JPS60122397A - Volume decreasing treating method of radioactive waste - Google Patents

Volume decreasing treating method of radioactive waste

Info

Publication number
JPS60122397A
JPS60122397A JP22909183A JP22909183A JPS60122397A JP S60122397 A JPS60122397 A JP S60122397A JP 22909183 A JP22909183 A JP 22909183A JP 22909183 A JP22909183 A JP 22909183A JP S60122397 A JPS60122397 A JP S60122397A
Authority
JP
Japan
Prior art keywords
waste
radioactive
glass
incineration
volume
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
JP22909183A
Other languages
Japanese (ja)
Inventor
佐藤 広栄
山内 典之
平山 俊彦
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 Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries 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 Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP22909183A priority Critical patent/JPS60122397A/en
Priority to EP84303715A priority patent/EP0155418A3/en
Priority to CA000457495A priority patent/CA1230221A/en
Publication of JPS60122397A publication Critical patent/JPS60122397A/en
Pending legal-status Critical Current

Links

Classifications

    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21FPROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
    • G21F9/00Treating radioactively contaminated material; Decontamination arrangements therefor
    • G21F9/28Treating solids
    • G21F9/30Processing
    • G21F9/301Processing by fixation in stable solid media
    • G21F9/302Processing by fixation in stable solid media in an inorganic matrix
    • G21F9/305Glass or glass like matrix
    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21FPROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
    • G21F9/00Treating radioactively contaminated material; Decontamination arrangements therefor
    • G21F9/28Treating solids
    • G21F9/30Processing
    • G21F9/308Processing by melting the waste

Landscapes

  • Physics & Mathematics (AREA)
  • Engineering & Computer Science (AREA)
  • General Engineering & Computer Science (AREA)
  • High Energy & Nuclear Physics (AREA)
  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • 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、原子力発電所等放射性物質扱い施設からの放
射性廃棄物の合目的な減容化処理方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for purposefully reducing the volume of radioactive waste from facilities handling radioactive materials such as nuclear power plants.

原子力発電所等原子力施設から発生する放射性排ガス以
外の放射性廃棄物としては、放射性廃液、可燃性固体廃
棄物(例えば衣類、紙、木材等可燃性雑固体、空調系活
性炭類、使用済イオン交換樹脂、廃油等)、及び不燃性
固体廃棄物(例えばグラスウール、金属部品、その他)
等がある。
Radioactive waste other than radioactive exhaust gas generated from nuclear facilities such as nuclear power plants includes radioactive liquid waste, combustible solid waste (e.g., combustible miscellaneous solids such as clothing, paper, and wood, activated carbon from air conditioning systems, and used ion exchange resin). , waste oil, etc.), and non-flammable solid waste (e.g. glass wool, metal parts, etc.)
etc.

従来、放射性廃棄物の?!I埋的・化学的性質を利用し
て、濃縮、乾燥、燻焼、焼却あるいは圧縮等積々の減容
処理を行ない、さらにアスファルト固化脅セメント固化
等種々の固化処理を施こし、固化体として貯蔵している
Traditionally, radioactive waste? ! I Utilizing the burial and chemical properties, we perform volume reduction treatments such as concentration, drying, smoking, incineration, or compression, and then perform various solidification treatments such as asphalt solidification, cement solidification, etc. It is stored.

例えば放射性廃液については、化学反応により放射性物
質を難治性として分離乾燥したり、鎖線したり、揮発性
成分については収部により減容する。又、可燃性固体廃
棄物については一般的に焼却により減容する。不燃性固
体廃棄物については圧縮減容が行われる。
For example, in the case of radioactive waste liquid, the radioactive substances are separated and dried by chemical reaction to make them refractory, or the volume of volatile components is reduced by a collection section. Additionally, combustible solid waste is generally reduced in volume by incineration. For non-combustible solid waste, compression volume reduction is carried out.

このような処理は廃棄物の種類により個別的に行われて
いて、いずれの場合においても減容効率の向上と同化体
の安定性がめられている。
Such treatment is carried out individually depending on the type of waste, and in each case, the aim is to improve volume reduction efficiency and stabilize the assimilate.

