it will take time to decompose the entire amount of decontamination solution to a certain level, and the drain process will be series after the decomposition process Since it is necessary to carry out, there is a problem that the decontamination time is further increased.

【0006】本発明の目的は、除染剤を分解しながら同
時にドレンを実施できる化学除染方法及びその装置を提
供することにある。
An object of the present invention is to provide a chemical decontamination method and an apparatus which can simultaneously perform drain while decomposing a decontamination agent.

【0007】[0007]

【課題を解決するための手段】上記目的を達成するため
に、本発明では、除染対象部位から導かれる還元除染剤
を少なくとも90%以上一過式で分解できる分解装置を
用いて還元除染剤を分解し、混床樹脂塔に通水する。こ
れにより、樹脂塔出口の水はドレン可能な水質条件を満
足させることが可能となる。また、この水の一部又は全
部を冷却器を通して降温した後ドレン系に排出し、残り
の分を除染対象部位に戻すことにより、除染対象部の除
染剤濃度も低減し、水位の調節も同時に可能となる。
In order to achieve the above object, the present invention provides a method for reducing and decontaminating a reduced decontamination agent introduced from a site to be decontaminated by at least 90% or more by a transient method. The dye is decomposed and water is passed through the mixed-bed resin tower. This makes it possible for the water at the outlet of the resin tower to satisfy the water quality conditions that allow drainage. In addition, part or all of this water is cooled down through a cooler, then discharged to a drain system, and the rest is returned to the decontamination target site, thereby reducing the concentration of the decontamination agent in the decontamination target part and reducing the water level. Adjustment is also possible at the same time.

【0008】[0008]

【発明の実施の形態】本発明の実施例を図1により説明
する。図1は原子炉の系統化学除染を実施する場合の系
統構成の一例を示している。除染対象となるのは、原子
炉1と原子炉再循環ポンプ3を含む原子炉再循環ライン
2である。除染を実施するための仮設機器としては、制
御棒案内管4につなげられた循環ライン7,循環ポンプ
5,ヒーター6,浄化系ポンプ8,カチオン交換樹脂塔
11,過酸化水素タンク14,過酸化水素注入ポンプ1
5,還元剤分解装置16,サージタンク17,冷却器1
8,混床イオン交換樹脂塔19,ドレンライン23に接
続されたドレン水用クーラー22,ガス抜きライン2
4,薬液注入ライン25に接続された薬液タンク26,
薬液注入ポンプ27,ベントライン28,ベントクーラ
ー29に流れを制御するための弁9,10,12,2
0,21を用いる。
DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described with reference to FIG. FIG. 1 shows an example of a system configuration when performing system chemical decontamination of a nuclear reactor. The object to be decontaminated is the reactor 1 and the reactor recirculation line 2 including the reactor recirculation pump 3. Temporary devices for carrying out decontamination include a circulation line 7, a circulation pump 5, a heater 6, a purification system pump 8, a cation exchange resin tower 11, a hydrogen peroxide tank 14, Hydrogen oxide injection pump 1
5, Reducing agent decomposition device 16, surge tank 17, cooler 1
8. Mixed bed ion exchange resin tower 19, drain water cooler 22 connected to drain line 23, gas vent line 2
4, a chemical tank 26 connected to the chemical injection line 25,
Valves 9, 10, 12, 2 for controlling the flow to the chemical injection pump 27, the vent line 28, and the vent cooler 29
0, 21 are used.

【0009】除染剤としてはシュウ酸0.2%にヒドラ
ジンを添加してpHを調整した還元除染剤と過マンガン
酸カリウム0.05%の酸化除染剤を用いることとす
る。除染工程としては、図2に示すように原子炉再循環
ポンプ3を起動してから循環ポンプ5とヒーター6を用
いて昇温し、所定の温度(90±5℃)に到達した段階
で、還元除染剤であるシュウ酸及びpH調整剤であるヒ
ドラジンを薬液タンク26から薬液注入ポンプ27を用
いて原子炉1に注入する。
As the decontamination agent, a reduced decontamination agent prepared by adding hydrazine to 0.2% of oxalic acid to adjust the pH and an oxidative decontamination agent of 0.05% potassium permanganate are used. In the decontamination step, as shown in FIG. 2, the reactor recirculation pump 3 is started, and then the temperature is raised by using the circulation pump 5 and the heater 6 to reach a predetermined temperature (90 ± 5 ° C.). Then, oxalic acid as a reducing decontamination agent and hydrazine as a pH adjuster are injected into the nuclear reactor 1 from a chemical tank 26 using a chemical injection pump 27.

