JP4665103B2 - Vitrification method of radioactive liquid waste - Google Patents

Vitrification method of radioactive liquid waste Download PDF

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JP4665103B2
JP4665103B2 JP2007286060A JP2007286060A JP4665103B2 JP 4665103 B2 JP4665103 B2 JP 4665103B2 JP 2007286060 A JP2007286060 A JP 2007286060A JP 2007286060 A JP2007286060 A JP 2007286060A JP 4665103 B2 JP4665103 B2 JP 4665103B2
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JP2009115490A (en
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義之 伊藤
盛弘 新原
暁和 高谷
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独立行政法人 日本原子力研究開発機構
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本発明は、放射性廃液を物理的にも化学的にも安定なガラス固化体にする方法に関し、更に詳しく述べると、主なガラス原料にアルコキシドを用いることにより、軟化点以下の温度で均質なガラス固化体を製造できる方法に関するものである。   The present invention relates to a method for converting a radioactive liquid waste into a physically and chemically stable vitrified body, and more specifically, by using an alkoxide as a main glass raw material, a homogeneous glass at a temperature below the softening point. The present invention relates to a method capable of producing a solidified body.

通常、再処理工場などの原子力施設から発生する放射性廃液は、濃縮した後、ガラス原料と共にガラス溶融炉に供給され、1000℃以上の高温で溶融処理した後、物理的、化学的に安定なガラス固化体へと処理される。得られたガラス固化体は、放射性廃棄物保管施設で保管される。このような技術は従来周知である。ガラス溶融炉には、加熱方式、炉材質、形式などによって種々のものが開発されている。代表的な例としては、炉の側壁に対向するように主電極を設置し、ガラスに直接通電することにより溶融させる直接通電方式がある。直接通電方式のガラス溶融炉による放射性廃液のガラス固化処理については、例えば特許文献1などにも記載がある。しかし、溶融ガラスは非常に腐食性が高いことから、溶融炉については、侵食に対応する設計とメンテナンスが必要であり、費用が増大する問題があった。   Normally, radioactive liquid waste generated from nuclear facilities such as reprocessing plants is concentrated, then supplied to the glass melting furnace together with the glass raw material, melted at a high temperature of 1000 ° C or higher, and then physically and chemically stable glass. It is processed into a solidified body. The obtained vitrified body is stored in a radioactive waste storage facility. Such techniques are well known in the art. Various glass melting furnaces have been developed depending on the heating method, furnace material, type, and the like. As a typical example, there is a direct energization method in which a main electrode is installed so as to face the side wall of the furnace and melted by directly energizing glass. About the vitrification process of the radioactive waste liquid by the glass melting furnace of a direct electricity system, patent document 1 etc. have description, for example. However, since molten glass is very corrosive, the melting furnace needs to be designed and maintained in response to erosion, which increases the cost.

ところで、高レベル放射性廃液の放射能のうち約98%はセシウムが占めており、セシウムの沸点は700℃程度であることから、従来のガラス溶融固化処理方法ではセシウム回収などの揮発対策が必要となっている。そのため、セシウムなど放射性元素の回収設備を付設しなければならず、その点でも設備やメンテナンスに要する費用が多くなる欠点があった。
特開2007−24816号公報
By the way, about 98% of the radioactivity of the high-level radioactive liquid waste is occupied by cesium, and since the boiling point of cesium is about 700 ° C., the conventional glass melt solidification processing method requires volatilization measures such as cesium recovery. It has become. For this reason, a facility for recovering radioactive elements such as cesium has to be attached, and in that respect, there is a drawback that the cost required for the facility and maintenance increases.
JP 2007-24816 A

本発明が解決しようとする課題は、放射性廃液のガラス固化処理に際し、ガラスの軟化点以下の低温でガラス固化できるように工夫することで、設備材料の侵食や放射性元素の揮発を抑制し、設備やメンテナンスの費用を大幅に削減できるようにすることである。   The problem to be solved by the present invention is to reduce the erosion of equipment materials and volatilization of radioactive elements by devising vitrification at a low temperature below the softening point of glass during vitrification treatment of radioactive liquid waste. And to be able to significantly reduce maintenance costs.