しかし、上記の種々の減容処理による生成物を安定に固
化するために、同化に際して種々の添加物が加えられ増
量すること、また空調系から廃棄されるエア・フィルタ
のグラスファイバは不燃性であり従来の圧縮処理では減
容効率が十分なものではないこと等から、従来の減容処
理方法では、年々廃棄物貯賊慮を増大させているので、
早急な対策がめられていた。
However, in order to stably solidify the products from the various volume reduction treatments mentioned above, various additives are added during assimilation to increase the volume, and the glass fibers of air filters discarded from air conditioning systems are nonflammable. However, due to the fact that the volume reduction efficiency of conventional compression treatment is not sufficient, the problem of waste storage is increasing year by year with conventional volume reduction treatment methods.
Immediate measures were required.

本発明は上記の不具合点を解決し、効率のよい減容と、
非常に安定した固化体を得る放射性廃棄物の処理方法を
提供することを目的とするものである。
The present invention solves the above-mentioned problems and achieves efficient volume reduction,
The purpose of this invention is to provide a method for treating radioactive waste that yields a highly stable solidified material.

本発明省らは、放射性廃棄物のうちの廃液及び可燃性固
体廃棄物を、乾燥、燻焼、焼却等して得た生成物(以下
焼却等生成物という)と、放射能汚染した廃棄グラス・
ファイバを適当比率にて混合し、瘍融炉中で一体化して
安定な固化体を得ることを考えつき、本発明に到った。
The Ministry of the Invention and others have identified products obtained by drying, smoking, incinerating, etc. waste liquid and combustible solid waste of radioactive waste (hereinafter referred to as incineration products) and radioactively contaminated waste glass.・
We came up with the idea of mixing fibers in an appropriate ratio and integrating them in a melting furnace to obtain a stable solidified product, and thus arrived at the present invention.

すなわち、本発明の要旨とするところは、原子力施設か
ら発生する放射性廃液および可燃性固体廃棄物を、乾燥
、燻焼、焼却などにより処理して得た放射性物質を含有
する生成物と、放射性物質が付増している廃棄ガラス・
ファイバを適当な比率で混合し、加熱溶解して一体化し
た安定同化体とすることを特徴とする放射性廃棄物の減
容化処理方法にある。
That is, the gist of the present invention is to provide products containing radioactive materials obtained by processing radioactive liquid waste and combustible solid waste generated from nuclear facilities by drying, smoking, incineration, etc. Waste glass with added
A method for reducing the volume of radioactive waste is characterized in that fibers are mixed in an appropriate ratio and heated and melted to form an integrated stable assimilate.

以下図にもとすいて本発明の詳細な説明する。The present invention will be explained in detail below with reference to the drawings.

第1図は本発明方法の一笑施態様例のフローを示す。FIG. 1 shows the flow of one embodiment of the method of the present invention.

第1図において、1は溶融炉、2は焼却等生成物容器、
2−1は焼却等生成物切出装置、2−2は切出装置2−
1の設定器、3,4及び5はそれぞれ種類の異なる廃棄
グラスファイバ用の容器、5−1.4−1及び5−1は
夫々の容器5S5に入っている廃棄グラスファイバの切
出装部、6は溶融炉から排出された溶融体を捕集する装
置である。
In FIG. 1, 1 is a melting furnace, 2 is an incineration product container,
2-1 is an incineration product cutting device, 2-2 is a cutting device 2-
1 setter, 3, 4, and 5 are containers for different types of waste glass fibers, and 5-1.4-1 and 5-1 are cutting parts for the waste glass fibers contained in the respective containers 5S5. , 6 is a device for collecting the melt discharged from the melting furnace.

