JPS6113196A - Glass solidifying treating method of radioactive waste sodium compound - Google Patents

Glass solidifying treating method of radioactive waste sodium compound

Info

Publication number
JPS6113196A
JPS6113196A JP13435184A JP13435184A JPS6113196A JP S6113196 A JPS6113196 A JP S6113196A JP 13435184 A JP13435184 A JP 13435184A JP 13435184 A JP13435184 A JP 13435184A JP S6113196 A JPS6113196 A JP S6113196A
Authority
JP
Japan
Prior art keywords
radioactive
zirconium oxide
radioactive waste
sodium
sodium compound
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.)
Granted
Application number
JP13435184A
Other languages
Japanese (ja)
Other versions
JPH0262033B2 (en
Inventor
大塚 勝幸
会川 英昭
玉井 秀昭
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.)
Doryokuro Kakunenryo Kaihatsu Jigyodan
Japan Radio Co Ltd
Original Assignee
Doryokuro Kakunenryo Kaihatsu Jigyodan
Japan Radio 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 Doryokuro Kakunenryo Kaihatsu Jigyodan, Japan Radio Co Ltd filed Critical Doryokuro Kakunenryo Kaihatsu Jigyodan
Priority to JP13435184A priority Critical patent/JPS6113196A/en
Publication of JPS6113196A publication Critical patent/JPS6113196A/en
Publication of JPH0262033B2 publication Critical patent/JPH0262033B2/ja
Granted legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03BMANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
    • C03B5/00Melting in furnaces; Furnaces so far as specially adapted for glass manufacture
    • C03B5/005Melting in furnaces; Furnaces so far as specially adapted for glass manufacture of glass-forming waste materials
    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03BMANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
    • C03B5/00Melting in furnaces; Furnaces so far as specially adapted for glass manufacture
    • C03B5/02Melting in furnaces; Furnaces so far as specially adapted for glass manufacture in electric furnaces, e.g. by dielectric heating
    • C03B5/023Melting in furnaces; Furnaces so far as specially adapted for glass manufacture in electric furnaces, e.g. by dielectric heating by microwave heating

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Organic 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】 〈産業上の利用分野〉 この発明は、高速炉で使用されて不要となったhり射性
廃ナトリウ11や使用済燃料再処理/7Ili設より発
生する成用性廃液のうちナトリウムを多量に含むもの等
をガラス固化処理丈る方法に関するものである。
[Detailed Description of the Invention] <Industrial Application Field> This invention is applicable to the reprocessing of radioactive waste sodium 11 which has been used in fast reactors and is no longer needed, and the utility generated from spent fuel reprocessing/7Ili facilities. This invention relates to a method for vitrifying waste liquid containing a large amount of sodium.

〈従来の技術〉 従来、高速炉で使用さ4″lて不要となった放射性廃ナ
トリウム等を処理するに際しては、ナトリウムを安定な
ナトリウム化合物に転換したのちセメント、アスファル
ト等と混合して固化体とする方法、が採られていた。し
かしながら、この方法では、減容比が小さく、また1q
られた固化体を地中や水中に埋めた場合に同化体内に封
じ込めた放射性ナトリウムが浸出しや1いという欠点か
あ・〕だ。
<Conventional technology> Conventionally, when processing radioactive waste sodium etc. that was used in fast reactors and was no longer needed, the sodium was converted into a stable sodium compound and then mixed with cement, asphalt, etc. to solidify it. However, with this method, the volume reduction ratio is small, and 1q
The drawback is that if the solidified material is buried underground or in water, the radioactive sodium contained within the assimilated material is likely to leach out.