【0010】シュウ酸濃度が所定の濃度(0.2% )に
到達した時点で、薬液注入ポンプ27を停止してシュウ
酸の注入を終了し、還元除染を行う。原子炉再循環ポン
プ3が起動している間はシール水がポンプ3から原子炉
1に流入するため、原子炉1内部の水位は徐々に上昇す
る。還元除染中は、溶解してきた金属イオンや放射性イ
オンを除去するために浄化系ポンプ8を起動し、弁10
と13,20を閉じて弁9と弁12を開き除染液の一部
をカチオン交換樹脂塔11に通水する。
When the concentration of oxalic acid reaches a predetermined concentration (0.2%), the chemical solution injection pump 27 is stopped to terminate the injection of oxalic acid, thereby performing reductive decontamination. While the reactor recirculation pump 3 is operating, the sealing water flows into the reactor 1 from the pump 3, so that the water level inside the reactor 1 gradually rises. During the reduction decontamination, the purification system pump 8 is started to remove dissolved metal ions and radioactive ions, and the valve 10 is operated.
, 13 and 20 are closed, the valves 9 and 12 are opened, and a part of the decontamination liquid is passed through the cation exchange resin tower 11.

【0011】還元除染工程(4時間から15時間程度)
が終了した後の除染剤の分解を行う段階では、弁13,
20,21を開き、弁9と12を閉じて還元剤分解装置
16に除染剤を導くように流れを変える。この際シュウ
酸およびヒドラジンを分解するために、過酸化水素タン
ク14から過酸化水素を注入ポンプ15を用いて還元剤
分解装置16の上流側に注入する。この時の過酸化水素
注入量は、注入後の除染液中のシュウ酸モル濃度とヒド
ラジンモル濃度の2倍の合計と過酸化水素モル濃度とが
同じとなるようにする。
Reduction decontamination step (about 4 to 15 hours)
At the stage of decomposing the decontamination agent after the completion of
20 and 21 are opened, valves 9 and 12 are closed and the flow is changed to direct the decontaminant to the reductant decomposer 16. At this time, in order to decompose oxalic acid and hydrazine, hydrogen peroxide is injected from the hydrogen peroxide tank 14 to the upstream side of the reducing agent decomposer 16 using the injection pump 15. The injection amount of hydrogen peroxide at this time is set so that the molar concentration of hydrogen peroxide is equal to the sum of twice the molar concentration of oxalic acid and the molar concentration of hydrazine in the decontamination solution after injection.

【0012】還元剤分解装置16としては紫外線照射装
置や触媒分解装置を適用することができる。還元剤分解
装置16で発生する分解ガスはサージタンク17で分離
され、ガス抜きライン24を通して原子炉1に戻す。サ
ージタンク17から流出する除染液はシュウ酸の大部分
が分解されているので、冷却器18で温度を80℃以下
に降温した後混床イオン交換樹脂塔19に導き、未分解
のシュウ酸とその他の金属イオン等を除去する。
As the reducing agent decomposing device 16, an ultraviolet irradiation device or a catalytic decomposing device can be applied. Decomposed gas generated in the reducing agent decomposition device 16 is separated in the surge tank 17 and returned to the reactor 1 through the gas release line 24. Since most of the oxalic acid in the decontamination liquid flowing out of the surge tank 17 has been decomposed, the temperature of the oxalic acid is reduced to 80 ° C. or less by the cooler 18 and then guided to the mixed-bed ion exchange resin tower 19, where undecomposed oxalic acid is removed. And other metal ions and the like are removed.

