JPS59200999A - Method of melting and solidifying incineration ash of radioactive waste - Google Patents

Method of melting and solidifying incineration ash of radioactive waste

Info

Publication number
JPS59200999A
JPS59200999A JP7383983A JP7383983A JPS59200999A JP S59200999 A JPS59200999 A JP S59200999A JP 7383983 A JP7383983 A JP 7383983A JP 7383983 A JP7383983 A JP 7383983A JP S59200999 A JPS59200999 A JP S59200999A
Authority
JP
Japan
Prior art keywords
melting
furnace body
radioactive waste
ash
reservoir
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
JP7383983A
Other languages
Japanese (ja)
Inventor
一郎 菅原
岳 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.)
JGC Corp
Original Assignee
JGC 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 JGC Corp filed Critical JGC Corp
Priority to JP7383983A priority Critical patent/JPS59200999A/en
Publication of JPS59200999A publication Critical patent/JPS59200999A/en
Pending legal-status Critical Current

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  • 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】 本発明は、放射性廃棄物の焼却灰の溶融固化方法に関し
、詳しくは、放射性廃棄物の焼却灰を誘導加熱炉を用い
溶融固化するに際し、炉体として発熱体となる黒鉛を使
用し、焼却灰を減容溶融固化する溶融固化方法に関する
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for melting and solidifying incinerated ash of radioactive waste, and more specifically, when incinerating radioactive waste ash is melted and solidified using an induction heating furnace, the furnace body serves as a heating element. This invention relates to a method of melting and solidifying incinerated ash to reduce its volume using graphite.

従来、放射性廃棄物は焼却炉において焼却し減容処理し
た後に、容器等に貯蔵して廃棄処理するのが通常行なわ
れる処理方法であるが、焼却灰のみをドラム罐等の貯蔵
容器に単独で貯蔵する場合には、焼却灰の輸送中に飛散
しやすいのみならず、焼却灰が水溶性のため貯蔵時に耐
浸出性が極めて劣り、また熱伝導性が低いために放射性
元素の崩壊時の温度上昇の際に容器が破損しやすく、長
期の貯蔵安定性を欠いていた。さらには貯蔵時の容器内
の密度が小さいために焼却灰を多量に処理することがで
きない等の欠点もある。
Conventionally, radioactive waste has been incinerated in an incinerator to reduce its volume, and then stored in containers for disposal. When storing incinerated ash, it is not only easy to scatter during transportation, but also because incinerated ash is water-soluble, it has extremely poor leaching resistance during storage, and also has low thermal conductivity, so the temperature at which radioactive elements decay The container was easily damaged during ascent and lacked long-term storage stability. Furthermore, there are also disadvantages such as the inability to process a large amount of incinerated ash because the density inside the container during storage is low.