焼却等生成物は灰状の粉体であり、一方廃棄グラスーフ
ァイバは繊維状固化体である。この両者を適当な比率で
混合し溶融炉1へ投入する方法としては、どちらを変え
ても適当な比率を得られるが、こ〜では廃棄グラス・フ
ァイバの童を基準として焼却等生成物の量を変えて行う
方法について説明する。
The incineration product is an ash-like powder, while the waste glass fiber is a fibrous solidified material. As for the method of mixing these two in an appropriate ratio and feeding them into the melting furnace 1, an appropriate ratio can be obtained by changing either of them, but in this case, the amount of incineration products is calculated based on the amount of waste glass fiber. We will explain how to do this by changing the .

なお、廃棄グラス・ファイバの成分は、それぞれ製品の
種類により異るので同一成分のものを集めて処理した方
がより安定化した同化体を得るので、図の如く6種類ま
で示したがこれに限定されるものではなく、任意の種類
徐とすることができる。
The components of waste glass fiber differ depending on the type of product, so it is better to collect and process products with the same components to obtain a more stable assimilated product. It is not limited to this and can be of any type.

ここで一般的な焼却等生成物の成分の1例を第1表に示
す。
Table 1 shows an example of the components of common incineration products.

第1表は加圧水型原子炉(PWR)の■焼生成物及び可
燃性雑固体の焼却生成物の成分を重量%にて示すもので
ある。
Table 1 shows the components of the incineration products of the pressurized water reactor (PWR) and the incineration products of combustible miscellaneous solids in weight percent.

第1表 なお、放射性廃液な減容のために■焼すると揮発しない
放射能物質を含む各種の金属酸化物が主体の集合体とな
る。例えばPWR発電所の場合ではホウFRBが主成分
となり、またBWR発電所ではNa が主成分となる。
Table 1 Note that in order to reduce the volume of radioactive waste liquid, it becomes an aggregate mainly of various metal oxides containing radioactive substances that do not volatilize when burned. For example, in the case of a PWR power plant, Hou FRB is the main component, and in the case of a BWR power plant, Na is the main component.

また、グラスクールの組成としてEガラスの代表的なも
のの一例を第2表に示す。
Further, Table 2 shows an example of a typical E glass composition as a glass coolant composition.

第2表 説明を簡略化するため、廃棄グラス・ファイバ容器3を
使用した場合の説明を行う。先ず廃棄グラス・ファイバ
切出装置3−1によりある量の廃棄グラス・ファイバを
溶融炉1に投入する。次に焼却等生成物の切出設定器2
−2を操作することにより、廃棄グラス・ファイバ容器
5のグラス・ファイバの成分と量に最適量の焼却等生成
物を混入する。
In order to simplify the explanation of Table 2, the case where the waste glass fiber container 3 is used will be explained. First, a certain amount of waste glass fiber is introduced into the melting furnace 1 by the waste glass fiber cutting device 3-1. Next, the cut-out setting device 2 for the products of incineration, etc.
-2, the composition and amount of glass fiber in the waste glass fiber container 5 are mixed with an optimum amount of products such as incineration.

溶融炉1内に混入された両者は、廃棄グラス−ファイバ
が溶解する温度まで加熱される。この場合、両者に付着
したり含まれている各種成分のうち、廃棄グラス・ファ
イバの融点より高い金属および金属酸化物は、粒状等の
固形物として溶液の中に存在するが、可燃物は燃焼し、
全体として最大の減容率を有するガラス状の生成物がで
きる。また、グラス中ファイバの融点より高い金属およ
び金属酸化物が溶解する温度まで加熱すると、グラス・
ファイバとこれ等金属および金属酸化物が溶は合い、分
子構造的に結合されて、より安定化したガラス状の生成
物ができる。
Both materials mixed into the melting furnace 1 are heated to a temperature at which the waste glass fibers are melted. In this case, among the various components attached to or contained in both, metals and metal oxides with a temperature higher than the melting point of the waste glass fiber exist in the solution as solid substances such as particles, but combustible substances are combustible. death,
A glassy product with the highest overall volume reduction is formed. In addition, when heated to a temperature that melts metals and metal oxides that are higher than the melting point of the fiber in the glass, the glass
The fibers and these metals and metal oxides are fused together and molecularly bonded to create a more stabilized glass-like product.