減容比を比較的太とづ゛るために、放射性廃ナトリウム
化合物に二酸化珪素やフリット等のガラス形成材を加え
て加熱溶融1ノだのも冷却、固化してガラス固化体とす
る技術が提案されているが、この場合にも、得られたガ
ラス固化体からtIl、耐性ナトリウムが浸出しやすい
という欠点は必ずしも解消することができない。
In order to keep the volume reduction ratio relatively high, a technology has been developed to add glass-forming materials such as silicon dioxide and frit to the radioactive waste sodium compound, melt it by heating, and then cool and solidify it into a vitrified material. Although it has been proposed, even in this case, the disadvantage that tIl and resistant sodium are easily leached from the obtained vitrified product cannot necessarily be overcome.

一方、軽水炉の燃料被覆管や燃料集合体の種々の金属部
材は耐食性、耐高温水性を備えたジルコニウム合金であ
るジルカロイが用いられているが、使用済燃料の処理に
際して排出されるかような放射性ジルカロイは高レベル
金属廃棄物であるため、その処理対策が問題とされてい
る。
On the other hand, Zircaloy, a zirconium alloy with corrosion resistance and high temperature water resistance, is used for various metal parts of the fuel cladding tubes and fuel assemblies of light water reactors. Since Zircaloy is a high-level metal waste, measures to deal with it are an issue.

〈発明が解決しようとする問題点〉 そこでこの発明は、放射性廃ナトリウム化合物をガラス
固化処理してナトリウムの浸出しにくいガラス同化体を
得ることができると同時に、従来からその処理対策が望
まれていた使用済燃料被覆管等の放射性ジルカロイ廃棄
物の処理も有効に行なうことができる処理方法を提供す
ることを目的としてなされたものである。
<Problems to be Solved by the Invention> Therefore, the present invention is capable of vitrifying radioactive waste sodium compounds to obtain a glass assimilate that is resistant to leaching of sodium, and at the same time, it solves a problem that has long been desired. The purpose of this invention is to provide a treatment method that can effectively treat radioactive Zircaloy waste such as spent fuel cladding tubes.

〈問題点を解決するための手段〉 すなわちこの発明は、使用済核燃料被覆管等の放射性ジ
ルカロイ廃棄物を酸化処理して酸化ジルコニウムとし、
放射性廃ナトリウム化合物をガラス形成材および前記酸
化ジルコニウムと混合し、この混合物を加熱溶融したの
ち冷却。
<Means for solving the problem> That is, the present invention oxidizes radioactive zircaloy waste such as spent nuclear fuel cladding tubes to produce zirconium oxide,
A radioactive waste sodium compound is mixed with a glass forming material and the zirconium oxide, and this mixture is heated to melt and then cooled.

固化すること盆特徴とする放射性廃す小すウム化合物の
ガラス固化処理方法である。
This is a vitrification treatment method for radioactive waste smallium compounds, which is characterized by solidification.

〈発明の具体的d2明〉 本発明者等は、放射性廃ナトリウム化合物を二酸化珪素
(SiO□)やフリット等のガラス形成材と混合溶融し
てガラス固化体を作る際に、酸化ジルコニウム(Zr 
O)をガラス形成材と共に添加混合することによって、
潮解性がなく耐浸出性に優れた安定なガラス固化体が得
られること、更には、」1記で使用する酸化ジルコニウ
ムとして、使用済燃料被覆管等を構成する放射性ジルカ
ロイ廃棄物を酸化してVノられる放射性の酸化ジルコニ
ウムを効果的に使用できることを見出し、この発明を完
成させたものである。
<Specific d2 of the invention> The present inventors have discovered that zirconium oxide (Zr
By adding and mixing O) with the glass forming material,
It is possible to obtain a stable vitrified material that is non-deliquescent and has excellent leaching resistance, and furthermore, as the zirconium oxide used in item 1, radioactive zircaloy waste constituting spent fuel cladding tubes, etc. can be oxidized. This invention was completed based on the discovery that radioactive zirconium oxide, which can be oxidized by V, can be used effectively.

この発明の被処理物である放射性廃ナトリウム化合物と
しては、Na OH,’ Na2O。
The radioactive waste sodium compounds to be treated in this invention include NaOH, 'Na2O.

