JPS63253298A - Method of processing radioactive washing waste liquor - Google Patents

Method of processing radioactive washing waste liquor

Info

Publication number
JPS63253298A
JPS63253298A JP8834387A JP8834387A JPS63253298A JP S63253298 A JPS63253298 A JP S63253298A JP 8834387 A JP8834387 A JP 8834387A JP 8834387 A JP8834387 A JP 8834387A JP S63253298 A JPS63253298 A JP S63253298A
Authority
JP
Japan
Prior art keywords
waste liquid
radioactive
laundry
salt compound
water
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
JP8834387A
Other languages
Japanese (ja)
Other versions
JPH0677070B2 (en
Inventor
紀昭 武士
菊池 恂
弘行 土屋
有馬 省一
位 長山
鈴木 悌
玉田 慎
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.)
Hitachi Service Engineering Co Ltd
Hitachi Ltd
Hitachi Kyowa Engineering Co Ltd
Original Assignee
Hitachi Kyowa Kogyo Ltd
Hitachi Service Engineering Co Ltd
Hitachi 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 Hitachi Kyowa Kogyo Ltd, Hitachi Service Engineering Co Ltd, Hitachi Ltd filed Critical Hitachi Kyowa Kogyo Ltd
Priority to JP62088343A priority Critical patent/JPH0677070B2/en
Publication of JPS63253298A publication Critical patent/JPS63253298A/en
Publication of JPH0677070B2 publication Critical patent/JPH0677070B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

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〕 本発明は、放射性洗濯廃液の処理方法に係り、特に発泡
性の著しい洗剤混入放射性廃液の粉体化処理及び造粒処
理に好適な放射性洗濯廃液の処理方法に関する。
Detailed Description of the Invention [Field of Industrial Application] The present invention relates to a method for treating radioactive laundry waste liquid, and in particular, a radioactive washing method suitable for powdering and granulation treatment of highly foaming detergent-containing radioactive waste liquid. Concerning a waste liquid treatment method.

〔従来の技術〕[Conventional technology]

原子力発電所などにおいては作業衣の洗濯等によって洗
剤が混入した放射性廃液が発生する。従来は、約115
00に濃縮減容した後、セメント固化等により保管して
いる。この保管量をさらに低減させるために、含有水を
除却して再利用し、界面活性剤のみを廃棄する方法が合
理的である。
At nuclear power plants and other facilities, radioactive waste liquid mixed with detergent is generated when working clothes are washed. Conventionally, approximately 115
After concentrating and reducing the volume to 0.00, it is stored by solidifying with cement. In order to further reduce this storage amount, it is reasonable to remove and reuse the contained water and discard only the surfactant.

水分を分離除却するためには、蒸発乾燥処理が用いられ
る。ところが、界面活性剤が高粘性物質であるため、粉
体化及び造粒が非常に困難であること、界面活性剤が発
泡性を有しており、粉体化の際発泡し蒸気側へ不純物が
移行するため、分離した水が汚れることなどの問題があ
る。つまり不純物が蒸気側へ移行する割合であるDF(
供給側不純物/蒸気側不純物)が小さくなる。
Evaporative drying treatment is used to separate and remove moisture. However, since the surfactant is a highly viscous substance, it is extremely difficult to powder and granulate it, and the surfactant has foaming properties, which causes impurities to flow into the steam when powdered. This causes problems such as the separated water becoming contaminated. In other words, DF(
Supply side impurities/steam side impurities) are reduced.

特公昭60−38680号によれば、洗濯廃液を単独処
理する際界面活性剤の以上のような性質を抑えるため、
廃液に活性炭などの吸着剤を添加し物理的に界面活性剤
を吸着させれば、粉体化が可能になることが論じられて
いる。
According to Japanese Patent Publication No. 60-38680, in order to suppress the above-mentioned properties of surfactants when treating laundry waste liquid alone,
It has been discussed that pulverization becomes possible by adding an adsorbent such as activated carbon to the waste liquid to physically adsorb the surfactant.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

上記従来技術は、乾燥時に界面活性剤が発泡する問題に
ついては、活性炭などの吸着材を添加することにより解
決したが、造粒性の点についての配慮がされていない。
In the above-mentioned prior art, the problem of foaming of the surfactant during drying was solved by adding an adsorbent such as activated carbon, but no consideration was given to granulation properties.

従来技術により作成したペレット(造粒物)は、比重が
小さく減容性について問題があった。
Pellets (granules) produced by conventional techniques have a low specific gravity and have a problem with volume reduction properties.

