JPS5977396A - Method of solidfying radioactive waste - Google Patents

Method of solidfying radioactive waste

Info

Publication number
JPS5977396A
JPS5977396A JP18700082A JP18700082A JPS5977396A JP S5977396 A JPS5977396 A JP S5977396A JP 18700082 A JP18700082 A JP 18700082A JP 18700082 A JP18700082 A JP 18700082A JP S5977396 A JPS5977396 A JP S5977396A
Authority
JP
Japan
Prior art keywords
resin
radioactive waste
acid
waste
mixture
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
JP18700082A
Other languages
Japanese (ja)
Inventor
冨田 俊英
祐二 南
松浦 宏之
蔭山 学史
小堀 順三
大部 悦二
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.)
Toshiba Corp
Mitsui Toatsu Chemicals Inc
Nippon Genshiryoku Jigyo KK
Nippon Atomic Industry Group Co Ltd
Original Assignee
Toshiba Corp
Mitsui Toatsu Chemicals Inc
Nippon Genshiryoku Jigyo KK
Nippon Atomic Industry Group 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 Toshiba Corp, Mitsui Toatsu Chemicals Inc, Nippon Genshiryoku Jigyo KK, Nippon Atomic Industry Group Co Ltd filed Critical Toshiba Corp
Priority to JP18700082A priority Critical patent/JPS5977396A/en
Publication of JPS5977396A publication Critical patent/JPS5977396A/en
Pending legal-status Critical Current

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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】 [発明の技術分野」 本発明t、1.熱硬化性樹脂を使用した放射性廃棄物の
固化タハ埋方法に関する。
[Detailed Description of the Invention] [Technical Field of the Invention] The present invention t.1. This invention relates to a method for solidifying and burying radioactive waste using thermosetting resin.

し発明の技術的背景とその問題点」 従来J、す、原子力発電所その他の原子力施設から発生
ずる放射性廃液は種々の処理がなされた後、最終的には
伺うかの方法で同化処理され(゛廃棄物中の放射能によ
り環境が汚染されないようにされている。
``Technical background of the invention and its problems'' Conventionally, radioactive waste fluid generated from nuclear power plants and other nuclear facilities is treated in various ways, and then finally assimilated by the following method ( ``The environment is prevented from being contaminated by radioactivity in waste.

1京子力発電所における固化処理法として一般的なもの
は、乾燥、粉末化された放射性廃棄物をセメン1−ある
いはアスファルトで固化りるセメント固化法あるいはア
スファル(・同化法C゛あるが、最近、プラスチック同
化法が優れた放用能閉じ込め能力と放射性廃棄物の減容
性の点で注目されている。
The most common solidification treatment methods used at the Ikyo Power Plant are the cement solidification method, which solidifies dried and powdered radioactive waste with cement 1- or asphalt, and the asphalt (and assimilation method C), but recently The plastic assimilation method is attracting attention for its excellent ability to contain radioactivity and its ability to reduce the volume of radioactive waste.

このようなプラスチック同化法には、同化剤としくポリ
エチレンのような熱可塑性樹脂を用いるものど、不飽和
ポリ1ステルと重含性単罪体とからなる不飽和ポリエス
テル樹脂を熱硬化性樹脂としく用いたものがあるが、特
に熱硬化性樹脂を用いたlラスチック固化法は、#11
Qtおよび重合開始剤、重合促進剤等の触媒の選択によ
り冨温にd3い(IIII!化反応の進行が可能となり
、放射性廃1!物と樹脂と触媒類が均一に混合されれば
固化剤の重合反応が常温で進行しC速やかにプラスチッ
ク同化体が得られるのぐ好ましい方法である。
In such plastic assimilation methods, a thermoplastic resin such as polyethylene is used as an assimilating agent, but an unsaturated polyester resin consisting of an unsaturated polyester and a polyester is used as a thermosetting resin. In particular, the plastic solidification method using thermosetting resin is #11.
By selecting Qt and catalysts such as polymerization initiators and polymerization promoters, it is possible to proceed with the d3 (III! conversion reaction) at the temperature of the temperature, and if the radioactive waste 1!, resin, and catalysts are uniformly mixed, the solidifying agent This is a preferred method because the polymerization reaction proceeds at room temperature and a plastic assimilate product can be obtained quickly.

