JPH03181899A - Cement solidification of cinder ash of radioactive waste - Google Patents
Cement solidification of cinder ash of radioactive wasteInfo
- Publication number
- JPH03181899A JPH03181899A JP32224089A JP32224089A JPH03181899A JP H03181899 A JPH03181899 A JP H03181899A JP 32224089 A JP32224089 A JP 32224089A JP 32224089 A JP32224089 A JP 32224089A JP H03181899 A JPH03181899 A JP H03181899A
- Authority
- JP
- Japan
- Prior art keywords
- cement
- radioactive waste
- solidification
- storage container
- incineration ash
- 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
Links
- 239000004568 cement Substances 0.000 title claims description 42
- 239000002901 radioactive waste Substances 0.000 title claims description 17
- 238000007711 solidification Methods 0.000 title description 28
- 230000008023 solidification Effects 0.000 title description 28
- 239000003818 cinder Substances 0.000 title 1
- 238000004056 waste incineration Methods 0.000 claims description 13
- 238000000034 method Methods 0.000 claims description 11
- 238000006703 hydration reaction Methods 0.000 claims description 10
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 8
- 239000011396 hydraulic cement Substances 0.000 claims description 5
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims description 4
- 239000000377 silicon dioxide Substances 0.000 claims description 4
- 238000010438 heat treatment Methods 0.000 claims 1
- 239000012530 fluid Substances 0.000 description 6
- 239000000463 material Substances 0.000 description 5
- 239000012857 radioactive material Substances 0.000 description 4
- 230000006835 compression Effects 0.000 description 3
- 238000007906 compression Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 230000005855 radiation Effects 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 239000011083 cement mortar Substances 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 239000011440 grout Substances 0.000 description 2
- 230000020169 heat generation Effects 0.000 description 2
- 230000036571 hydration Effects 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 230000002285 radioactive effect Effects 0.000 description 2
- 230000015271 coagulation Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 230000003111 delayed effect Effects 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 239000000941 radioactive substance Substances 0.000 description 1
- 238000004904 shortening Methods 0.000 description 1
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.
Description
【発明の詳細な説明】
「産業上の利用分野」
本発明は、放射性廃棄物焼却灰のセメント固化方法に係
り、特に、放射性廃棄物焼却灰を速やかに固化状態に導
く技術に関するものである。DETAILED DESCRIPTION OF THE INVENTION "Field of Industrial Application" The present invention relates to a method for solidifying radioactive waste incineration ash into cement, and particularly relates to a technique for quickly bringing radioactive waste incineration ash into a solidified state.
「従来の技術」
原子カプラント関係施設において発生する放射性廃棄物
の容積を減少させる(減容させる)方法として、可燃物
及び熱分解対象物を焼却することが行なわれ、そして、
この場合に生じる焼却灰は、放射性物質が濃縮された状
態となるために、放射性物質の拡散防止を図るための一
つの手段として、焼却灰をグラウト(セメントモルタル
)とともにドラム缶に充填して、セメント固化処理する
ことにより閉じ込めた状態とし、さらに、放射線汚染を
防止するために、セメント固化体を放射性廃棄物貯蔵施
設に長期間保管することが計画されている。"Prior Art" As a method of reducing the volume of radioactive waste generated in nuclear couplant-related facilities, incineration of combustible materials and materials to be thermally decomposed is carried out, and
The incinerated ash produced in this case has concentrated radioactive materials, so one way to prevent the spread of radioactive materials is to fill drums with grout (cement mortar) and cement the incinerated ash with grout (cement mortar). It is planned that the solidified cement will be kept in a confined state through solidification treatment, and that it will be stored for a long period of time in a radioactive waste storage facility to prevent radioactive contamination.
[発明が解決しようとする課題]
しかし、セメント固化体を形成する場合にあって、固化
前の放射性廃棄物焼却灰及び固化途中の放射性廃棄物焼
却灰は、そのセメント固化処理工程中に、放射性物質が
崩壊する現象によって放射線を放出するために、セメン
ト固化作業に従事する作業員の被曝線量の管理を十分に
行なって安全性を確保することが必要であるが、セメン
トが固化するまでの間は、被固化物の収納容器を運搬す
ることかできず、相当期間の貯蔵を余儀なくされる。[Problem to be solved by the invention] However, when forming a cement solidified body, radioactive waste incineration ash before solidification and radioactive waste incineration ash in the middle of solidification become radioactive during the cement solidification process. Since radiation is emitted by the phenomenon of material decay, it is necessary to adequately control the radiation dose of workers engaged in cement solidification work to ensure safety. However, it is not possible to transport the container containing the material to be solidified, and the material must be stored for a considerable period of time.