【0013】混床イオン交換樹脂塔19の流出液はほぼ
純水に近くなっているので、その一部又は全部をドレン
ライン23に設置されたドレン水用クーラー22を通し
てプラントの廃液処理系にドレンすることができる。ク
ーラー22を用いるのは除染液の温度を下げ蒸気の放出
を低減させるためである。このように除染剤を一過式で
高い分解率で分解することによりイオン交換樹脂への負
荷を減らし、かつ混床イオン交換樹脂塔を用いることで
除染剤分解工程中に除染液の一部をドレンすることが可
能となる。
Since the effluent of the mixed-bed ion exchange resin tower 19 is almost close to pure water, part or all of the effluent is drained to a waste liquid treatment system of the plant through a drain water cooler 22 installed in a drain line 23. can do. The use of the cooler 22 is for lowering the temperature of the decontamination liquid and reducing the release of steam. Thus, the load on the ion exchange resin is reduced by temporarily decomposing the decontaminant at a high decomposition rate, and the decontamination solution is decomposed during the decontamination agent decomposition step by using a mixed bed ion exchange resin tower. Part of it can be drained.

【0014】したがって還元除染工程中に増加した水位
を除染剤分解中に元のレベルまで戻すことができる。還
元剤が分解する際に発生するガスは、最終的には原子炉
1の上部に設置したベントライン28を通してベントク
ーラー29で余分な蒸気を凝縮除去して排気系に放出す
る。
Accordingly, the water level increased during the reductive decontamination step can be returned to the original level during the decontamination agent decomposition. The gas generated when the reducing agent is decomposed is finally condensed and removed by a vent cooler 29 through a vent line 28 installed in the upper part of the reactor 1 and discharged to an exhaust system.

【0015】還元除染剤の分解が終了した後、薬液タン
ク26から薬液注入ポンプ27を用いて酸化除染剤であ
る過マンガン酸カリウムを系統中に注入し所定の濃度
(0.05%)に調節する。この時は、弁9と10のみ開
き、他を閉じることによってイオン交換樹脂に酸化剤が
接触することを防ぐ。これは酸化剤によって触媒及びイ
オン交換樹脂の劣化を防ぐためである。
After the decomposition of the reduction decontamination agent is completed, potassium permanganate, which is an oxidative decontamination agent, is injected into the system from the chemical solution tank 26 by using a chemical injection pump 27 and adjusted to a predetermined concentration (0.05%). I do. At this time, only the valves 9 and 10 are opened, and the others are closed to prevent the oxidizing agent from contacting the ion exchange resin. This is to prevent the oxidizing agent from deteriorating the catalyst and the ion exchange resin.

【0016】酸化除染工程(4時間から8時間程度)終
了後は、再びシュウ酸を注入して過マンガン酸イオンを
分解し、2価のマンガンイオンに還元する。酸化剤が分
解する際に発生するガスも還元剤の分解時に発生するガ
スと同様に最終的には原子炉1の上部に設置したベント
ライン28を通してベントクーラー29で余分な蒸気を
凝縮除去して排気系に放出する。酸化剤の分解終了後は
カチオン交換樹脂塔11への通水を再開し、溶出した放
射能や酸化剤が分解して生成したマンガンイオン,カリ
ウムイオン等を除去する。
After completion of the oxidative decontamination step (about 4 to 8 hours), oxalic acid is injected again to decompose permanganate ions and reduce them to divalent manganese ions. The gas generated when the oxidizing agent is decomposed is, like the gas generated when the reducing agent is decomposed, finally condensed and removed by a vent cooler 29 through a vent line 28 provided above the reactor 1. Release to exhaust system. After the decomposition of the oxidizing agent, the flow of water to the cation exchange resin tower 11 is restarted to remove the eluted radioactivity and manganese ions and potassium ions generated by the decomposition of the oxidizing agent.

【0017】2回目の還元工程が終了した後は第1回目
の還元剤分解工程と同じ手順で分解し、分解終了後は混
床樹脂を用いて最終浄化を行う。図2では2サイクルを
想定した工程となっているが、より高い除染効果を望む
場合は3サイクル以上とすれば良い。3サイクル以上の
場合には酸化工程,酸化剤分解工程,還元工程,還元剤
分解工程,浄化工程を1つのサイクルとして第1,第2
サイクルの間に挿入した工程とすればよい。
After the completion of the second reduction step, decomposition is carried out in the same manner as in the first reduction agent decomposition step, and after completion of the decomposition, final purification is performed using a mixed bed resin. In FIG. 2, the process assumes two cycles, but if a higher decontamination effect is desired, three or more cycles may be used. In the case of three or more cycles, the oxidation step, the oxidizing agent decomposition step, the reducing step, the reducing agent decomposition step, and the purification step are defined as one cycle, and
It may be a step inserted between cycles.