しかしながら、放射性廃棄物中には熱硬化性樹脂の重合
反応を阻害する物質が含まれる場合があることが判明し
た。例えば沸騰水型原子力光電所−C発/i覆る濃縮廃
液の主成分は硫酸ナトリウム(Na 2 SOn )ぐ
あるが、この他に微量成分とLノ’(Ca 、 3+ 
、 Fe 、 Go 、’Ni 、 CI ドイツた元
素が社々にしで含まれでJ3す、特にCIの水酸化物が
存在すると熱硬化性樹脂の組合反応が著しく El害さ
れることが判明した。
However, it has been found that radioactive waste may contain substances that inhibit the polymerization reaction of thermosetting resins. For example, the main component of the concentrated waste liquid from boiling water nuclear photovoltaic power station C/i is sodium sulfate (Na 2 SOn), but in addition to this, trace components and L'(Ca, 3+
, Fe, Go, 'Ni, CI, and other elements are commonly found in the chemical industry.In particular, it has been found that the presence of CI hydroxide significantly impairs the combination reaction of thermosetting resins.

ちなみに濃縮廃液の主成分である硫酸す1−リウム粉体
ど水酸化銅粉体とを59:1となるJ、うに混合し、こ
の粉体を不飽和ポリエステル樹脂を主成分どJる熱硬化
性樹脂に粉体混入率が60重量%どなるように加え、さ
らに重合開始剤としCメチルエヂルクトンパーAキ−リ
ーイドを熱硬化性樹脂に対しU2.O重罪%、重合促進
剤とし°(ナフテン酸コバルトを熱硬化製樹脂に対し−
U0.5重量%添加混合し、−昼夜hIi置した後の状
態を調べたところ、重合反応の進行は認められるものの
ゲル状態て”反応が停止しており硬化し−Cい4丁かっ
た。
By the way, 1-lium sulfate powder, which is the main component of concentrated waste liquid, and copper hydroxide powder are mixed in a ratio of 59:1, and this powder is heat-cured with unsaturated polyester resin as the main component. The powder mixture was added to the thermosetting resin at a mixing rate of 60% by weight, and further, C methyl ethylene chloride per A key lead was added as a polymerization initiator to the thermosetting resin. %, as a polymerization accelerator (cobalt naphthenate for thermosetting resins)
When 0.5% by weight of U was added and mixed and the condition was examined after being left for day and night, it was found that although progress of the polymerization reaction was observed, it was found that the reaction had stopped and the mixture had hardened.

これは銅の水酸化物は両性的性質を有しC次式のJ、う
に解離し、 C”   (OH)  2  ;======Cu  
”  ”  +  2 0 1−l  −CU (01
」) 2 =士cuQ2−’ −+2 El ”ここで
発生する11+は、重合開始剤、重合促進剤にj;り生
ずる一次ラジカルおJ:びこれに引き続ぎ発生する連鎖
反応におけるラジカルと反応してラジカルを不活性化゛
するためであると考えられる。
This is because copper hydroxide has amphoteric properties and dissociates into J of the following formula, C" (OH) 2 ;======Cu
” ” + 2 0 1-l -CU (01
'') 2 = CuQ2-' -+2 El ``The 11+ generated here reacts with the primary radicals generated by the polymerization initiator and the polymerization accelerator, and with the radicals generated in the subsequent chain reaction. This is thought to be to inactivate radicals.

このように酸性物質を含んだ熱硬化性樹脂の重合硬化が
極め(°困ガであることは、次の実験にJ:り確かめら
れる。
The following experiment confirms that the polymerization and curing of thermosetting resins containing acidic substances is extremely difficult.