溶融が終ると溶融炉1から溶融体捕集容器6に移され、
冷却されて放射能、金属、金属酸化物等を密封した同化
体を得る。あるいは、溶融体捕集容器6に移さないで、
溶融炉1の中で冷却固化した後に同化体として取出すこ
ともできる。
When the melting is finished, it is transferred from the melting furnace 1 to the melt collection container 6,
It is cooled to obtain an assimilate containing radioactivity, metals, metal oxides, etc. Alternatively, without transferring to the melt collection container 6,
It can also be taken out as an assimilate after being cooled and solidified in the melting furnace 1.

上述の方法において、廃棄グラスウールと焼却等生成物
の好ましい混合比率としては、例えば、第1表の■を2
0%グラス・ウールを80%(W、T0%)混合し約1
,400℃加熱溶融する。
In the above method, the preferred mixing ratio of waste glass wool and incineration products is, for example, 2 in Table 1.
Mix 80% (W, T0%) of 0% glass wool and make approximately 1
, heated and melted at 400℃.

得られた生成物の組成は次のとおりであった。The composition of the obtained product was as follows.

sio□ B203A1203NIL20.CILOそ
の他46.9 18.7 11.6 0.9 14.8
 7.1この生成物は、通常のホウ珪酸ガラスの固化体
であり、常温では強度、安定性、耐久性および(注)耐
滲出性がある。
sio□ B203A1203NIL20. CILO Others 46.9 18.7 11.6 0.9 14.8
7.1 This product is a solidified body of ordinary borosilicate glass, and has strength, stability, durability, and (note) oozing resistance at room temperature.

(注)滲出率は100℃の蒸溜熱水中で強制攪拌した時
に単位面積から滲出する成分の重量で示す。
(Note) The exudation rate is expressed as the weight of the component exuded from a unit area when the product is forcibly stirred in distilled hot water at 100°C.

また好ましい混合比率の別の一例としては、■を20%
、■を25%、グラス・ウールを31°2 B2O3ム
’205 0aONa2Oその他49.8 16.4 
8,0 10.2 o、914.7この生成物は前記の
ものと比較したときはy同程度で性状その他人差がなか
った。
Also, as another example of a preferable mixing ratio, ■ is 20%
, ■ 25%, glass wool 31°2 B2O3 M'205 0aONa2O Others 49.8 16.4
8,0 10.2 o, 914.7 When this product was compared with the above product, y was at the same level and there were no differences in properties or other characteristics between people.

実施例 第1表に示した焼却等生成物と第2表にその組成を示し
た廃棄グラスファイバを用いて下記率3表に示す条件で
、本発明方法により減容処理を行った。それぞれについ
て得られた結果についても第3表に併せて示す。
EXAMPLES Using the incineration products shown in Table 1 and the waste glass fibers whose compositions are shown in Table 2, volume reduction treatment was carried out according to the method of the present invention under the conditions shown in Table 3 below. The results obtained for each are also shown in Table 3.

以上詳述したところからも本発明の効果は明らかである
が、焼却等生成物は粉体で飛散し易く、吸湿性があり、
保管・貯蔵には措置をこうする必要があり、また廃棄グ
ラス・ファイバは圧縮減容の方法などがあるものの減容
効率も最大ではない欠点があったが、本発明はこれ等の
欠点を同時に解決して、放射性物質の滲出率が極めて少
(強度的にも、経時変化の点からも充分上質な安定固化
体を得ることが出来る。優れた放射性廃棄物の減容処理
方法である。
The effects of the present invention are clear from the detailed explanation above, but the products of incineration are powders that easily scatter, are hygroscopic,
It is necessary to take such measures for storage and storage, and although there are methods for compressing and reducing the volume of waste glass fibers, the volume reduction efficiency is not the highest.However, the present invention solves these drawbacks at the same time. The leaching rate of radioactive materials is extremely low (it is possible to obtain a stable solidified material of sufficient quality in terms of strength and aging).It is an excellent volume reduction treatment method for radioactive waste.