本発明は、かかる事情に鑑みてなされたもので、セメン
ト固化に要する時間を短縮し、セメント固化時における
放射性物質の滞貨量を低減することを目的とするもので
ある。The present invention has been made in view of the above circumstances, and aims to shorten the time required for cement solidification and reduce the amount of radioactive materials accumulated during cement solidification.
「課題を解決するための手段」
かかる目的を達成するため、本発明にあっては、放射性
廃棄物焼却灰を収納容器に収納してセメント固化するも
のであるが、収納容器内に、水及び放射性廃棄物焼却灰
と、シリカセメント、アルミナセメント等の水硬性セメ
ントとを充填して密封し、該密封した収納容器を高速回
転させることにより、混合内容物に遠心力を付与して圧
縮状態とするとともに、セメントの水和反応熱によって
内容物を加熱して、凝結硬化状態に導くことを特徴とす
る放射性廃棄物焼却灰のセメント固化方法としている。"Means for Solving the Problem" In order to achieve the above object, in the present invention, radioactive waste incineration ash is stored in a storage container and solidified with cement. Radioactive waste incineration ash and hydraulic cement such as silica cement or alumina cement are filled and sealed, and the sealed storage container is rotated at high speed to apply centrifugal force to the mixed contents and bring them into a compressed state. In addition, the method for solidifying radioactive waste incineration ash into cement is characterized in that the content is heated by the heat of the hydration reaction of the cement to bring it into a solidified and hardened state.
「作用 」
収納容器内に、水及び放射性廃棄物焼却灰と、シリカセ
メント、アルミナセメント等の水硬性セメントとを収納
すると、いわゆるセメントの水和作用、セメント鉱物と
水との反応により、凝結現象を生じるとともに、続いて
硬化現象が起こる。"Function" When water, radioactive waste incineration ash, and hydraulic cement such as silica cement or alumina cement are stored in a storage container, a coagulation phenomenon occurs due to the so-called hydration of cement and the reaction between cement minerals and water. , followed by a hardening phenomenon.
この場合に、混合内容物に遠心力が付与されていると、
混合内容物が遠心力によって圧縮された状態となる。こ
の圧縮による熱と、セメントの水和反応時の熱とにより
、セメントの水和反応が促進されて固化時間が短縮され
、また、比較的比重の大きなセメント硬化部分等が収納
容器の外側近傍に集積状態となって、外側から固化が起
こって収納容器と一体化状態となる。この場合に、中央
部に比較的多く集積する流動性物質の回転が遅れる傾向
を示すことにより、回転方向の温度を均一化状態として
固化時間を短縮し、かつ、外側を速やかに固化させるこ
とによる取り扱い性の向上を図るものである。In this case, if centrifugal force is applied to the mixed contents,
The mixed contents are compressed by centrifugal force. The heat from this compression and the heat from the hydration reaction of the cement promote the hydration reaction of the cement, shortening the solidification time, and causing the hardened cement parts, etc., which have a relatively large specific gravity, to close to the outside of the storage container. It becomes an accumulated state, solidification occurs from the outside, and becomes integrated with the storage container. In this case, by showing a tendency for the rotation of the fluid substance that accumulates in a relatively large amount in the center to be delayed, it is possible to shorten the solidification time by equalizing the temperature in the rotation direction, and to quickly solidify the outside. The purpose is to improve ease of handling.
「実施例」
以下、第1図を参照して、本発明に係る放射性廃棄物焼
却灰のセメント固化方法の一実施例について説明する。"Example" Hereinafter, with reference to FIG. 1, an example of the method for solidifying radioactive waste incineration ash into cement according to the present invention will be described.
図中、符号Aは収納容器(例えばドラム缶)、lはター
ンテーブル、2は断熱性ケース、3は回転軸、4は電動
モータ等の回転駆動源、5・6は軸受け、7はボルト等
の締結具である。In the figure, symbol A is a storage container (for example, a drum), l is a turntable, 2 is a heat insulating case, 3 is a rotating shaft, 4 is a rotational drive source such as an electric motor, 5 and 6 are bearings, and 7 is a bolt, etc. It is a fastener.
放射性廃棄物を焼却処理して生成された焼却灰は、他種
類の放射性物質や酸化金属等を含む粉末状であるため、
セメント固化時の細骨材として利用される。The incineration ash produced by incinerating radioactive waste is in powder form containing other types of radioactive substances and metal oxides, etc.
Used as fine aggregate during cement solidification.