すなわち硫酸ナトリウム59重量%、不飽和ポリエステ
ル樹脂を主成分とする熱硬化性樹脂40単用%、水酸化
鋼1重罪%を混合し、この混合物にコバルト60のγ線
を7メガレントゲン照射しても、混合物は液状のままで
あり、重合反応の進行は認められなかった。一方、水酸
化銅を混合しないで熱硬化性樹脂と硫酸ナトリウムのみ
の場合は完全にl1llj化しC強固なプラスチック同
化体が得られた。
That is, 59% by weight of sodium sulfate, 40% of a thermosetting resin whose main component is unsaturated polyester resin, and 1% of hydroxide steel were mixed, and this mixture was irradiated with cobalt-60 gamma rays at 7 megaroentgen. However, the mixture remained liquid, and no progress of the polymerization reaction was observed. On the other hand, when only the thermosetting resin and sodium sulfate were used without mixing copper hydroxide, 11llj was completely converted and a strong plastic assimilated product was obtained.

このよ−)にラジカル重合にJ:り硬化Jる熱硬化性樹
脂は、ラジカルと反応り−る1−1÷の発生源、例えば
水酸化銅が(f7I!Jる場合1使化し難く、放射性廃
棄物と熱硬化性樹脂との混合物は未重合ある0は硬化不
充分のまま貯蔵容器内に貯蔵されることになる。この混
合物番よ未不合のままでは放射能閉じ込め能力旧1とん
ど期待できず、そのうえ未重合の同化剤【よ消防法ト危
険物に分類さit 1.:もの−ぐAリリ、放口・1↑
JII¥i!東物をより危険な状態におくことになると
いう問題があった。
In this way, thermosetting resins that undergo radical polymerization and harden are difficult to convert into 1-1 ÷ sources that react with radicals, such as copper hydroxide (f7I!J). A mixture of radioactive waste and thermosetting resin will be stored in a storage container without polymerization or with insufficient hardening.If this mixture remains unpolymerized, the radioactivity trapping capacity will decrease. What's more, the unpolymerized assimilation agent [it is classified as a dangerous substance under the Fire Service Act] 1.
JII¥i! The problem was that it would put Tomono in a more dangerous situation.

]発明の目的」 本発明はこのような問題を解消するためなされ15−も
のひ、放射性廃棄物中に硬化反応を妨害する水酸化1f
Jが含有されCいても硬化が充分に行なわれる放射性廃
棄物の同化処理方法を捉供づ゛ることを目的とする。
] Purpose of the Invention The present invention has been made to solve these problems.
The object of the present invention is to provide a method for assimilating radioactive waste that can be sufficiently cured even if it contains J and C.

[発明の概要] すなわち本発明方法は、水酸化銅を含有する放射性FJ
ト棄物の熱硬化性樹脂による同化処理を、フアルカリ性
物質の存在下で行なうことを特徴とする。
[Summary of the invention] That is, the method of the present invention is a method for producing radioactive FJ containing copper hydroxide.
The method is characterized in that the assimilation treatment of waste with a thermosetting resin is carried out in the presence of a halogen substance.

本発明に使用する熱硬化性樹脂は、不飽和ポリ−Lス・
アルと重合性単昂体とからなる不飽和ポリ−1−スプル
樹脂であり、不飽和ポリ」−ステルと(よ二塩基酸成分
とグリコール成分とのJステル化重縮合物を指し、該二
塩基酸成分としく代表的なもの&よ、例えばマレイン酸
、無水マレイン酸、フマル酸、イタコン酸、シ1〜ラコ
ン酸、メサコン酸、塩素化マレイン酸等のα、β−不飽
和二塩塁酸並び【こ無水フタル酸、イソフタル酸、テレ
フタル酸、モノクロルフタル酸、ジクロルフタル酸、ト
リク【1ノ1ノフタル酸、ヘラ1−醸“、テトラクロロ
無水フタル酸、アトラブロモ無水フタル酸、エンドメチ
レンチF・うじドロ無水フタル酸、テl〜ラヒド1〕1
無水フタル酸、アジピン酸、セバシン酸、]ハク酸舌の
飽和二塩基酸であり、上記したα、β−不飽和二塩吊酸
ど飽和二塩基酸との併用も含まれることは勿論Cある。
The thermosetting resin used in the present invention is an unsaturated polyester resin.
It is an unsaturated poly-1-sprue resin consisting of aluminum and a polymerizable monomer, and refers to a J-stellated polycondensate of an unsaturated polyester, a dibasic acid component, and a glycol component. Typical basic acid components include α,β-unsaturated dibases such as maleic acid, maleic anhydride, fumaric acid, itaconic acid, laconic acid, mesaconic acid, and chlorinated maleic acid. Acid list: Phthalic anhydride, isophthalic anhydride, terephthalic acid, monochlorophthalic acid, dichlorophthalic acid, trichlorophthalic acid, tetrachlorophthalic anhydride, atrabromophthalic anhydride, endomethylenethiF・Ujidrophthalic anhydride, Tel-Rahydride 1] 1
It is a saturated dibasic acid such as phthalic anhydride, adipic acid, sebacic acid, and succinic acid, and of course also includes combinations with saturated dibasic acids such as the above-mentioned α, β-unsaturated dichlorosulfonic acid. .