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

第1図は本発明方法による一笑施態様例のフローを示す
。 復代理人 内 1) 明 復代理人 萩 原 亮 − 手続補正書 昭和59年 /月ヲb日 特許庁長官 若杉和夫殿 1、事件の表示 昭和58年特許願第229091号 2− 発#4’)名不承 放射性廃棄物の減容化処理方
法3、補正をする者 事件との関係 特許出願人 住 所 東京都千代田区丸の内二丁目5番1号1″尼 (f、$4;) (620)三菱重工業株式会社4、後
代 理 人 住 所 東京都港区虎ノ門−丁目16番2号5、補正命
令の日付 自発補正 (1)明細書の「発明の詳細な説明」の欄8、補正の内
容 (1)明細書第2頁2行の「従来、」なる記載を「従来
、中、低レベル放射性廃棄物は、その」に訂正する。 (2)同第6頁第6行と第4行の間に1また高レベル放
射性廃棄物については、ガラス固化によって減容処理す
る試みがなされているが、ガラスの材料として良質のガ
ラス・フリットが必要で、しかもガラス・フリットはそ
れぞれの高レベル廃棄物に対し最適に調合されたものを
選定する必要があり、従来は原子力施設外から搬入する
良質のガラス・フリットを使用していたので高価であり
且廃棄物は搬入したガラス・フリットの量だけ明らかに
増量するという問題があった。」なる記載を挿入する。 (3) 同第11頁第9行の「得ることが出来る。」な
る記載のあとに「またガラスの材料は原子(2) 力施設内から必然的に発生するエアフィルタで放射性固
体廃棄物となるグラス・ファイバを使用するので材料コ
ストは零であり、廃棄物の増量はない等」を挿入する。
FIG. 1 shows a flowchart of an exemplary embodiment of the method of the present invention. Sub-agents 1) Clearance agent Ryo Hagiwara - Procedural amendment 1980/Month/2016 Director-General of the Japan Patent Office Kazuo Wakasugi 1, Indication of case Patent application No. 229091 of 1988 2 - Issue number 4' ) Unnamed Radioactive Waste Volume Reduction Processing Method 3, Relationship with the Amendment Case Patent Applicant Address 2-5-1 Marunouchi, Chiyoda-ku, Tokyo, 1″ (f, $4;) ( 620) Mitsubishi Heavy Industries, Ltd. 4, successor manager Address 16-2-5 Toranomon-chome, Minato-ku, Tokyo Date of amendment order Voluntary amendment (1) Column 8 of "Detailed Description of the Invention" of the specification, Amendment Contents (1) The statement ``Conventionally,'' on page 2, line 2 of the specification is corrected to ``Conventionally, intermediate and low-level radioactive waste is the same.'' (2) Between lines 6 and 4 on page 6, there are attempts to reduce the volume of high-level radioactive waste by vitrification, but high-quality glass frit is used as a material for glass. Moreover, it is necessary to select the glass and frit that is optimally formulated for each type of high-level waste, and conventionally high-quality glass and frit brought in from outside the nuclear facility was used, which was expensive. Moreover, there was a problem in that the amount of waste material clearly increased by the amount of glass frit that was brought in. ” is inserted. (3) On page 11, line 9, after the statement ``Can be obtained.'', there is a statement that says ``Glass is made of atomic materials.'' The material cost is zero because glass fiber is used, and there is no increase in waste, etc."

Claims (1)

【特許請求の範囲】[Claims] 原子力施設から発生する放射性廃液および可燃性固体廃
棄物を、乾燥、収部、焼却などにより処理して得た放射
性物質を含有する生成物と、放射性物質が付着している
廃棄ガラス・ファイバを適当な比率で混合し、加熱溶解
して一体化した安定同化体とすることを特徴とする放射
性廃棄物の減容化処理方法。
Products containing radioactive materials obtained by processing radioactive liquid waste and combustible solid waste generated from nuclear facilities by drying, collection, incineration, etc., and waste glass and fibers with radioactive materials attached are appropriately collected. A method for reducing the volume of radioactive waste, characterized by mixing the mixture at a suitable ratio and heating and melting it to form an integrated stable assimilate.
JP22909183A 1983-12-06 1983-12-06 Volume decreasing treating method of radioactive waste Pending JPS60122397A (en)