本発明は、放射性廃液中に、ガラス固化体として必要なガラス物性を得るための水溶性原料、及びアルコキシドの加水分解を促進するための溶媒を添加し、更に親油性のアルコキシド原料を添加して混和し、加水分解・重合反応を進めてゾルをゲル化し、得られた湿潤ゲルを乾燥させ、その乾燥ゲルを熱処理でガラス軟化点以下の温度で焼結させることによりガラス固化体にすることを特徴とする放射性廃液のガラス固化処理方法である。   In the present invention, a water-soluble raw material for obtaining glass properties necessary as a vitrified body and a solvent for promoting hydrolysis of an alkoxide are added to a radioactive liquid waste, and a lipophilic alkoxide raw material is further added. Mixing, proceeding with hydrolysis and polymerization reaction to gel the sol, drying the resulting wet gel, and sintering the dried gel at a temperature below the glass softening point by heat treatment It is the vitrification method of the radioactive waste liquid characterized.

ここで、湿潤ゲルを乾燥させる際、ゲル中の湿潤部分と乾燥部分の間に応力がかかり、ひび割れを生じる恐れがあるので、湿潤ゲルを粉砕して乾燥させる。燥ゲルを仮焼した後、所定の形状に圧縮成型し、焼結させることで、大型で緻密なガラス固化体を得る。


Here, when drying the wet gel, a stress is applied between the wet portion and a dry portion of the gel, than which may cause cracking, drying by grinding a moist gel. After calcining Drying gel, and compression molded into a predetermined shape, by sintering, Ru obtain a dense vitrified large.


本発明において、例えば水溶性原料として硝酸塩を、アルコキシドの加水分解を促進するための溶媒としてアルコールを、親油性のアルコキシド原料としてトリメチルボラートとケイ酸エチルを用いるのが好ましい。   In the present invention, for example, nitrate is preferably used as a water-soluble raw material, alcohol is used as a solvent for promoting hydrolysis of an alkoxide, and trimethyl borate and ethyl silicate are preferably used as a lipophilic alkoxide raw material.

本発明に係る放射性廃液のガラス固化処理方法は、ガラス原料に主にアルコキシドを用いることで、軟化点(ホウケイ酸ガラスであれば約600℃)以下の温度でガラス固化体を製造することが可能となる。これにより、侵食性の高い溶融ガラスを取り扱う必要がなくなり、設備材料の侵食が抑制され、メンテナンス費用を削減することができる。また、高レベル放射性廃液には多くのセシウムが含まれているが、本発明では全工程を通じてセシウムの沸点未満で取り扱うことができるので、回収設備も簡略化できる。   The vitrification method for radioactive liquid waste according to the present invention can produce a vitrified body at a temperature below the softening point (about 600 ° C. for borosilicate glass) by mainly using alkoxide as a glass raw material. It becomes. Thereby, it is not necessary to handle molten glass having high erodibility, erosion of equipment materials is suppressed, and maintenance costs can be reduced. The high-level radioactive liquid waste contains a large amount of cesium, but in the present invention, it can be handled at less than the boiling point of cesium throughout the entire process, so that the recovery equipment can be simplified.

本発明は、主に、水溶性原料による組成調整、アルコキシドの加水分解を促進するための溶媒の添加、親油性原料による組成調整とゲル骨格を形成するゾルの生成、ゲル化、乾燥、熱処理の工程からなる。本発明の処理対象となる放射性廃液としては、不揮発性の廃棄物を含む水溶液、ゾル、サスペンションなどでもよい。   The present invention mainly includes composition adjustment with a water-soluble raw material, addition of a solvent for promoting alkoxide hydrolysis, composition adjustment with a lipophilic raw material, formation of a sol forming a gel skeleton, gelation, drying, and heat treatment. It consists of a process. The radioactive waste liquid to be treated in the present invention may be an aqueous solution containing volatile waste, a sol, a suspension, or the like.

図1は、本発明によるガラス固化処理方法の一例を示す工程図である。これは、バルク乾燥方式の例である。放射性廃液10中に、必要なガラスの物性(転移温度、融点、強度等)を得るための水溶性原料を添加する。水溶性原料としては、例えば金属硝酸塩を用いる。また、次に添加する親油性アルコキシド原料を水溶性の廃液と混和し、加水分解を促進するための溶媒を添加する。この溶媒には、エタノールやメタノールなどのアルコールを用いる。その後、前記水溶性原料と同様、必要なガラスの特性を得るために、ケイ酸エチルやケイ酸メチルなどの親油性アルコキシド原料を添加し、混和する。   FIG. 1 is a process diagram showing an example of a vitrification method according to the present invention. This is an example of a bulk drying method. A water-soluble raw material for obtaining the necessary glass physical properties (transition temperature, melting point, strength, etc.) is added to the radioactive liquid waste 10. For example, metal nitrate is used as the water-soluble raw material. Further, the lipophilic alkoxide raw material to be added next is mixed with a water-soluble waste liquid, and a solvent for promoting hydrolysis is added. An alcohol such as ethanol or methanol is used as this solvent. Thereafter, in order to obtain the necessary glass properties, the lipophilic alkoxide raw material such as ethyl silicate and methyl silicate is added and mixed as in the case of the water-soluble raw material.

