JPH0552916B2 - - Google Patents
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- Publication number
- JPH0552916B2 JPH0552916B2 JP59230240A JP23024084A JPH0552916B2 JP H0552916 B2 JPH0552916 B2 JP H0552916B2 JP 59230240 A JP59230240 A JP 59230240A JP 23024084 A JP23024084 A JP 23024084A JP H0552916 B2 JPH0552916 B2 JP H0552916B2
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- JP
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- Prior art keywords
- reaction
- sulfuric acid
- temperature
- boiling point
- solution
- Prior art date
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- Treatment Of Water By Oxidation Or Reduction (AREA)
Description
【発明の詳細な説明】
[発明の技術分野]
本発明は放射性有機廃棄物の酸化分解液中の硫
酸イオンを二酸化イオウとして除去する化学反応
において、反応条件である温度および硫酸濃度を
制御する方法に関する。[Detailed Description of the Invention] [Technical Field of the Invention] The present invention provides a method for controlling temperature and sulfuric acid concentration, which are reaction conditions, in a chemical reaction for removing sulfuric acid ions in the oxidative decomposition solution of radioactive organic waste as sulfur dioxide. Regarding.
[発明の技術的背景とその問題点]
原子力発電所から発生する放射性廃棄物処理の
一つとして、水の浄化に使用した使用済み放射性
イオン交換樹脂や放射性有機廃棄溶媒等の固体ま
たは液体の放射性有機廃棄物の処理がある。これ
らの廃棄物の処理方法としては化学的に分解する
方法が検討されており、例えば、硫酸と硝酸、ま
たは硫酸と過酸化水素によるいわゆる酸消化の方
法、あるいは硫酸第一鉄、硫酸第二鉄または硫酸
銅等を触媒塩として過酸化水素により酸化分解す
る方法、あるいは高温(200℃以上)、高圧(40気
圧以上)で酸素または空気を吹込んで水中で酸化
分解する方法等がある。[Technical background of the invention and its problems] One of the ways to treat radioactive waste generated from nuclear power plants is to treat the radioactivity of solid or liquid materials such as used radioactive ion exchange resins and radioactive organic waste solvents used for water purification. There is processing of organic waste. As a treatment method for these wastes, chemical decomposition methods are being considered; for example, so-called acid digestion methods using sulfuric acid and nitric acid, or sulfuric acid and hydrogen peroxide, or ferrous sulfate and ferric sulfate. Alternatively, there is a method of oxidative decomposition with hydrogen peroxide using copper sulfate as a catalyst salt, or a method of oxidative decomposition in water by blowing oxygen or air at high temperature (200°C or higher) and high pressure (40 atmospheres or higher).
このうち硫酸銅を触媒塩として過酸化水素で酸
化分解する方法では、分解液中の銅イオンを電解
の原理で電極板に回収し、残りの硫酸イオンを含
む液を還元剤または金属銅(この金属銅としては
電極板上の金属銅を利用する)と接触させて硫酸
成分を分解させ、二酸化イオウとして除去する方
法が検討されている。これを金属銅を使用する場
合について示すと、次式のとおりである。 Among these methods, in the method of oxidative decomposition with hydrogen peroxide using copper sulfate as a catalyst salt, the copper ions in the decomposition solution are collected on an electrode plate using the principle of electrolysis, and the remaining sulfate ion-containing solution is used with a reducing agent or metallic copper (copper metal). A method is being considered in which the sulfuric acid component is decomposed by contacting it with metallic copper (using metallic copper on an electrode plate) and removed as sulfur dioxide. This is shown in the following equation when metallic copper is used.
Cu+2H2SO4→CuSO4+SO2↑+
2H2O
一般に
A(水溶液)+B(固体)→C↑(気体)+
D↓(沈殿)
の反応では、生成物CおよびDはそれぞれ気体お
よび沈殿物として反応系外へ出てしまうため、反
応が進行するに従つて反応物であるAの濃度は次
第に低下し、それに伴なつて反応速度も低下す
る。これを第2図に示す。第2図は反応時間の経
過に伴う硫酸分解率の変化を示したもので、図中
破線は加熱せずに反応させた場合の分解率を示し
ている。この場合は反応液中の硫酸濃度が低下し
たために反応速度が低下し、硫酸の分解率が低下
している。一方、実線は後述する方法により反応
条件を制御しながら行つた本発明の場合である。 Cu+2H 2 SO 4 →CuSO 4 +SO 2 ↑+
2H 2 O Generally A (aqueous solution) + B (solid) → C↑ (gas) +
In the reaction D↓ (precipitation), products C and D exit the reaction system as gas and precipitate, respectively, so as the reaction progresses, the concentration of reactant A gradually decreases, and The reaction rate also decreases accordingly. This is shown in FIG. FIG. 2 shows the change in the decomposition rate of sulfuric acid with the passage of reaction time, and the broken line in the figure shows the decomposition rate when the reaction is carried out without heating. In this case, the reaction rate decreased because the sulfuric acid concentration in the reaction solution decreased, and the decomposition rate of sulfuric acid decreased. On the other hand, the solid line represents the case of the present invention, which was carried out while controlling the reaction conditions by the method described below.