Na2Co3. Na No、等を主成分とする固体ま
たは水溶液である。かような放射性廃ナトリウム化合物
の発生源は、例えば高速炉からの放射°性廃ナトリウム
や、軽水炉再処理施設からの含ナトリウム廃液等が上げ
られる。前者の廃ナトリウムはそのままでは化学的活性
が高いため、Na、OH等の安定なナトリウム化合物と
する不活性化工程が必要となるが、後者の含ナトリウム
廃液の場合には廃液中でナトリウムが収部安定なナトリ
ウム化合物となっ′ているため不活性化工程は必要ない
Na2Co3. It is a solid or aqueous solution whose main components are Na, No, etc. Sources of such radioactive waste sodium compounds include, for example, radioactive waste sodium from fast reactors and sodium-containing waste liquid from light water reactor reprocessing facilities. The former type of waste sodium has high chemical activity as it is, so an inactivation process is required to convert it into stable sodium compounds such as Na and OH, but in the case of the latter type of sodium-containing waste liquid, sodium is recovered in the waste liquid. Since it is a partially stable sodium compound, there is no need for an inactivation step.

放射性廃ナトリウム化合物が水溶液の場合には、蒸発処
理して所定濃度まで濃縮する前処理が必要となる。
If the radioactive waste sodium compound is an aqueous solution, pretreatment is required to evaporate it and concentrate it to a predetermined concentration.

また、被処理物である上記の如き放射性廃ナトリウム化
合物中には、ナトリウム化合物以外の放射性物質(例え
ば炉構成材料の腐食生成物や燃料物質の核分裂生成物等
)が一般に同伴して含まれているが、これらの同伴放射
性物質もナトリウム化合物と共にこの発明の処理方法に
よってガラス固化体中に安定に保持することができる。
In addition, radioactive waste sodium compounds such as those mentioned above, which are the materials to be treated, generally contain radioactive substances other than sodium compounds (for example, corrosion products of reactor constituent materials, nuclear fission products of fuel materials, etc.). However, these accompanying radioactive substances can also be stably retained in the vitrified body together with the sodium compound by the treatment method of the present invention.

この発明で用いるガラス形成材としては、二酸化珪素や
フリット等の従来がら放射性廃棄物の同化処理技術分野
で慣用されているガラス形成材を使用することができる
が、この発明によれば、ガラス形成材に加えて酸化ジル
コニウムを添加することによって、得られたガラス固化
体からの放射性ナトリウムの浸出を低減させることがで
きる。特にこの発明においてはこの酸化ジルコニウムと
して、使用済の燃料被覆管や燃料集合体の各種金属部材
として用いられた放射化されたジルコニウム金属くシル
カ0イ)を酸化処理して得た放射性酸化ジルコニウムを
使用するのである。使用済のジルカロイを酸化処Jlj
づ−るには、酸化性雰囲気でジルカロイを900℃以上
に加熱づればよく、これによって酸化ジルコニウムの粉
末を得ることができる。
As the glass forming material used in this invention, glass forming materials conventionally used in the technical field of assimilation treatment of radioactive waste, such as silicon dioxide and frit, can be used. By adding zirconium oxide in addition to the material, leaching of radioactive sodium from the obtained vitrified material can be reduced. In particular, in this invention, the zirconium oxide is radioactive zirconium oxide obtained by oxidizing radioactive zirconium metal used as various metal parts of spent fuel cladding tubes and fuel assemblies. Use it. Oxidation treatment of used Zircaloy
For this purpose, zircaloy can be heated to 900° C. or higher in an oxidizing atmosphere, thereby producing zirconium oxide powder.

被処理物である放射性廃ナトリウム化合物は、ガラス形
成材および使用済ジルカロイからの酸化ジルコニウムと
乾式或いは湿式混合したのら、混合物を好ましくはマイ
クロ波加熱により溶融し、冷却、固化してガラス固化体
とする。
The radioactive waste sodium compound to be treated is mixed dry or wet with a glass forming material and zirconium oxide from spent Zircaloy, and then the mixture is preferably melted by microwave heating, cooled, and solidified to form a vitrified product. shall be.