そして、適当な温度に加熱し超音波を加えるなどして加水分解・重合反応を進め、ゾルをゲル化する。次に、得られた湿潤ゲルを乾燥させる。その際、ゲル中の乾燥部分と湿潤部分の間に応力がかかり、ひび割れを生じる恐れがある。そこで、ひび割れを防ぐ簡易な方法として、一度に処理するゲル量を制限し、加熱によって徐々に乾燥させる。その他のひび割れ防止手段として、超臨界乾燥あるいは凍結乾燥などの技術を用いてもよい。最後に、その乾燥ゲルをガラス軟化点以下の温度で熱処理し、ゲル中の結晶水、溶媒を分解、揮発させ、焼結させることにより緻密なガラス固化体12にする。   Then, it is heated to an appropriate temperature and subjected to hydrolysis / polymerization reaction by adding ultrasonic waves, etc. to gel the sol. Next, the obtained wet gel is dried. At that time, stress is applied between the dry part and the wet part in the gel, which may cause cracks. Therefore, as a simple method for preventing cracks, the amount of gel to be processed at one time is limited and gradually dried by heating. As other crack preventing means, a technique such as supercritical drying or freeze drying may be used. Finally, the dried gel is heat-treated at a temperature equal to or lower than the glass softening point, and crystal water and solvent in the gel are decomposed, volatilized, and sintered to obtain a dense glass solidified body 12.

このガラス固化処理方法において、水溶性原料として特に金属硝酸塩が好ましいのは、金属硝酸塩は、放射性廃液に溶解し易く加熱により脱硝することから、均質なガラス固化体を得る上で好都合だからである。例えば、アルミナを含むガラスは結晶化し難い性質を持つ。放射性廃液に硝酸アルミニウムを添加すれば、後の熱処理によって脱硝され、アルミナを均質に含むガラス固化体が合成できる。硝酸アルミニウムの他には、硝酸カルシウムを添加すると(ガラス固化体中では酸化カルシウムとして均質に存在)、アルカリ金属の溶出防止効果などが生じる。なお、金属硝酸塩は水和物であってもよい。   In this vitrification method, the metal nitrate is particularly preferable as the water-soluble raw material because the metal nitrate is easy to dissolve in the radioactive liquid waste and is denitrated by heating, which is advantageous in obtaining a homogeneous vitrified body. For example, glass containing alumina has a property that is difficult to crystallize. If aluminum nitrate is added to the radioactive liquid waste, it is denitrated by a subsequent heat treatment, and a vitrified body containing alumina uniformly can be synthesized. In addition to aluminum nitrate, addition of calcium nitrate (homogeneously present as calcium oxide in the vitrified body) produces an alkali metal elution preventing effect. The metal nitrate may be a hydrate.

ところで、ガラス原料として、例えばホウ酸は軟化点を下げる効果がある。しかし、放射性廃液にホウ酸を添加しても完全には溶解せず、ガラス固化体は不均質となる。そこで本発明では、ホウ素原料として水溶性のホウ酸の代わりに、トリメチルボラートなどのアルコキシドを使用している。アルコキシドを添加すれば、既に添加されているアルコールによく混和し、均質なガラス固化体を得ることができる。特にトリメチルボラートおよびケイ酸エチル等の中心元素にアルコキシドが2つ以上配位した化合物は、添加とともに重合を起こしゲル化するため、最後に混合する。   By the way, as a glass raw material, for example, boric acid has an effect of lowering the softening point. However, even if boric acid is added to the radioactive liquid waste, it is not completely dissolved, and the vitrified body becomes inhomogeneous. Therefore, in the present invention, an alkoxide such as trimethyl borate is used as a boron raw material instead of water-soluble boric acid. If an alkoxide is added, it can mix well with the alcohol already added, and a homogeneous glass solid can be obtained. In particular, a compound in which two or more alkoxides are coordinated to a central element such as trimethyl borate and ethyl silicate is mixed at the end because it undergoes polymerization and gelation upon addition.