この反応速度の低下を防止するためには、加熱
して水分を蒸発させ、反応物の濃度の低下を防止
しなければならない。しかしながら、この加熱に
よる濃度上昇の方が前述の反応の進行に伴う濃度
低下を上回るようになると、反応物の濃度は上昇
して最適範囲を超えるようになる。したがつて反
応系の制御としては温度と濃度の両方をコントロ
ールする必要がある。 In order to prevent this reduction in reaction rate, it is necessary to evaporate water by heating to prevent a reduction in the concentration of the reactants. However, when the increase in concentration due to heating exceeds the decrease in concentration as the reaction progresses, the concentration of the reactant increases and exceeds the optimum range. Therefore, it is necessary to control both temperature and concentration to control the reaction system.
前記(1)の反応において、硫酸成分の分解条件は
温度150℃以上、硫酸濃度約70%以上が望ましい
とされるが、このような高い硫酸濃度を連続的に
測定することは難しい。 In the reaction (1) above, the decomposition conditions for the sulfuric acid component are said to be preferably a temperature of 150° C. or higher and a sulfuric acid concentration of about 70% or higher, but it is difficult to continuously measure such a high sulfuric acid concentration.
一方このような条件で使用される反応容器の装
置材料は限られており、特に原子力の分野では専
ら金属材料を使用することから、硫酸濃度があま
り上昇するのは好ましくなく、ある一定範囲、好
ましくは70%程度に抑えることが望まれる。 On the other hand, equipment materials for reaction vessels used under such conditions are limited, and metal materials are used exclusively in the field of nuclear energy, so it is undesirable for the sulfuric acid concentration to increase too much, and it is preferable within a certain range. It is desirable to keep it to around 70%.
以上のことから、上記反応においては、硫酸濃
度の連続的測定が困難であるにも拘らず、硫酸濃
度を一定範囲内にコントロールすることが強く望
まれる。 From the above, in the above reaction, it is strongly desired to control the sulfuric acid concentration within a certain range, although it is difficult to continuously measure the sulfuric acid concentration.
[発明の目的]
本発明は上記情況に鑑みてなされたもので、そ
の目的とするところは、放射性有機廃棄物の酸化
分解液を還元剤または金属銅の存在下に加熱濃縮
して分解液中の硫酸成分を二酸化イオウに変化さ
せる反応において、温度と硫酸濃度を同時に制御
することのできる方法を提供するにある。[Object of the Invention] The present invention has been made in view of the above circumstances, and its purpose is to heat and concentrate the oxidized decomposition solution of radioactive organic waste in the presence of a reducing agent or metallic copper, and to concentrate the oxidized decomposition solution in the decomposition solution. An object of the present invention is to provide a method in which temperature and sulfuric acid concentration can be simultaneously controlled in a reaction for converting a sulfuric acid component into sulfur dioxide.
[発明の概要]
本発明は放射性有機廃棄物の酸化分解液を還元
剤または金属銅の存在下に加熱反応させて前記分
解液中の硫酸成分を二酸化イオウに分解すること
よりなる放射性有機廃棄物の処理方法において、
反応液を加熱して沸騰させ、この沸点を測定して
測定温度値が常に反応液の最適濃度に対応する沸
点の近似範囲内に入るように希釈水を注入するこ
とにより制御することを特徴とする放射性有機廃
棄物の処理方法に関する。[Summary of the Invention] The present invention provides a method for producing radioactive organic waste by subjecting an oxidative decomposition solution of radioactive organic waste to a heating reaction in the presence of a reducing agent or metal copper to decompose the sulfuric acid component in the decomposition solution into sulfur dioxide. In the processing method of
The method is characterized in that the reaction solution is heated to boiling, the boiling point is measured, and dilution water is injected so that the measured temperature value is always within the approximate range of the boiling point corresponding to the optimum concentration of the reaction solution. Concerning a method for disposing of radioactive organic waste.