【0018】[0018]

【発明の効果】本発明の除染方法を用いれば、還元除染
剤分解工程中に系統水の一部をドレンできるため、除染
時間を延長させることなく水位調節が可能となる。
According to the decontamination method of the present invention, a part of the system water can be drained during the step of decomposing the reducing decontaminant, so that the water level can be adjusted without extending the decontamination time.

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

【図1】本発明の化学除染を実施する場合の系統構成を
示す図。
FIG. 1 is a diagram showing a system configuration when performing chemical decontamination of the present invention.

【図2】除染工程の一例を示す図。FIG. 2 is a diagram showing an example of a decontamination step.

【符号の説明】[Explanation of symbols]

1…原子炉、2…原子炉再循環ライン、3…原子炉再循
環ポンプ、4…制御棒案内管、5…循環ポンプ、6…ヒ
ーター、7…除染用仮設循環ライン、8…浄化系ポン
プ、9,10,12,13,20,21…弁、11…カ
チオン交換樹脂塔、14…過酸化水素タンク、15…過
酸化水素注入ポンプ、16…還元剤分解装置、17…サ
ージタンク、18…冷却器、19…混床イオン交換樹脂
塔、22…ドレン水用クーラー、23…ドレンライン、
24…ガス抜きライン、25…薬液注入ライン、26…
薬液タンク、27…薬液注入ポンプ、28…ベントライ
ン、29…ベントクーラー。
DESCRIPTION OF SYMBOLS 1 ... Reactor, 2 ... Reactor recirculation line, 3 ... Reactor recirculation pump, 4 ... Control rod guide tube, 5 ... Circulation pump, 6 ... Heater, 7 ... Temporary circulation line for decontamination, 8 ... Purification system Pump, 9, 10, 12, 13, 20, 21 ... valve, 11 ... cation exchange resin tower, 14 ... hydrogen peroxide tank, 15 ... hydrogen peroxide injection pump, 16 ... reducing agent decomposition device, 17 ... surge tank, 18 ... cooler, 19 ... mixed bed ion exchange resin tower, 22 ... cooler for drain water, 23 ... drain line,
24 ... gas release line, 25 ... chemical liquid injection line, 26 ...
Chemical solution tank, 27: Chemical solution injection pump, 28: Vent line, 29: Vent cooler.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 長瀬 誠 茨城県日立市大みか町七丁目2番1号 株 式会社日立製作所電力・電機開発本部内 (72)発明者 中村 文人 茨城県日立市幸町三丁目1番1号 株式会 社日立製作所日立工場内 (72)発明者 穴沢 和美 茨城県日立市幸町三丁目1番1号 株式会 社日立製作所日立工場内 (72)発明者 ▲吉▼川 博雄 大阪府大阪市中央区北浜二丁目2番22号 栗田エンジニアリング 株式会社内 (72)発明者 古川 清治 神奈川県厚木市森の里若宮7−1 栗田工 業 株式会社内 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Makoto Nagase 7-2-1, Omika-cho, Hitachi City, Ibaraki Pref. Hitachi, Ltd. Power and Electricity Development Division (72) Inventor Fumito Nakamura Yukicho, Hitachi City, Ibaraki Prefecture 3-1-1, Hitachi, Ltd., Hitachi Plant, Hitachi, Ltd. (72) Inventor Kazumi Anazawa 3-1-1, Sakaimachi, Hitachi, Ibaraki Prefecture, Hitachi, Ltd. Hitachi Plant, Hitachi Plant (72) Inventor ▲ Yoshikawa Hiroo 2-22-22 Kitahama, Chuo-ku, Osaka City, Osaka Prefecture Kurita Engineering Co., Ltd. (72) Inventor Seiji Furukawa 7-1 Morinosato Wakamiya, Atsugi City, Kanagawa Prefecture Kurita Kogyo Co., Ltd.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】放射性核種に汚染された金属部材表面から
放射性核種を化学的に除去する化学除染方法において、 ジカルボン酸を主成分とする還元除染剤を用いる還元除
染工程終了後に、前記還元除染剤の分解装置を用いて除
染剤を一過式で分解し、混床樹脂塔に通水して未分解成
分を除去した後、その一部又は全部をドレンして還元剤
分解工程中に水位調節を行うことを特徴とする化学除染
方法。
1. A chemical decontamination method for chemically removing radionuclides from the surface of a metal member contaminated with radionuclides, the method comprising the steps of: The decontamination agent is decomposed in a single pass using a decontamination device for the reducing decontamination agent, and after passing through a mixed-bed resin tower to remove undecomposed components, draining part or all of the decomposed agent to decompose the reducing agent A chemical decontamination method comprising adjusting the water level during the process.
【請求項2】前記還元除染剤のジカルボン酸がシュウ酸
であることを特徴とする請求項1記載の化学除染方法。
2. The chemical decontamination method according to claim 1, wherein the dicarboxylic acid of the reduction decontamination agent is oxalic acid.
【請求項3】還元除染剤としてヒドラジンを添加成分と
することを特徴とする請求項1又は請求項2記載の化学
除染方法。
3. The chemical decontamination method according to claim 1, wherein hydrazine is added as a reducing decontamination agent.
【請求項4】除染対象部位から導き出され再び除染対象
部位に戻る環状導管に、還元除染剤を分解する分解装置
と、その下流側に混床イオン交換樹脂塔を有し、さらに
その下流側に管状導管の外部へ連絡された分岐管がある
ことを特徴とする化学除染装置。
4. A decomposer for decomposing a reducing decontaminant, and a mixed-bed ion-exchange resin tower downstream of the decontamination device are provided in an annular conduit led out of the site to be decontaminated and returned to the site to be decontaminated. A chemical decontamination apparatus characterized in that there is a branch pipe connected to the outside of the tubular conduit on the downstream side.
JP10222626A 1998-08-06 1998-08-06 Chemical decontaminating method and device therefor Pending JP2000056087A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10222626A JP2000056087A (en) 1998-08-06 1998-08-06 Chemical decontaminating method and device therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10222626A JP2000056087A (en) 1998-08-06 1998-08-06 Chemical decontaminating method and device therefor