これらの欠点を補うためには、焼却灰を固化する方法が
有効であり、例えば (1)セメント固化法、(2)アスファルト固化法が提
案されている。しかし、このセメント固化法はセメント
を多量に用いるl〔め増量が著しく減容率に劣り、また
耐浸出性に劣る。一方、アスファルト同化法は成る程度
減容されるものの耐火性、強度面に問題がある。次いで
近年になってセメント同化法、アスファルト固化法に代
る固化法として、(3〕プラスチツク同化法、(4〕ガ
ラス同化法、(5)セラミック同化法および(6)マイ
クロ波同化法等の方法が提案されている。このうちガラ
ス同化法、セラミック同化法、マイクロ波同化法は焼却
灰を溶融固化する方法であり、セメント同化法の欠点を
成る程度解消するものであるが、これらの溶融同化法で
は溶融炉で焼却灰を溶融し、これを取り出すときに傾動
装置を用いて炉体を傾けて他の容器に移すためにかなり
時間を浪費し、また装置が大がかりになるため電力や作
業空間を必要とするので、経済性および作業性に問題が
あった。また、ガラス固化法、セラミック固化法にあっ
ては、発熱体が金属性であるためできるだけ低温で溶融
しなければならず、そのために融点降下剤を入れるので
、固化物の吊が増え減容率に若干劣るといった欠点があ
る。他方、マイクロ波溶融法は焼却灰中に金属や未燃カ
ーボン等の導電体が含まれていると、放電して加熱でき
ず、このためこれら導電体を除去しな番プれば溶融がで
きないという問題があり、作業工程が繁雑となってしま
う。
In order to compensate for these drawbacks, methods of solidifying incinerated ash are effective, and for example, (1) cement solidification method and (2) asphalt solidification method have been proposed. However, this cement solidification method uses a large amount of cement, so the volume increase is significantly inferior to the volume reduction rate, and the leaching resistance is inferior. On the other hand, although the asphalt assimilation method reduces the volume to some extent, there are problems with fire resistance and strength. Then, in recent years, methods such as (3) plastic assimilation method, (4) glass assimilation method, (5) ceramic assimilation method, and (6) microwave assimilation method have been introduced as solidification methods to replace cement assimilation method and asphalt solidification method. Among these methods, the glass assimilation method, ceramic assimilation method, and microwave assimilation method are methods that melt and solidify incinerated ash, and eliminate to some extent the drawbacks of the cement assimilation method. In this method, the incinerated ash is melted in a melting furnace, and when the ash is taken out, a tilting device is used to tilt the furnace body and transfer it to another container, which wastes a considerable amount of time.In addition, the equipment is large-scale, so it consumes electricity and work space. In addition, in the vitrification method and ceramic solidification method, since the heating element is metallic, it must be melted at the lowest possible temperature. Since a melting point depressant is added to the incineration ash, there is a disadvantage that the volume reduction rate is slightly inferior due to the increase in the amount of solidified material.On the other hand, the microwave melting method has the disadvantage that the incineration ash contains conductors such as metals and unburned carbon. Therefore, there is a problem that heating cannot be performed by discharging, and therefore, unless these conductors are removed, melting cannot be performed, which makes the work process complicated.

本発明は上記の問題点を解決すべくなされたもので、焼
却灰の減容焼却同化能力を増加させると共に、装置の小
型化を図ることによって作業性、経済性に優れた放射性
廃棄物の焼却灰の溶融同化方法を提供することを目的と
する。
The present invention has been made in order to solve the above-mentioned problems, and in addition to increasing the volume reduction incineration and assimilation capacity of incinerated ash, it also improves the efficiency and economy of radioactive waste incineration by reducing the size of the device. The purpose is to provide a method for melting and assimilating ash.

本発明者らは上記目的に沿って検討の結果、誘導加熱炉
によって放射性廃棄物の焼却灰を溶融固化するに際し、
誘導加熱炉の炉体として黒鉛を用い、かつ該黒鉛を発熱
体とすることにより、上記目的が達成されることを見出
し本発明に到達した。
As a result of studies in line with the above objectives, the present inventors found that when melting and solidifying radioactive waste incineration ash using an induction heating furnace,
The inventors have discovered that the above object can be achieved by using graphite as the furnace body of an induction heating furnace and using the graphite as a heating element, and have arrived at the present invention.

ザなわら本発明は、放射性廃棄物の焼却灰を誘導加熱炉
によって溶融固化するに際し、炉体として発熱体となる
黒鉛を使用したことを特徴とし、さらには該炉体の中空
部の下部または底部に溜部を設け、該溜部は中心に位置
する取出孔に向かって傾斜を有し、該取出孔はス1〜ツ
バ−を嵌合することにより閉塞され、炉体に投入された
焼却灰は該溜部で溶融され、所望量となったとき、該ス
トッパーを引き上げ該取出孔を開口せしめることにより
、溶融物を該炉体の下方の容器に回収することを特徴と
する焼却灰の溶融同化方法にある。
The present invention is characterized in that graphite, which serves as a heating element, is used as the furnace body when incineration ash of radioactive waste is melted and solidified in an induction heating furnace, and further, the lower part of the hollow part of the furnace body or A reservoir is provided at the bottom, and the reservoir has an inclination toward the take-out hole located in the center, and the take-out hole is closed by fitting the tabs 1 to 2, and the incineration put into the furnace body is closed. The ash is melted in the reservoir, and when the desired amount is reached, the stopper is pulled up to open the take-out hole, and the molten material is collected into a container below the furnace body. In the melt assimilation method.