本発明において、反応液の沸点を一定値に維持
することにより反応温度および硫酸濃度を同時に
制御できる理由を以下に示す。 In the present invention, the reason why the reaction temperature and sulfuric acid concentration can be controlled simultaneously by maintaining the boiling point of the reaction solution at a constant value will be explained below.
前記したように本発明における硫酸分解反応の
温度条件は150℃以上、反応液中の硫酸濃度は70
%程度が望ましいが、このような条件はこの反応
の反応液の沸点の条件に近い。すなわち硫酸の沸
点曲線を示すと第3図のようになる。例えば濃度
70%の硫酸の沸点は第3図において点線で示され
るように約164℃である。これより濃度が上昇す
れば沸点も上昇する。したがつて、沸点がこの温
度に達したら、希釈水の注入よつて沸点をこの温
度に維持するよにすれば、温度と同時に硫酸濃度
も約70%に保たれることになる。 As mentioned above, the temperature conditions for the sulfuric acid decomposition reaction in the present invention are 150°C or higher, and the sulfuric acid concentration in the reaction solution is 70°C.
%, but such conditions are close to the boiling point conditions of the reaction solution in this reaction. In other words, the boiling point curve of sulfuric acid is shown in Figure 3. For example concentration
The boiling point of 70% sulfuric acid is approximately 164°C, as shown by the dotted line in FIG. If the concentration increases beyond this, the boiling point will also increase. Therefore, when the boiling point reaches this temperature, by injecting dilution water to maintain the boiling point at this temperature, the sulfuric acid concentration will be maintained at about 70% at the same time as the temperature.
[発明の実施例] 本発明の一実施例を第1図によつて説明する。[Embodiments of the invention] An embodiment of the present invention will be described with reference to FIG.
第1図において反応器1は撹拌機2、加熱器
3、温度センサー4、およびコンデンサー5を備
えている。反応容器中の反応液(硫酸水溶液)6
は反応物(金属銅)7と反応して、二酸化イオ
ウ、水および硫酸銅8を生成する。二酸化イオウ
と水は気体としてコンデンサ5を経由して系外へ
出る。反応器1は加熱器3により常時加熱されて
おり、反応液の温度は温度センサー4により常に
検知されている。反応および加熱が進むにしたが
つて、反応液の温度は上昇し、設定した沸点温度
を越える状態になると、温度センサー4からの温
度信号により希釈水注入ポンプ10が制御器9の
監視の下に起動し、希釈タンク11から希釈液1
2が反応器1に注入される。この希釈水12の注
入により反応液6の濃度は低下し、温度も低下す
る。設定温度を下回る温度を温度センサー4が検
知すれば、制御器9の働きで希釈水注入ポンプ1
0は停止する。こうした動作を繰返すことによ
り、反応温度と硫酸濃度を所定値に維持すること
ができる。 In FIG. 1, a reactor 1 is equipped with a stirrer 2, a heater 3, a temperature sensor 4, and a condenser 5. Reaction liquid (sulfuric acid aqueous solution) in reaction vessel 6
reacts with reactant (metallic copper) 7 to produce sulfur dioxide, water and copper sulfate 8. Sulfur dioxide and water exit the system via the condenser 5 as gases. The reactor 1 is constantly heated by a heater 3, and the temperature of the reaction liquid is constantly detected by a temperature sensor 4. As the reaction and heating proceed, the temperature of the reaction liquid rises, and when it exceeds the set boiling point temperature, the dilution water injection pump 10 is activated under the supervision of the controller 9 based on the temperature signal from the temperature sensor 4. Start up and pour diluent 1 from dilution tank 11.
2 is injected into reactor 1. By injecting this dilution water 12, the concentration of the reaction liquid 6 is lowered and the temperature is also lowered. If the temperature sensor 4 detects a temperature lower than the set temperature, the dilution water injection pump 1 is activated by the controller 9.
0 stops. By repeating these operations, the reaction temperature and sulfuric acid concentration can be maintained at predetermined values.
第4図は、上記方法により反応液の温度を制御
した場合とかかる制御を行わなかつた場合とで比
較したグラフである。第4図から明らかなよう
に、本発明による場合は反応液温度が一定に制御
され、一定の硫酸濃度の条件で反応が進行してい
る。一方本発明の方法を採用しなかつた場合は、
反応液の温度は上昇し、水分が蒸発して硫酸濃度
が高くなり、不安定な反応条件となつて装置材料
への影響がでる。 FIG. 4 is a graph comparing the case where the temperature of the reaction solution was controlled by the above method and the case where such control was not performed. As is clear from FIG. 4, in the case of the present invention, the temperature of the reaction solution is controlled to be constant, and the reaction proceeds under conditions of a constant sulfuric acid concentration. On the other hand, if the method of the present invention is not adopted,
The temperature of the reaction solution increases, water evaporates, and the sulfuric acid concentration increases, creating unstable reaction conditions and affecting the equipment materials.