なお、アルコキシド原料がトリメチルボラートなどの反応性の高い物質であると、反応の過程でアルコキシドからアルコールが発生するため、必ずしもアルコール溶媒を添加する必要はないが、通常は加水分解を促進するためにエタノールなどを添加するのが好ましい。後の乾燥の工程では、ゲルの乾燥部分と湿潤部分に応力がかかり、ひび割れを生じる恐れがあるが、アルコールの一部をジメチルホルムアミドによって置き換えることで乾燥時のひび割れ防止を図ることができるし、熱処理時におけるガラスの相分離を抑えることもできる。   Note that if the alkoxide raw material is a highly reactive substance such as trimethylborate, alcohol is generated from the alkoxide during the reaction, so it is not always necessary to add an alcohol solvent, but usually it promotes hydrolysis. It is preferable to add ethanol or the like. In the subsequent drying process, stress is applied to the dry and wet parts of the gel, which may cause cracking, but by replacing part of the alcohol with dimethylformamide, it is possible to prevent cracking during drying, It is also possible to suppress phase separation of the glass during the heat treatment.

図2は、本発明によるガラス固化処理方法の他の例を示す工程図である。これは、粉砕乾燥方式の例である。前記の例と同様、放射性廃液10中に水溶性原料、溶媒(アルコール)を添加する。更に、親油性アルコキシド原料を添加し混和する。加水分解・重合反応を進め、ゾルをゲル化する。そして、この例では得られた湿潤ゲルを粉砕し乾燥させる。最後に、その乾燥ゲルをガラス軟化点以下の温度で熱処理する。まず、仮焼することでゲル中の結晶水、溶媒を分解、揮発させ、仮焼粉体を所定の形状に圧縮成形し、その圧縮成形体を焼結させることにより大型の緻密なガラス固化体12にする。   FIG. 2 is a process diagram showing another example of the vitrification method according to the present invention. This is an example of a pulverization drying method. As in the above example, a water-soluble raw material and a solvent (alcohol) are added to the radioactive waste liquid 10. Furthermore, a lipophilic alkoxide raw material is added and mixed. The hydrolysis / polymerization reaction proceeds to gel the sol. In this example, the obtained wet gel is pulverized and dried. Finally, the dried gel is heat treated at a temperature below the glass softening point. First, by calcination, the crystal water and solvent in the gel are decomposed and volatilized, the calcined powder is compression-molded into a predetermined shape, and the compression-molded body is sintered to sinter the large dense glass solidified body. Set to 12.

前述したように、乾燥の工程では、乾燥部分と湿潤部分に応力がかかり、ひび割れを生じる恐れがある。しかし、この例では、湿潤ゲルを粉砕するため、ひび割れ対策が不要であり、一度に乾燥するゲルの量を増加できるとともに、乾燥時間の短縮が可能となる。但し、乾燥ゲルが粉体であることから、ガラス固化体を製造するために新たに圧縮成型の工程を追加している。   As described above, in the drying process, stress is applied to the dry portion and the wet portion, which may cause cracks. However, in this example, since the wet gel is pulverized, it is not necessary to take measures against cracks, the amount of gel to be dried at a time can be increased, and the drying time can be shortened. However, since the dried gel is a powder, a new compression molding step is added to produce a glass solid.

本発明は、高レベル放射性廃液や低レベル放射性廃液のガラス固化処理など、広い分野への応用が可能である。   The present invention can be applied to a wide range of fields such as vitrification treatment of high-level radioactive liquid waste and low-level radioactive liquid waste.

図1に示すバルク乾燥方式により、加圧水型軽水炉にて28000MWD/t燃焼した燃料を0.5年冷却後再処理し、5年冷却した放射性廃液の模擬物をガラス固化した。   By the bulk drying method shown in FIG. 1, 28000 MWD / t burned fuel in a pressurized water reactor was cooled for 0.5 years and then reprocessed, and a simulated radioactive waste liquid cooled for 5 years was vitrified.

まず、廃液8.18ml中に、必要なガラスの特性(転移温度、融点、強度等)を得るために、水溶性原料として次のような組成の硝酸塩を添加した。
・LiNO3 … 0.69g
・Ca(NO3 2 ・4H2 O … 0.63g
・Zn(NO3 2 ・6H2 O … 0.55g
・Al(NO3 3 ・9H2 O … 1.84g
なお、添加量は、いずれもガラス固化体5g当たりの原料重量である。
First, in order to obtain necessary glass characteristics (transition temperature, melting point, strength, etc.) in 8.18 ml of the waste liquid, a nitrate having the following composition was added as a water-soluble raw material.
・ LiNO 3 ... 0.69g
・ Ca (NO 3 ) 2 / 4H 2 O 0.63 g
・ Zn (NO 3 ) 2 .6H 2 O 0.55 g
・ Al (NO 3 ) 3 · 9H 2 O ... 1.84 g
In addition, all addition amount is the raw material weight per 5 g of glass solidification bodies.