以下、図面を用いて本発明を具体的に説明する。Hereinafter, the present invention will be specifically explained using the drawings.

第1図は、本発明の一実施例に係わる溶融固化プロセス
の概略図であり、第2図は本発明の他の実施例に係わる
炉体部分の拡大断面図である。
FIG. 1 is a schematic diagram of a melting and solidifying process according to one embodiment of the present invention, and FIG. 2 is an enlarged sectional view of a furnace body portion according to another embodiment of the present invention.

第1図において、放射性廃棄物の焼却灰1は、焼却灰ポ
ツパー2に一時的に蓄えられ、焼却灰1は適宜に焼却灰
供給管3中を通って高周波誘導加熱炉4中の中空状の黒
鉛からなる炉体5底部の溜部6に供給される。溜部6に
は、その中心に取出7L 7が設けられており、溜部6
は取出孔7に向って傾斜を有している。そして取出孔7
にはストッパー昇降m8等の移送手段により昇降するス
トッパー9の先端が嵌合され、取出孔7を閉塞した状態
としている。焼却灰1が炉体5の溜部6に所望量満され
ると、高周波誘導加熱炉4は高周波電源10により加熱
され、黒鉛からなる炉体5は発熱体として機能し、焼却
灰1は溶融固化し溶融物11となる。焼却灰1が完全に
溶融物11になると適宜にストッパー昇降機8によって
ストッパー9が引き上げられ、取出孔7は開口し、溶融
物11が取出孔7から自重にてキャニスタ12内に落下
して冷却固化する。第2図においては、溜部6は炉体5
のやや下部に位置しており、炉体5内の溜部6の位置は
焼却灰1を所望量満たせればよく、特に制限はうけない
が、経済的に処理することを考慮すると下部または底部
であり、好ましくは底部である。また、取出孔7は第2
図に示されているように、ストッパー9の先端と好適に
嵌合するように傾斜を有することが望ましい。溶融物1
1が全てキャニスタ12に落下すると、ストッパー昇降
機8が下降し、取出孔7にストッパー9の先端が再び嵌
合し、取出孔7が閉塞され、焼却灰供給管3より新たな
焼却灰が炉体5の溜部6に満たされ、キャニスタ12が
冷N1された溶融物11で一杯になるまで繰り返し溶融
固化される。
In FIG. 1, incinerated ash 1 of radioactive waste is temporarily stored in an incinerated ash popper 2, and the incinerated ash 1 is appropriately passed through an incinerated ash supply pipe 3 to a hollow-shaped high-frequency induction heating furnace 4. It is supplied to a reservoir 6 at the bottom of the furnace body 5 made of graphite. The reservoir 6 is provided with a takeout 7L 7 at its center.
has an inclination toward the extraction hole 7. and extraction hole 7
The distal end of the stopper 9 which is raised and lowered by a transfer means such as a stopper raising/lowering m8 is fitted to close the extraction hole 7. When the desired amount of incinerated ash 1 is filled in the reservoir 6 of the furnace body 5, the high-frequency induction heating furnace 4 is heated by the high-frequency power supply 10, the furnace body 5 made of graphite functions as a heating element, and the incinerated ash 1 is melted. It solidifies to become a melt 11. When the incinerated ash 1 completely becomes the molten material 11, the stopper 9 is appropriately lifted up by the stopper elevator 8, the extraction hole 7 is opened, and the molten material 11 falls from the extraction hole 7 under its own weight into the canister 12, where it cools and solidifies. do. In FIG. 2, the reservoir 6 is the furnace body 5.
The position of the reservoir 6 in the furnace body 5 is not particularly limited as long as it can fill the desired amount of incinerated ash 1, but in consideration of economical processing, it may be located at the lower part or the bottom. , preferably at the bottom. Moreover, the extraction hole 7 is the second
As shown in the figure, it is desirable to have a slope so as to suitably fit with the tip of the stopper 9. Melt 1
1 falls into the canister 12, the stopper elevator 8 descends, the tip of the stopper 9 refits into the take-out hole 7, the take-out hole 7 is closed, and new incinerated ash flows from the incinerated ash supply pipe 3 into the furnace body. 5 is filled, and the canister 12 is repeatedly melted and solidified until it is filled with the cold N1 melt 11.