[発明の効果]
以上説明したように本発明の方法によれば、反
応液の温度を測定することによつて反応液の沸点
を所定値に維持するようにし、それによつて反応
温度と同時に硫酸濃度も制御することができる。
したがつて放射性有機廃棄物の酸化分解液中の硫
酸成分を分解させるに当り、温度のみの測定によ
つて硫酸濃度をもコントロールし効率的に反応を
進行させることができる。[Effects of the Invention] As explained above, according to the method of the present invention, the boiling point of the reaction solution is maintained at a predetermined value by measuring the temperature of the reaction solution. Concentration can also be controlled.
Therefore, when decomposing the sulfuric acid component in the oxidative decomposition solution of radioactive organic waste, the sulfuric acid concentration can be controlled by measuring only the temperature, and the reaction can proceed efficiently.
また温度制御および硫酸濃度制御をこのように
行なうことによつて、これらの異常上昇を避ける
ことができるので、反応装置の材料に悪影響を及
ぼすことも防止することができる。 Further, by controlling the temperature and the sulfuric acid concentration in this way, it is possible to avoid these abnormal increases, and therefore it is also possible to prevent adverse effects on the materials of the reactor.
第1図は本発明の方法を実施するための装置の
一例を示す装置概略図、第2図は反応時間の経過
に伴なう硫酸分解率の変化を、加熱しなかつた場
合と本発明の方法を適用した場合とについて示す
グラフ、第3図は硫酸の濃度と沸点との関係を示
すグラフ、第4図は本発明により反応液の温度を
制御した場合と制御しなかつた場合とで比較した
反応温度の変化を示すグラフである。
1……反応器、3……加熱器、4……温度セン
サー、6……反応液、7……反応物、9……制御
器、10……希釈水注入ポンプ、11……希釈水
タンク。
Fig. 1 is a schematic diagram of an apparatus showing an example of an apparatus for carrying out the method of the present invention, and Fig. 2 shows changes in the sulfuric acid decomposition rate with the passage of reaction time, in the case without heating and in the case of the present invention. Figure 3 is a graph showing the relationship between the concentration of sulfuric acid and boiling point. Figure 4 is a comparison between when the temperature of the reaction solution is controlled according to the present invention and when it is not controlled. 2 is a graph showing changes in reaction temperature. 1... Reactor, 3... Heater, 4... Temperature sensor, 6... Reaction liquid, 7... Reactant, 9... Controller, 10... Dilution water injection pump, 11... Dilution water tank .
Claims (1)
は金属銅の存在下に加熱反応させて前記分解液中
の硫酸成分を二酸化イオウに分解することからな
る放射性有機廃棄物の処理方法において、反応液
を加熱して沸騰させ、この沸点を測定して測定温
度値が常に反応液の最適濃度に対応する沸点の近
似範囲内に入るように希釈水を注入することによ
り制御することを特徴とする放射性有機廃棄物の
処理方法。1. In a method for treating radioactive organic waste, which comprises subjecting an oxidative decomposition solution of radioactive organic waste to a heating reaction in the presence of a reducing agent or metallic copper to decompose the sulfuric acid component in the decomposition solution into sulfur dioxide, the reaction solution is heated to boiling point, and the boiling point is measured and controlled by injecting dilution water so that the measured temperature value is always within the approximate range of the boiling point corresponding to the optimum concentration of the reaction solution. How to dispose of organic waste.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP23024084A JPS61110099A (en) | 1984-11-02 | 1984-11-02 | Method of disposing radioactive organic waste |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP23024084A JPS61110099A (en) | 1984-11-02 | 1984-11-02 | Method of disposing radioactive organic waste |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS61110099A JPS61110099A (en) | 1986-05-28 |
| JPH0552916B2 true JPH0552916B2 (en) | 1993-08-06 |
Family
ID=16904721
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP23024084A Granted JPS61110099A (en) | 1984-11-02 | 1984-11-02 | Method of disposing radioactive organic waste |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS61110099A (en) |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS49104100A (en) * | 1973-02-12 | 1974-10-02 | ||
| JPS59184899A (en) * | 1983-04-05 | 1984-10-20 | 株式会社東芝 | Method of treating and volume-decreasing decomposition solution of sulfur-containing radioactive organic waste |
-
1984
- 1984-11-02 JP JP23024084A patent/JPS61110099A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS61110099A (en) | 1986-05-28 |
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