Publications (1)

Publication Number Publication Date
JP2000056087A true JP2000056087A (en) 2000-02-25

Family

ID=16785409

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10222626A Pending JP2000056087A (en) 1998-08-06 1998-08-06 Chemical decontaminating method and device therefor

Country Status (1)

Country Link
JP (1) JP2000056087A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001289992A (en) * 2000-04-07 2001-10-19 Toshiba Corp Washing method of nuclear power plant
JP2002339088A (en) * 2001-05-18 2002-11-27 Nuclear Services Co Treating agent and method for aluminum surface
CN108780669A (en) * 2016-03-16 2018-11-09 法玛通有限公司 The method of waste water for handling the purification from metal surface, the purposes of wastewater treatment equipment and wastewater treatment equipment
JP2019117205A (en) * 2019-03-20 2019-07-18 株式会社東芝 Method for performing decontamination and method for preparing for decontamination

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001289992A (en) * 2000-04-07 2001-10-19 Toshiba Corp Washing method of nuclear power plant
JP2002339088A (en) * 2001-05-18 2002-11-27 Nuclear Services Co Treating agent and method for aluminum surface
CN108780669A (en) * 2016-03-16 2018-11-09 法玛通有限公司 The method of waste water for handling the purification from metal surface, the purposes of wastewater treatment equipment and wastewater treatment equipment
KR20180124091A (en) * 2016-03-16 2018-11-20 프라마톰 게엠베하 Wastewater treatment method due to decontamination of metal surface, wastewater treatment apparatus and wastewater treatment apparatus
JP2019508704A (en) * 2016-03-16 2019-03-28 フラマトム ゲゼルシャフト ミット ベシュレンクテル ハフツング Method for treating wastewater from decontamination of metal surfaces, use of a wastewater treatment device and wastewater treatment device
KR102356764B1 (en) * 2016-03-16 2022-01-27 프라마톰 게엠베하 Wastewater treatment method due to decontamination of metal surfaces, wastewater treatment equipment and uses of wastewater treatment equipment
JP2019117205A (en) * 2019-03-20 2019-07-18 株式会社東芝 Method for performing decontamination and method for preparing for decontamination

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