好ましい混合割合は、混合物全重量に対して酸化ジルコ
ニウムは5〜20重量%の範囲、放射性廃ナトリウム化
合物は30重量%以下(Na、O換算)、残部をガラス
形成材どづ゛る。酸化ジルコニウムが5重量%より少な
いと得られたガラス固化体が潮解性をもつようになり、
ナトリウムの耐浸出性が劣化し、20重量%より多いと
混合物の溶融時に共融潤度が高くなり未溶解酸化ジルコ
ニウムが残留づる傾向がある。
The preferred mixing ratio is that zirconium oxide is in the range of 5 to 20% by weight, the radioactive waste sodium compound is in the range of 30% by weight or less (calculated as Na and O), and the remainder is the glass forming material. When the amount of zirconium oxide is less than 5% by weight, the vitrified material obtained becomes deliquescent,
The leaching resistance of sodium deteriorates, and if the amount exceeds 20% by weight, the degree of eutectic wetting increases when the mixture is melted, and undissolved zirconium oxide tends to remain.

またナトリウム化合物を30重量%より多Mに混合する
と未溶解酸化ジルコニウムが多くなって酸化ジルコニウ
ム添加効果が発現されにくく、得られたガラス同化体が
潮解性をもつようになる。
Furthermore, if the sodium compound is mixed in an amount higher than 30% by weight, the amount of undissolved zirconium oxide increases, making it difficult to exhibit the effect of adding zirconium oxide, and the resulting glass assimilate becomes deliquescent.

混合物の加熱温度は各成分が共融する温度であればよく
、各成分の混合割合によって変わるが一般的には110
0〜1500℃の範囲である。なお、必要に応じて混合
物中に酸化硼素(8,03)等の溶融温度降下剤を添加
することにより、比較的低い温度で溶融させることがで
きる。
The heating temperature of the mixture only needs to be the temperature at which each component is eutectic, and although it varies depending on the mixing ratio of each component, it is generally 110
It is in the range of 0 to 1500°C. Note that by adding a melting temperature lowering agent such as boron oxide (8,03) to the mixture as necessary, it is possible to melt the mixture at a relatively low temperature.

このにうにしで得られた溶融物を冷却、固化することに
よって、主としてN a、S i O3,N a27r
 Si O,、ZrO2の単体もしくはこれらの混合物
からなるガラス同化体を得ることができる。
By cooling and solidifying the melt obtained from sea urchin, mainly Na, SiO3, Na27r
A glass assimilate consisting of Si 2 O, ZrO 2 alone or a mixture thereof can be obtained.

〈実施例〉 以下に実施例J5よび比較例を上げて更に説明する。な
お%は全で重量%である。
<Example> Example J5 and a comparative example will be further explained below. Note that all percentages are percentages by weight.

実施例1゜ 放射性廃ナトリウム化合物、二酸化珪素、使用済ジルカ
ロイを酸化して得られた酸化ジルコニウムおよび溶融温
度降下剤酸化硼素を下表に示した各種割合で混合し、混
合物をマイクロ波加熱溶融炉を用いて溶融したのち冷F
JJ 、固化してガラス同化体を得た。このガラス固化
体の固化状態を調べた結果を下表に示す。
Example 1 Radioactive waste sodium compound, silicon dioxide, zirconium oxide obtained by oxidizing spent zircaloy, and boron oxide as a melting temperature lowering agent were mixed in various proportions shown in the table below, and the mixture was heated in a microwave heating melting furnace. After melting using cold F
JJ, solidified to obtain glass assimilate. The results of examining the solidification state of this vitrified material are shown in the table below.