第1図に示すように、シリカセメント、アルミナセメン
ト等のいわゆる水硬性セメントに、焼却灰、必要に応じ
てS f OtSA Is Os等の適量の細骨材と水
とを混合する練り合わせた状態、または、収納容器Aに
、水、焼却灰を投入して混合させるとともに、セメント
等を投入して、概略練り合わせた状態にして充填した後
、蓋をして密封状態とする。As shown in Fig. 1, a mixture is prepared by mixing so-called hydraulic cement such as silica cement and alumina cement with incinerated ash and, if necessary, an appropriate amount of fine aggregate such as S f OtSA Is Os and water. Alternatively, water and incineration ash are put and mixed into the storage container A, and cement or the like is also put into the storage container A to roughly knead it and then filled, and then the container is covered and sealed.
次いで、これら焼却灰等の収納容器Aをターンテーブル
1の上に搭載するとともに、その上に断熱性ケース2を
被せて、締結具7によって収納容器Aをターンテーブル
lに固定し、第1図に示す状態とする。Next, the storage container A for incinerated ash, etc. is mounted on the turntable 1, and the heat insulating case 2 is placed on top of it, and the storage container A is fixed to the turntable 1 with the fastener 7, as shown in FIG. The condition shown is as follows.
回転駆動源4の作動により、ターンテーブルIを高速回
転させ、収納容器Aの内容物に遠心力を付与する。By operating the rotational drive source 4, the turntable I is rotated at high speed and centrifugal force is applied to the contents of the storage container A.
収納容器Aの内部においては、セメント鉱物と水との反
応により、凝結現象を生じるいわゆるセメントの水和作
用が起こり、凝結現象を生じるとともに、続いて硬化現
象が起こる。Inside the storage container A, a so-called hydration effect of cement occurs due to the reaction between the cement mineral and water, causing a setting phenomenon, and a hardening phenomenon subsequently occurs.
この場合に、収納容器Aの混合内容物に遠心力が付与さ
れると、水または流動物よりも相対的に比重の大きな物
質が、遠心力によって外側に集積させられる現象が生じ
、比重の大きな物質、つまり、大部分の混合内容物が遠
心力によって圧縮された状態となる。この圧縮による熱
と、セメントの水和反応時の婆とによって、セメントの
水和反応が促進されて固化時間が短縮されることが期待
される。そして、断熱性ケース2によって覆うことによ
り、大気中への放熱を低減する。In this case, when centrifugal force is applied to the mixed contents of storage container A, a phenomenon occurs in which substances with a relatively higher specific gravity than water or fluids are accumulated on the outside due to the centrifugal force. The substance, ie, most of the mixed contents, is compressed by centrifugal force. It is expected that the heat generated by this compression and the heat generated during the hydration reaction of the cement will accelerate the hydration reaction of the cement and shorten the solidification time. By covering with the heat insulating case 2, heat radiation into the atmosphere is reduced.
また、比重の大きな焼却灰を取り込んで固化し始めたセ
メント硬化部分、っまり固化槽Xは、他の流動性を有し
ている部分及び水よりも、相対的に比重が大きいために
、第2図に示すように、外ωり近傍に集積した状態とな
り、そして、固化槽Xが固化状態となることによって収
納容器Aの内周面に付着した一体化状態となると考えら
れる。In addition, the solidification tank As shown in FIG. 2, it is considered that the particles are accumulated near the outer periphery, and as the solidification tank X becomes solidified, the particles adhere to the inner circumferential surface of the storage container A and become integrated.
この場合に、収納容器Aの中央部に残されている流動性
を有する部分、つまり流動相Yは、その流動性に基づい
て、固化槽Xよりも回転が遅れる傾向を示すことにより
、流動性を有する部分に対流現象が生じて、回転方向の
温度を均一化することと、回転方向のずれにより発熱す
ることとが起こる。このため、セメント固化が速やかに
行なわれるものとなる。In this case, the part with fluidity remaining in the center of storage container A, that is, the fluid phase Y, shows a tendency to rotate later than the solidification tank X based on its fluidity. A convection phenomenon occurs in a portion having a rotation direction, which equalizes the temperature in the rotation direction, and generates heat due to a deviation in the rotation direction. Therefore, the cement hardens quickly.