他方、上記グリ:TJ−ル成分として代表的なものC7
L、例えば玉チレングリコール、プロピレングリ−J−
ル、ジJ′JIノングリ−コール、ジブ上1ピレングリ
−」−ル、1へり上チレングリ=1−ル、1.4−ブΣ
レングリニ]−ル、ネオベンブールグリコール−1シレ
ングリコール、オクチルグリコール、ビスフェノールΔ
・ジA:Vシ」チルl−チル(j+加物、水添ビスフェ
ノールA、ビスフェノールA・ジオ:1:シゾ1−1ピ
ルーrーデルイ・1加物おJ:び−丁ヂレンAニ1リイ
ド、/1−1ピレンAキザイド、ブチレンオキサ−イド
′簀のアル、ルンAキリイド、まだジシ9日ペンタジJ
−ン、デック1」ペンタジェン重合体等C・あり、必要
に応じ(’ 1〜リメチ1]−シブ11パン、グリt!
リンの多価アル−]−ルを所望重加えることもできる。
On the other hand, C7, which is typical as the above-mentioned Green: TJ-le component.
L, e.g. tamethylene glycol, propylene glycol J-
J'JI non-glycol, 1 pyrene glycol on the jib, 1 pyrene glycol on the edge, 1.4 pylene glycol, 1.4-butyl
Renglilin], neobenbul glycol-1silene glycol, octyl glycol, bisphenol Δ
・Di-A: V-chill l-chill (j+additive, hydrogenated bisphenol A, bisphenol A ・Gio: 1: schizo 1-1 pyru-r-delui 1-additive J: bi-dilene A-1 Lid, /1-1 Pyrene A Kizaide, Butylene Oxide'Al, Run A Kiriido, Still Jishi 9th Pentaji J
-N, Deck 1'' Pentadiene polymer etc. C・ Yes, as required (' 1 ~ Rimethi 1] - Shiv 11 Pan, Grit!
A desired amount of polyhydric alcohol of phosphorus can also be added.

本発明に使用される不飽和ポリ1スプル樹脂とじCは、
酸価80以下のものが好ましい。
The unsaturated poly 1 sprue resin binding C used in the present invention is
Those having an acid value of 80 or less are preferred.

fF合性中川用どしく(−未不飽和ポリ−[ステルと共
車合司能なづべCの弔鉛体が使用Cきる。そのうち代表
的なものとしでは、例えばスヂレン、αーメヂルスチレ
ン、ビニルトル土ン、りl:l INスチレン、アクリ
ル酸、メタクリル酸のアルキルコースチル1−リアリル
シアヌレ−1・、トリアリルイソシアヌレート、アクリ
ルアミドがある,、 Q!iにスブーレンエノマー、メ
タクリル酸メチルが望ましい。これらl)1吊体の好)
内な使用量は、不飽和ポリエステルとの合削但に対して
20へ・80単指%の範囲ぐある。
fF-combined Nakagawa Yodoshiku (-unsaturated poly-[stell and co-combined with Nazube C) can be used. Typical examples include styrene, α-methylstyrene, and vinyl styrene. Soil, Ri:l IN Styrene, acrylic acid, methacrylic acid alkyl costyl 1-lylyl cyanurate-1, triallyl isocyanurate, acrylamide, Q!i is preferably suburene enomer, methyl methacrylate .These l) 1 hanging body)
The amount used ranges from 20% to 80% when combined with unsaturated polyester.