Priority Applications (3)

Application Number Priority Date Filing Date Title
JP22909183A JPS60122397A (en) 1983-12-06 1983-12-06 Volume decreasing treating method of radioactive waste
EP84303715A EP0155418A3 (en) 1983-12-06 1984-06-04 Method of volume-reducing disposal of radioactive wastes
CA000457495A CA1230221A (en) 1983-12-06 1984-06-26 Method for disposal of radioactive waste involving volume reduction

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP22909183A JPS60122397A (en) 1983-12-06 1983-12-06 Volume decreasing treating method of radioactive waste

Publications (1)

Publication Number Publication Date
JPS60122397A true JPS60122397A (en) 1985-06-29

Family

ID=16886606

Family Applications (1)

Application Number Title Priority Date Filing Date
JP22909183A Pending JPS60122397A (en) 1983-12-06 1983-12-06 Volume decreasing treating method of radioactive waste

Country Status (3)

Country Link
EP (1) EP0155418A3 (en)
JP (1) JPS60122397A (en)
CA (1) CA1230221A (en)

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EP0242569A2 (en) * 1986-03-25 1987-10-28 Doryokuro Kakunenryo Kaihatsu Jigyodan Process for preparing a cartridge for disposal of a radioactive waste liquid
JPH05249294A (en) * 1992-03-03 1993-09-28 Nuclear Fuel Ind Ltd Method of solidifying and disposing of radioactive contaminant
JP2016534311A (en) * 2013-08-08 2016-11-04 アレヴァ・エヌセーAreva Nc Method and apparatus for incineration, melting and vitrification of organic and metal waste

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DE4118123A1 (en) * 1991-06-03 1992-12-10 Siemens Ag METHOD AND DEVICE FOR TREATING A RADIOACTIVE WASTE SOLUTION
FR2940718A1 (en) * 2008-12-30 2010-07-02 Areva Nc ALUMINO-BOROSILICATE GLASS FOR CONTAINING RADIOACTIVE LIQUID EFFLUENTS, AND PROCESS FOR TREATING RADIOACTIVE LIQUID EFFLUENTS
CN113990544A (en) * 2021-10-28 2022-01-28 武汉理工大学 Method for curing medium-low-level glass fiber and high-level waste liquid in cooperation with glass
KR102615509B1 (en) * 2023-04-05 2023-12-19 (주)한국원자력 엔지니어링 Radioactive waste solidification and immobilization method

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DE2731327C3 (en) * 1977-07-12 1981-01-22 Kernforschungszentrum Karlsruhe Gmbh, 7500 Karlsruhe Process for filtering dust from radioactive waste gases and equipment for carrying out the process
DE3110192A1 (en) * 1981-03-17 1982-10-07 Kernforschungszentrum Karlsruhe Gmbh, 7500 Karlsruhe METHOD FOR COATING RADIOACTIVELY CONTAMINATED OR RADIOACTIVE SOLIDS CONTAINING SOLUTIONS FROM NUCLEAR TECHNICAL PLANTS WITH A REPOSABLE MATRIX
DE3142356A1 (en) * 1981-10-26 1983-05-11 Alkem Gmbh, 6450 Hanau "METHOD FOR FINAL CONDITIONING RADIOACTIVE AND / OR TOXIC WASTE"

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0242569A2 (en) * 1986-03-25 1987-10-28 Doryokuro Kakunenryo Kaihatsu Jigyodan Process for preparing a cartridge for disposal of a radioactive waste liquid
JPH05249294A (en) * 1992-03-03 1993-09-28 Nuclear Fuel Ind Ltd Method of solidifying and disposing of radioactive contaminant
JP2016534311A (en) * 2013-08-08 2016-11-04 アレヴァ・エヌセーAreva Nc Method and apparatus for incineration, melting and vitrification of organic and metal waste

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CA1230221A (en) 1987-12-15
EP0155418A3 (en) 1986-11-20
EP0155418A2 (en) 1985-09-25

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