一方、第2図に示すように、収納容器Aの内部において
、収納容器Aの壁と一体化した状態の固化槽Xが徐々に
形成されるが、その厚さが十分なものとなると、その後
に収納容器Aの内部中央部が、セメントの水和反応によ
って固化状態に導かれる場合においても、固化むらや偏
心等が起こりにくくなるために、固化工程の途中におい
て運搬や貯蔵庫への保管等を行ない得るものとなり、遠
隔操縦による取り扱い性の向上が図られることになる。On the other hand, as shown in Fig. 2, a solidification tank X is gradually formed inside the storage container A, which is integrated with the wall of the storage container A. Even when the center of the interior of storage container A is brought to a solidified state by the hydration reaction of cement, it is difficult to cause uneven solidification or eccentricity, so transport or storage in storage during the solidification process is not recommended. This will improve the ease of handling through remote control.
「発明の効果」
以上説明したように、本発明に係る放射性廃棄物焼却灰
のセメント固化方法は、焼却灰を収納容器に収納してセ
メント固化する場合に、水、焼却灰、水硬性セメント等
を収納密封した状態で、高速回転させて遠心力を付与し
ながら固化させるものであるから、圧縮による発熱、セ
メントの水和反応熱、固化途中における固化槽と流動相
との回転方向のずれによる発熱等を利用して、速やかに
凝結硬化状態に導いて固化時間を短縮することができる
。"Effects of the Invention" As explained above, the method for solidifying radioactive waste incineration ash into cement according to the present invention, when storing incineration ash in a storage container and solidifying it with cement, water, incineration ash, hydraulic cement, etc. Since it is stored in a sealed state and solidified while rotating at high speed and applying centrifugal force, it is caused by heat generation due to compression, heat of hydration reaction of cement, and misalignment of the direction of rotation between the solidification tank and the fluid phase during solidification. By utilizing heat generation or the like, the solidification time can be shortened by quickly leading to a solidification and hardening state.
また、固化槽が流動相より外側に位置して、収納容器と
より速く一体化状態となるので、短時間で運搬や保管等
の取り扱い性を得て、セメント固化のための放射性物質
の滞貨量を低減することができる等の効果を奏する。In addition, since the solidification tank is located outside the fluid phase and becomes integrated with the storage container more quickly, it becomes easier to handle for transportation and storage in a short time, and the radioactive materials for cement solidification are stored. This has effects such as being able to reduce the amount.
第1図は本発明に係る放射性廃棄物焼却灰のセメント固
化方法の一実施例を示す一部を断面した正面図、第2図
はセメント固化途中の状態を示す第1図の鎖線■−■線
矢視図である。
A・・・・・・収納容器(ドラム缶
1・・・・・ターンテーブル、
2・・・・・・断熱性ケース、
3・・・・・・回転軸、
4・・・・・・回転駆動源、
5・・・・・・軸受け、
6・・・・・・軸受け、
7・・・・・・締結具、
X・・・・・・固化槽、
Y・・・・・流動相。
)、Fig. 1 is a partially sectional front view showing an embodiment of the cement solidification method for radioactive waste incineration ash according to the present invention, and Fig. 2 is a chain line in Fig. 1 showing a state in the middle of cement solidification. It is a line arrow view. A...Storage container (drum 1...Turntable, 2...Insulating case, 3...Rotating shaft, 4...Rotating drive source, 5...bearing, 6...bearing, 7...fastener, X...solidification tank, Y...fluid phase.) ,
Claims (1)
メント、アルミナセメント等の水硬性セメントとを充填
して密封し、該密封した収納容器を高速回転させること
により、混合内容物に遠心力を付与して圧縮状態とする
とともに、セメントの水和反応熱によって内容物を加熱
して、凝結硬化状態に導くことを特徴とする放射性廃棄
物焼却灰のセメント固化方法。A storage container is filled with water, radioactive waste incineration ash, and hydraulic cement such as silica cement or alumina cement and sealed, and the sealed storage container is rotated at high speed to apply centrifugal force to the mixed contents. 1. A method for solidifying radioactive waste incineration ash into cement, the method comprising: applying heat to compress the contents, and heating the contents using the heat of hydration reaction of the cement to bring the contents into a solidified and hardened state.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP32224089A JPH03181899A (en) | 1989-12-12 | 1989-12-12 | Cement solidification of cinder ash of radioactive waste |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP32224089A JPH03181899A (en) | 1989-12-12 | 1989-12-12 | Cement solidification of cinder ash of radioactive waste |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH03181899A true JPH03181899A (en) | 1991-08-07 |
Family
ID=18141482
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP32224089A Pending JPH03181899A (en) | 1989-12-12 | 1989-12-12 | Cement solidification of cinder ash of radioactive waste |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH03181899A (en) |
-
1989
- 1989-12-12 JP JP32224089A patent/JPH03181899A/en active Pending
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