この不飽和ポリエステル樹脂には必要に応じCハイド【
1キノン、ベンゾキノン、劃−プチルカテー1−ル等の
重合禁止剤が含まれる。
This unsaturated polyester resin can be used with C-hyde [
Polymerization inhibitors such as 1-quinone, benzoquinone, and butylene quinone are included.

かくし”C得られた本発明組成物に(J、炭酸カルシウ
ム、りIノー、石こう、水酸化アルミニラ11、ぼう硝
等の充填剤、樹脂の改質材としCジブチルノタレ−1−
、ジゾチルマレ土−1−、ジオクブルフタレーI・等の
可塑剤、また1〜リブチルフAスフ]。
To the obtained composition of the present invention (J, calcium carbonate, resin, gypsum, alumina hydroxide 11, fillers such as sulfur salt, etc., and as a resin modifier, C dibutylnotare-1-
, dizotyl male earth-1-, diocvulphthalate I, etc.;

−1−、トリスフ【」ロエチルホスフエー1−等の11
リリン酸ニスデル、塩素化パラフィン、三酸化アンチモ
ン、デカノロモジフェニルエーテル等の難燃剤、右11
質もしくは無機質の顔料、熱可塑性樹脂等の低収縮剤等
を添加することができる。
-1-, trisph [''loethyl phosphene 1-, etc. 11]
Flame retardants such as Nisdel lyphosphate, chlorinated paraffin, antimony trioxide, decanolomodiphenyl ether, right 11
Natural or inorganic pigments, low shrinkage agents such as thermoplastic resins, etc. can be added.

上記した不飽和ポリニスアル樹脂の重合同化方ン入とし
く(、1、イ)1ツ(金属塩とケ1〜ンバーオキザイド
(ご31、るhンノいベンゾイルパー:、t 二I=リ
−イドとソ゛メナルアニリンまたはジエチルアニリン(
ごよる方法、またベンゾイルパー′A−1−リ−イド、
t−ブチルパーΔキシベンゾ−I −’ l−による高
温分解ン人等があげられる。
Polymerization of the above-mentioned unsaturated polyester resin (1, 1) 1 (metal salt and 1 - amber oxide (31, 2) and somemenalaniline or diethylaniline (
According to the method, also benzoyl per'A-1-lead,
Examples include high-temperature decomposition with t-butylperΔxybenzo-I-'l-.

本発明に便用りる]アルカリ性物質としくはノ゛トリウ
ム、7グ諸シウム、カルシウムトtの水酸化物(1・)
るい(3)ゴiif化物の、粉末あるいは水溶液があげ
られる。J、た、(−のアルカリ性物質の混合は予め放
用性廃東物中11−含有さ1j ”U t> J、く、
あるいは熱硬化↑(1樹脂と放64 t!I−廃棄物と
を混合覆る際にアルカリ性物1物費を添加りるにうにし
Cもよい。さらにまた、重合1je進剤にアルカリ性物
質を含有しC添加するようにしCt)よい。添加量は水
酸化銅とほぼ同当債ど’JるiTt /JNり1ましい
[Used conveniently in the present invention] Examples of alkaline substances include hydroxides of sodium chloride, sodium chloride, calcium hydroxide (1)
Examples include powders or aqueous solutions of blue (3) goiif compounds. J, t, (- The mixture of alkaline substances is preliminarily mixed with 11-contained 1j ``U t> J, ku,
Alternatively, thermosetting ↑ (1 resin and 64 t! I- It is also good to add 1 alkaline substance when mixing and covering the waste. Furthermore, it is also possible to add an alkaline substance to the polymerization 1je promoter. It is better to add Ct). The amount added is almost the same as that of copper hydroxide.