この表から、酸化ジルコニウムの添加量は20%以下、
ナトリウム化合物は30%以下(N a20換算)で潮
解性のない、ずなわらす1−リウムの浸出しにくい安定
なガラス固化体(AおよびB)が得られることがわかる
From this table, the amount of zirconium oxide added is 20% or less,
It can be seen that stable vitrified products (A and B) with no deliquescent property and from which 1-lium is difficult to leach out can be obtained with a sodium compound content of 30% or less (calculated as Na20).

実施例2゜ 下記組成の混合物を実施例1と同様にして溶融、冷却、
固化してガラス固化体とした。
Example 2 A mixture having the following composition was melted, cooled, and melted in the same manner as in Example 1.
It was solidified to form a vitrified product.

廃NaOH77,49 <Na、O!Atl      6o  (+  >S
iO104g λ ZI’022(1’(I B203         35、.6g得られたガラ
ス固化体は潮解性もなく、透明度も比較的高いガラス質
化したちので通常のソーダガラス、と同様な外観を呈し
ていた。
Waste NaOH77,49 <Na, O! Atl 6o (+ >S
iO104g λ ZI'022(1'(I B203 35, .6g) The obtained vitrified material had no deliquescent properties and was vitrified with relatively high transparency, so it had an appearance similar to ordinary soda glass. .

一方、比較のために下記組成の混合物(1)および(2
)を同様に溶fi1! 、冷却、固化・しく固化体を調
製 し ノこ 。
On the other hand, for comparison, mixtures (1) and (2) with the following compositions were prepared.
) in the same way! , cool, solidify and prepare a solidified material.

廃 Na   OH75,5g         10
0    Q(N  a20  換 p  )    
      (58,50)       (77,5
g   >Si  0275,50   200 0H
2080m、(12001TIG 得られた固化体は何れも潮解性を有し、ガラス質化しな
かった。
Waste NaOH75.5g 10
0 Q (Na20 conversion p)
(58,50) (77,5
g>Si 0275,50 200 0H
2080m, (12001TIG) All of the obtained solidified bodies had deliquescent properties and did not become vitrified.

〈効 果〉 以上説明したようにこの発明の処理方法によれば、軟躬
性廃ナトリウム化合物にガラス形成材と共に酸化ジルコ
ニウムを添加混合して溶融。
<Effects> As explained above, according to the treatment method of the present invention, zirconium oxide is added and mixed with a glass forming material to a soft waste sodium compound and melted.

冷却、同化することによって、ナトリウムの浸出しにく
いガラス固化体を得ることができ、効果的な放射性廃ナ
トリウム化合物の同化処理ができる。
By cooling and assimilating it, it is possible to obtain a vitrified material that does not easily exude sodium, and it is possible to effectively assimilate radioactive waste sodium compounds.

また酸化ジルコニウムどしては使用済燃料被覆管等の放
射性ジルカロイ廃棄物を酸化処理して得られる放射性の
酸化ジルコニウムを使用するため、放射性ジルカロイ廃
棄物の処理対策としても有効であり、放射性廃棄物の増
■防止が図れるという利点がある。
In addition, since zirconium oxide is obtained by oxidizing radioactive zircaloy waste such as spent fuel cladding, it is effective as a treatment measure for radioactive zircaloy waste. This has the advantage of preventing an increase in

Claims (1)

【特許請求の範囲】 1、使用済核燃料被覆管等の放射性ジルカロイ廃棄物を
酸化処理して酸化ジルコニウムとし、放射性廃ナトリウ
ム化合物をガラス形成材および前記酸化ジルコニウムと
混合し、この混合物を加熱溶融したのち冷却、固化する
ことを特徴とする放射性廃ナトリウム化合物のガラス固
化処理方法。 2、前記混合工程において、混合物全重量に対して酸化
ジルコニウムを5〜20重量%、廃ナトリウム化合物を
30重量%以下(Na_2O換算)、残部がガラス形成
材となるように混合する特許請求の範囲第1項記載の方
法。
[Claims] 1. Radioactive zircaloy waste such as spent nuclear fuel cladding tubes is oxidized to produce zirconium oxide, a radioactive waste sodium compound is mixed with a glass forming material and the zirconium oxide, and this mixture is heated and melted. A method for vitrifying radioactive waste sodium compounds, which is characterized by cooling and solidifying the compounds. 2. In the mixing step, zirconium oxide is mixed in an amount of 5 to 20% by weight, waste sodium compound is mixed in an amount of 30% by weight or less (in terms of Na_2O), and the remainder is a glass forming material based on the total weight of the mixture. The method described in paragraph 1.
JP13435184A 1984-06-29 1984-06-29 Glass solidifying treating method of radioactive waste sodium compound Granted JPS6113196A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP13435184A JPS6113196A (en) 1984-06-29 1984-06-29 Glass solidifying treating method of radioactive waste sodium compound