キャニスタ12が一杯になると、移動装置13により固
化された溶融物11は貯蔵場所に運ばれドラム罐等の貯
蔵容器14に貯蔵される。発生した廃ガスは廃ガス管1
5より取り出され、必要なら焼却炉の廃ガス処理系で処
理され放射線が除去される。
When the canister 12 is full, the solidified melt 11 is transported by the transfer device 13 to a storage location and stored in a storage container 14 such as a drum can. The generated waste gas is transferred to waste gas pipe 1.
5 and, if necessary, processed in the waste gas treatment system of the incinerator to remove radiation.

以上のように、本発明では炉体の溜部に取出孔を設けて
あり、しかも溜部は取出孔に向かって傾斜が設けである
ために、ストッパーを上下するだけで自重で下方に設け
られたキャニスタに落下し冷却同化するので、連続的処
理が可能となることから焼却灰の処理能力が向上すると
共に、加熱溶融炉の設備が必要最小限に縮小され、経済
性、作業性に優れた溶融同化方法を提供することができ
る。また、本発明では誘導加熱炉を用いているために、
前処理として小金属片や未燃カーボン等の導電体を取り
除くという工程が不要である。さらには、本発明では発
熱体として黒鉛を用いていることから、発熱体として金
属を用いたガラス同化法等に比して高い温度で加熱処理
が可能であり、しかも炉体が消耗し使用不能となった際
はそのまま焼却することができるので新たな廃棄物を発
生しないという利点もある。
As described above, in the present invention, the take-out hole is provided in the reservoir of the furnace body, and since the reservoir is inclined toward the take-out hole, the stopper can be moved downward by its own weight simply by moving the stopper up and down. Since the ash falls into a canister and is cooled and assimilated, continuous processing is possible, which improves the processing capacity of incinerated ash, and reduces the heating and melting furnace equipment to the minimum necessary, making it highly economical and workable. A melt assimilation method can be provided. In addition, since the present invention uses an induction heating furnace,
There is no need for a pre-treatment step to remove conductors such as small metal pieces and unburned carbon. Furthermore, since graphite is used as the heating element in the present invention, heat treatment can be performed at a higher temperature than in glass assimilation methods that use metal as the heating element, and the furnace body is consumed and becomes unusable. When this occurs, it can be incinerated as is, which has the advantage of not generating new waste.

従って本発明は、放射性廃棄物の焼却灰の溶融固化方法
として好適に利用される。
Therefore, the present invention is suitably used as a method for melting and solidifying incineration ash of radioactive waste.

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

第1図は、本発明の一実施例に係わる溶融同化プロセス
の概略図、および 第2図は本発明の他の実施例に係わる炉体部分の拡大断
面図。 1:焼却灰、   2:焼却灰ホッパー、3:焼却灰供
給管、4:高周波誘導加熱炉、5:炉体、    6:
溜部、 7二取出孔、   8:ストッパー昇liI機、9ニス
1−ツバ−110:高周波電源、11:溶融物、 12
:キャニスタ、 13:移動装置、14:貯蔵容器、 15:廃ガス管。 特許出願人 日 揮 株 式 会 社 代理人 弁理士 伊 東 辰 雄 代理人 弁理士 伊 東 哲 也
FIG. 1 is a schematic diagram of a melting assimilation process according to one embodiment of the present invention, and FIG. 2 is an enlarged sectional view of a furnace body portion according to another embodiment of the present invention. 1: Incineration ash, 2: Incineration ash hopper, 3: Incineration ash supply pipe, 4: High frequency induction heating furnace, 5: Furnace body, 6:
Reservoir part, 72 extraction holes, 8: Stopper lift machine, 9 Varnish 1-Brim 110: High frequency power supply, 11: Melt, 12
: Canister, 13: Transfer device, 14: Storage container, 15: Waste gas pipe. Patent Applicant JGC Corporation Company Agent Patent Attorney Tatsuo Ito Agent Patent Attorney Tetsuya Ito