本発明におい((ま乾燥、粉末化した放射fL廃東物に
熱硬化性樹脂を添加混合し、さらにアルカリ性物質を均
一に混合させた後臣合聞始剤a3よび重合(j7メ(剤
を混合して常湿で放置させる。
In the present invention, a thermosetting resin is added to and mixed with dried and powdered radiation fL waste, and an alkaline substance is evenly mixed therein. Mix and let stand at normal humidity.

[発明の実施例] 次に本発明の実施例につい−(説明覆る。[Embodiments of the invention] Next, examples of the present invention will be explained.

実施例1 1IllI酸プ1〜リプ1〜リウム59不飽和ポリニス
デル樹脂を生成分どする熱砂化性樹IIiLi’I O
重U)%、水酸化銅1重量%の混合物にψ合間始剤メチ
ルエブールクトンバーオキリ゛イドを熱硬化f1−樹脂
に対して2重量%、中台促進剤ナノデン酸」パル1−を
熱硬化性樹脂に対して0.5重量%それぞれ添加)化合
した。この混合物にアルカリ性物5!iとして水酸化す
i〜リウムの20%溶液を熱硬化性樹脂に対しく5重量
%添加しさらに混合した。−昼夜tJ!iHvi後強固
なシラスデック同化体が得られた。ゲル化時間および得
られたシラスデック同化体の表面)I!I!度を表に示
T0 実施例t 5東都%の水酸化ナトリウムの20%′?B液を1中!
v%の酸化マグネシウムに替えた以外は実施例1ど同様
にし°(tl?;合したところ、−昼夜放置後ぐ強固4
1シンスナック固化体が得られた。ゲル化時間おJ、ひ
表面硬1′!14同様に表に示す−0実施例 5重り%の水酸化)I・リウム20%溶液を水酸化マグ
ネシウム1重ω%に賛えた以外は実施例1ど同様にしC
混合し、−昼夜放置したところ強固41プラスチツク同
化休が得られた。グル化時間おJ、び表面硬度を表に示
す。
Example 1 1IllI acid Pr 1 ~ LiP 1 ~ Lium 59 Thermal sanding tree IIiLi'IO for producing and separating unsaturated polynisder resin
In a mixture of 1% by weight of copper hydroxide, 2% by weight of the thermosetting f1-resin, 2% by weight of the intermediate initiator methyl ethylene chloride peroxide, and 1% by weight of the intermediate accelerator nanodenic acid Pal 1- (added at 0.5% by weight each to the thermosetting resin). Add 5 alkaline substances to this mixture! A 20% solution of sourium to hydroxide (i) was added to the thermosetting resin in an amount of 5% by weight and further mixed. -Day and night tJ! A strong Shirasudek assimilate was obtained after iHvi. Gelation time and surface of the obtained Shirasdek assimilate) I! I! The degree is shown in the table T0 Example t 5 Toto% of sodium hydroxide 20%'? One part of liquid B!
Example 1 was repeated except that magnesium oxide of v% was used.
A 1-thin snack solidified body was obtained. Gel time is J, surface hardness is 1'! 14 Similarly shown in the table -0 Example 5 Hydroxide (wt%) I. Lium 20% solution was added to magnesium hydroxide 1 wt ω% C
When the mixture was mixed and left for day and night, a strong 41 plastic assimilation period was obtained. The gluing time and surface hardness are shown in the table.

実施例1 同様IJ水酸化す1〜シリウム0%溶液を1小丘%の酸
化カルシウムに替えた以外は実施例1と同様にしく混合
し、−昼夜放防したところ強固なプラスブック同化が得
られた。
Example 1 The mixture was mixed in the same manner as in Example 1 except that the IJ hydroxide 1-silium 0% solution was replaced with 1% calcium oxide, and the mixture was exposed day and night, resulting in strong plus book assimilation. It was done.