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP13435184A JPS6113196A (en) 1984-06-29 1984-06-29 Glass solidifying treating method of radioactive waste sodium compound

Publications (2)

Publication Number Publication Date
JPS6113196A true JPS6113196A (en) 1986-01-21
JPH0262033B2 JPH0262033B2 (en) 1990-12-21

Family

ID=15126328

Family Applications (1)

Application Number Title Priority Date Filing Date
JP13435184A Granted JPS6113196A (en) 1984-06-29 1984-06-29 Glass solidifying treating method of radioactive waste sodium compound

Country Status (1)

Country Link
JP (1) JPS6113196A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0854115A1 (en) * 1997-01-15 1998-07-22 CENTRE D'ETUDES DE L'ENERGIE NUCLEAIRE, établissement d'utilité publique Process for the oxidation of at least one alkali metal

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0854115A1 (en) * 1997-01-15 1998-07-22 CENTRE D'ETUDES DE L'ENERGIE NUCLEAIRE, établissement d'utilité publique Process for the oxidation of at least one alkali metal
BE1010854A3 (en) * 1997-01-15 1999-02-02 En Nucleaire Etablissement D U Oxidation process at least one metal alkali.

Also Published As

Publication number Publication date
JPH0262033B2 (en) 1990-12-21

Similar Documents

Publication Publication Date Title
US4514329A (en) Process for vitrifying liquid radioactive waste
KR850000462B1 (en) Containing nuclear waste via chemical polymerization
CA1171266A (en) Nuclear waste encapsulation in borosilicate glass by chemical polymerization
US4097401A (en) Thermodynamically stable product for permanent storage and disposal of highly radioactive liquid wastes
JP3232993B2 (en) Radioactive waste treatment method
Langowski et al. Volatility literature of chlorine, iodine, cesium, strontium, technetium, and rhenium; technetium and rhenium volatility testing
Bates et al. Glass as a waste form for the immobilization of plutonium
JPS6113196A (en) Glass solidifying treating method of radioactive waste sodium compound
CN114180834B (en) Iron-containing low-phosphate glass, preparation method and application thereof
CN114105472B (en) Iron-containing high-phosphate glass, preparation method and application thereof
CA1196180A (en) Cinder aggregate from purex waste
JPH0252839B2 (en)
JP2019043810A (en) Processing method of glass solidified body
JP3864203B2 (en) Solidification method for radioactive waste
US6329563B1 (en) Vitrification of ion exchange resins
USH1013H (en) Process for the immobilization and volume reduction of low level radioactive wastes from thorium and uranium processing
JPS61132898A (en) Method of solidying and treating radioactive waste
JP2001027694A (en) Solidified body of radioactive condensed waste substance and manufacture of the same
Dong et al. Dechlorination and vitrification of electrochemical processing salt waste
Rudolph et al. Lab-scale R+ D work on fission product solidification by vitrification and thermite processes
Sheng et al. Vitrification of borate waste generated by nuclear power plants
US3373116A (en) Radioactive fluophosphate glass composition
JPS63241400A (en) Solidifying processing method of radioactive waste
GB2170496A (en) Vitrification of inorganic materials
Gombert et al. Vitrification of high-level ICPP calcined wastes