Claims (1)

【特許請求の範囲】 1、放射性廃棄物の焼却灰を誘導加熱炉によって溶融固
化するに際し、炉体として発熱体となる黒鉛を使用した
ことを特徴とする焼却灰の溶融同化方法。 2、放射性廃棄物の焼却灰を誘導加熱炉によって溶融固
化するに際し、炉体として発熱体となる中空状の黒鉛を
使用し、該炉体の中空部の下部または底部に溜部を設け
、該溜部は中心に位置する取出孔に向かって傾斜を有し
、該取出孔はストッパーを嵌合することにより閉塞され
、炉体に投入された焼却灰は該溜部で溶融され、所望m
となったとき、該ストッパーを引き上げ該取出孔を開口
せしめることにより、溶融物を該炉体の下方の容器に回
収することを特徴とする焼却灰の溶融固化方法。
[Claims] 1. A method for melting and assimilating radioactive waste incineration ash, characterized in that graphite serving as a heating element is used as a furnace body when melting and solidifying incineration ash of radioactive waste in an induction heating furnace. 2. When incineration ash of radioactive waste is melted and solidified in an induction heating furnace, a hollow graphite which serves as a heating element is used as the furnace body, and a reservoir is provided at the bottom or bottom of the hollow part of the furnace body. The reservoir has an inclination toward the take-out hole located at the center, and the take-out hole is closed by fitting a stopper, and the incinerated ash introduced into the furnace body is melted in the reservoir to the desired m
A method for melting and solidifying incinerated ash, characterized in that when the stopper is pulled up to open the extraction hole, the molten material is collected in a container below the furnace body.
JP7383983A 1983-04-28 1983-04-28 Method of melting and solidifying incineration ash of radioactive waste Pending JPS59200999A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7383983A JPS59200999A (en) 1983-04-28 1983-04-28 Method of melting and solidifying incineration ash of radioactive waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7383983A JPS59200999A (en) 1983-04-28 1983-04-28 Method of melting and solidifying incineration ash of radioactive waste

Publications (1)

Publication Number Publication Date
JPS59200999A true JPS59200999A (en) 1984-11-14

Family

ID=13529705

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7383983A Pending JPS59200999A (en) 1983-04-28 1983-04-28 Method of melting and solidifying incineration ash of radioactive waste

Country Status (1)

Country Link
JP (1) JPS59200999A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61210998A (en) * 1985-03-15 1986-09-19 日本碍子株式会社 Continuous melter for waste
JPS61226699A (en) * 1985-04-01 1986-10-08 日揮株式会社 Melting treatment reactor for miscellaneous waste
JPS61246513A (en) * 1985-04-24 1986-11-01 Jgc Corp Melt vessel and melt treating method for miscellaneous wastes using it

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5326505A (en) * 1976-08-24 1978-03-11 Nippon Telegr & Teleph Corp <Ntt> Voice rec ognizing device
JPS57169592A (en) * 1981-04-10 1982-10-19 Nippon Mining Co Flow rate regulation of molten metal
JPS5847300A (en) * 1981-09-16 1983-03-18 株式会社東芝 Method and apparatus for solidifying radioactive waste by ceramics

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5326505A (en) * 1976-08-24 1978-03-11 Nippon Telegr & Teleph Corp <Ntt> Voice rec ognizing device
JPS57169592A (en) * 1981-04-10 1982-10-19 Nippon Mining Co Flow rate regulation of molten metal
JPS5847300A (en) * 1981-09-16 1983-03-18 株式会社東芝 Method and apparatus for solidifying radioactive waste by ceramics

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61210998A (en) * 1985-03-15 1986-09-19 日本碍子株式会社 Continuous melter for waste
JPS61226699A (en) * 1985-04-01 1986-10-08 日揮株式会社 Melting treatment reactor for miscellaneous waste
JPS61246513A (en) * 1985-04-24 1986-11-01 Jgc Corp Melt vessel and melt treating method for miscellaneous wastes using it

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