次に、加水分解を促進するための溶媒としてエタノールを添加した。更に、重合を起こす親油性のアルコキシド原料であるケイ酸エチル8.09g及びトリメチルボラート2.51gを添加した。   Next, ethanol was added as a solvent for promoting hydrolysis. Further, 8.09 g of ethyl silicate and 2.51 g of trimethyl borate, which are lipophilic alkoxide raw materials that cause polymerization, were added.

このようにして得られた混合物を、35℃の超音波洗浄器中で1時間攪拌した。加水分解・重合反応を進め、ゾルをゲル化させた。その後、2日間室温にて放置し、十分ゲル化を進めた。そして、100℃の浴槽中で乾燥させ、乾燥ゲルを得た。この乾燥ゲルを、一旦300℃で3時間加熱し、更に600℃まで温度上昇して1時間加熱することで焼結させ、ガラス固化体5.00gを得た。   The mixture thus obtained was stirred for 1 hour in a 35 ° C. ultrasonic cleaner. The hydrolysis and polymerization reaction proceeded to gel the sol. Thereafter, the mixture was allowed to stand at room temperature for 2 days, and the gelation was sufficiently advanced. And it was made to dry in a 100 degreeC bathtub, and the dried gel was obtained. The dried gel was once heated at 300 ° C. for 3 hours, further heated to 600 ° C. and heated for 1 hour to sinter, thereby obtaining 5.00 g of a glass solidified body.

上記ようにして作製したガラス固化体を粉砕し、比表面積を計測するとともに、95℃500ml湯浴に1日浸漬し、溶出重量を計測することにより、単位面積あたりの溶出速度を既存のガラス溶融固化体と比較した。その結果、本発明によって作製したガラス固化体の溶出速度は0.263g/m2 dayであり、既存のガラス溶融固化体の溶出速度0.232g/m2 dayと同等の性能を有することが確認された。 The glass-solidified material produced as described above is pulverized, measured for specific surface area, immersed in a 500 ml hot water bath at 95 ° C. for 1 day, and measured for elution weight, so that the elution rate per unit area can be determined by melting existing glass. Compared with solidified body. As a result, the dissolution rate of the vitrified produced by the present invention is 0.263 g / m 2 day, confirmed to have a dissolution rate 0.232 g / m 2 day performance equivalent existing glass melting solidified It was done.

本発明に係るガラス溶融処理方法の一例を示す工程図。Process drawing which shows an example of the glass melting processing method which concerns on this invention. 本発明に係るガラス溶融処理方法の他の例を示す工程図。Process drawing which shows the other example of the glass melting processing method which concerns on this invention.

符号の説明Explanation of symbols

10 放射性廃液
12 ガラス固化体
10 Radioactive waste liquid 12 Glass solidified body

Claims (2)

放射性廃液中に、ガラス固化体として必要なガラス物性を得るための水溶性原料、及びアルコキシドの加水分解を促進するための溶媒を添加し、更に親油性のアルコキシド原料を添加して混和し、加水分解・重合反応を進めてゾルをゲル化し、得られた湿潤ゲルを粉砕して乾燥させ、その乾燥ゲルを仮焼することによりゲル中の結晶水、溶媒を分解、揮発させ、次いで仮焼粉体を圧縮成型し、その圧縮成型体をガラス軟化点以下の温度で焼結させることにより緻密なガラス固化体にすることを特徴とする放射性廃液のガラス固化処理方法。 In the radioactive liquid waste, a water-soluble raw material for obtaining glass properties necessary as a glass solidified body and a solvent for accelerating hydrolysis of the alkoxide are added, and a lipophilic alkoxide raw material is further added and mixed. The decomposition / polymerization reaction is advanced to gel the sol, and the resulting wet gel is pulverized and dried, and the dried gel is calcined to decompose and volatilize the crystal water and solvent in the gel, and then calcined powder A method for vitrifying radioactive waste liquid, comprising compacting a body and sintering the compacted body at a temperature below the glass softening point to form a dense vitrified body. 前記水溶性原料として硝酸塩を、アルコキシドの加水分解を促進するための溶媒としてアルコールを、親油性のアルコキシド原料としてトリメチルボラートとケイ酸エチルを用いる請求項1記載の放射性廃液のガラス固化処理方法。 The nitrate as a water-soluble material, an alcohol as a solvent for promoting the hydrolysis of the alkoxide, vitrification method for treating a radioactive liquid waste according to claim 1 Symbol placement using trimethyl borate and ethyl silicate as an alkoxide material lipophilic .
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CN114242295B (en) * 2021-12-23 2024-07-19 西南科技大学 Method for solidifying radioactive waste liquid glass
CN114276013A (en) * 2021-12-31 2022-04-05 西南科技大学 Method for directly vitrifying high-level waste by utilizing microwave

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