実施例5 同IJに水酸化す:−リウムの20%溶液を1重昂%の
水酸化カルシウムに替えた以外は実施例1と同様にLノ
(混合し)、−昼夜放置したところ強固4′r−グラス
ブツク同化休が得られた。ゲル化時間d3よび表面硬度
を表に示す。
Example 5 The same IJ was hydrated: The mixture was mixed in the same manner as in Example 1, except that the 20% solution of -lium was replaced with 1% calcium hydroxide. r-glass book assimilation holiday was obtained. The gelation time d3 and surface hardness are shown in the table.

なお、表中の参考例は水酸化’Mn3よびアルカリ性物
質の存在しない例を示す。
Note that the reference examples in the table are examples in which hydroxide 'Mn3 and alkaline substances are not present.

(以下余白) ;トJIS   K7215 (以下余白) 「発明の効果] 以上説明したように本発明方法によれば、水酸化銅のよ
うな重合硬化反応をM害するものが存在していても硬化
が充分(−jなわれ、強固なプラス1−ツタ同化体が得
られる。
(Hereinafter in the margin); To JIS K7215 (Hereinafter in the margin) "Effects of the Invention" As explained above, according to the method of the present invention, even if there is a substance such as copper hydroxide that harms the polymerization curing reaction, curing is not possible. Sufficient (-j), a strong plus 1- ivy assimilate is obtained.

代理人弁理士   須 111  佐 −第1頁の続き ■出 願 人 三井東圧化学株式会社 東京都千代田区霞が関3丁目2 番5号 ■出 願 人 東京芝浦電気株式会社 川崎市幸区堀川町72番地Representative Patent Attorney Su 111 Sa - Continued from page 1 ■Submitted by: Mitsui Toatsu Chemical Co., Ltd. 3-2 Kasumigaseki, Chiyoda-ku, Tokyo number 5 ■Submitted by: Tokyo Shibaura Electric Co., Ltd. 72 Horikawa-cho, Saiwai-ku, Kawasaki City

Claims (1)

【特許請求の範囲】 (1)水酸化銅を含有する放射性廃棄物の、熱硬化性樹
脂【こよる固化処理を、アルカリ性物質の存在下0行な
うことを特徴とする放0=I iff廃棄物の同化処理
力法。 (2〉熟)ゆ化性樹脂は、不飽和ポリエステルとf11
合性中性中とからなる不飽和ポリエステル樹脂である’
R1i’l請求の範囲第1]i′i記載の放射性廃棄物
の同化処理方法。 (3)アルカリ性物質は、水酸化銅とほぼ同当坦どなる
よう熱伺j化t!l樹脂と放射性廃棄物どの混合物に添
加される特許請求の範囲第1項または第2項記載のh9
削性廃東物の同化処理方法。
[Claims] (1) Thermosetting resin of radioactive waste containing copper hydroxide [I iff waste characterized in that the solidification treatment is carried out in the presence of an alkaline substance] anabolic processing power method. (2〉Mature) Enamel resin is unsaturated polyester and f11
It is an unsaturated polyester resin consisting of a synthetic neutral medium.
R1i'l Claim 1] The method for assimilating radioactive waste according to i'i. (3) Alkaline substances are heated to almost the same level as copper hydroxide! h9 according to claim 1 or 2, which is added to any mixture of resin and radioactive waste.
Assimilation treatment method for scraping waste.
JP18700082A 1982-10-25 1982-10-25 Method of solidfying radioactive waste Pending JPS5977396A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP18700082A JPS5977396A (en) 1982-10-25 1982-10-25 Method of solidfying radioactive waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP18700082A JPS5977396A (en) 1982-10-25 1982-10-25 Method of solidfying radioactive waste

Publications (1)

Publication Number Publication Date
JPS5977396A true JPS5977396A (en) 1984-05-02

Family

ID=16198447

Family Applications (1)

Application Number Title Priority Date Filing Date
JP18700082A Pending JPS5977396A (en) 1982-10-25 1982-10-25 Method of solidfying radioactive waste

Country Status (1)

Country Link
JP (1) JPS5977396A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0429098A (en) * 1990-05-25 1992-01-31 Toshiba Corp Method for solidifying radioactive waste with plastic

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0429098A (en) * 1990-05-25 1992-01-31 Toshiba Corp Method for solidifying radioactive waste with plastic

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