これは、界面活性剤を物理吸着させる吸着剤として、多
量の活性炭またはゼオライトを使用するため、廃棄物量
が増大してしまうという問題を有しており、さらにこれ
ら吸着剤の比重が軽く、かつ造粒性の悪い物質であるた
め、造粒しても比重が小さく、結果的にさらに減容性を
低下させることになる。
This method uses a large amount of activated carbon or zeolite as an adsorbent to physically adsorb the surfactant, which has the problem of increasing the amount of waste.Furthermore, the specific gravity of these adsorbents is light and Since it is a substance with poor granularity, its specific gravity is small even when granulated, resulting in further reduction in volume reduction properties.

減容性を向上させるために、添加量が少量で消泡効果の
あるシリコン系消泡剤を使用することを考えたが、消泡
剤、界面活性剤共に高粘性物質であり、粉体間に界在し
粉体化造粒が困難となる現象を程し、混合量には限界が
あった。
In order to improve volume reduction performance, we considered using a silicone antifoaming agent that has an antifoaming effect in small amounts, but both the antifoaming agent and the surfactant are highly viscous substances, and There was a limit to the mixing amount due to the phenomenon that powdering and granulation was difficult.

本発明の目的は、吸着剤を用いずに消泡し乾燥時のDF
を向上させると共に、減容性と造粒性に優れた放射性洗
濯廃液の処理方法を提供することである。
The purpose of the present invention is to eliminate foaming without using an adsorbent and to reduce the DF during drying.
It is an object of the present invention to provide a method for treating radioactive laundry waste liquid that improves the quality of radioactive laundry waste and has excellent volume reduction properties and granulation properties.

〔問題点を解決するための手段〕[Means for solving problems]

本発明は、上記目的を達成するために、アルカリ土類金
属と鉱酸の水溶性塩類化合物を添加し。
In order to achieve the above object, the present invention adds a water-soluble salt compound of an alkaline earth metal and a mineral acid.

界面活性剤とアルカリ土類金属とを反応させて沈澱性塩
類化合物とすることにより界面活性剤を原因とする発泡
を抑制し、洗濯廃液と他の廃液(ホウ酸廃液、硫酸ナト
リウム廃液、硝酸ナトリウム廃液等)を混合することに
より界面活性剤の影響を最小限にして粉体化し、造粒に
適合しうる粉体を生成させる方法を提案するものである
By reacting a surfactant with an alkaline earth metal to form a precipitable salt compound, foaming caused by the surfactant is suppressed, and washing waste liquid and other waste liquids (boric acid waste liquid, sodium sulfate waste liquid, sodium nitrate waste liquid) are This paper proposes a method to minimize the influence of surfactants by mixing waste liquid, etc.) to produce a powder suitable for granulation.

すなわち、洗濯廃液中の洗剤成分に対し、アルカリ土類
金属と鉱酸の水溶性塩類化合物を10重量%以上添加す
ることにより、目的が達成される。
That is, the objective is achieved by adding 10% by weight or more of a water-soluble salt compound of an alkaline earth metal and a mineral acid to the detergent component in the laundry waste liquid.

〔作用〕[Effect]

界面活性剤は、親水基と疎水基を持つため、気液界面へ
吸着、配向し単分子膜を形成して表面張力を低下させる
。洗濯廃液はこの界面活性剤が入っているため表面張力
が低く発泡しゃすい6アルカリ土類金属を添加すること
により、界面活性剤の陰イオン基(脂肪酸の長鎖アルキ
シル)と反応し、溶m度の小さい沈澱性塩類となり、単
念子膜の形成を防止し、表面張力の低下を防ぐことにな
る。
Since surfactants have hydrophilic and hydrophobic groups, they are adsorbed and oriented to the gas-liquid interface, forming a monomolecular film and lowering the surface tension. Laundry waste liquid contains this surfactant, so it has a low surface tension and is easy to foam.By adding an alkaline earth metal, it reacts with the anionic group (long chain alkyl of fatty acid) of the surfactant, and the solution becomes muffled. It becomes a precipitable salt with a low degree of precipitation, which prevents the formation of a singleton film and prevents a decrease in surface tension.

以上の作用により泡が蒸気側へ移行せず、DFが向上す
る。
Due to the above action, bubbles do not move to the steam side, and DF is improved.

また、沈澱性の塩類とすることにより、高粘性物質をよ
り固形分化しやすくできるため、他の廃液と混合処理し
た場合、洗濯廃液の混入量の増加が可能となり、非常に
減容性に優れた処理方法となった。
In addition, by using precipitable salts, highly viscous substances can be more easily solidified, so when mixed with other waste liquids, it is possible to increase the amount of laundry waste liquid mixed in, and it has excellent volume reduction properties. This is a new processing method.

〔実施例〕〔Example〕

洗剤を含んだ放射性洗濯廃液に、アルカリ土類金属と鉱
酸との水溶性塩類化合物を添加して遠心薄膜乾燥機で処
理したところ、乾燥時に発泡がなくなり、乾fi機のD
Fは洗剤を含まない廃液と同等になった。また生成した
粉体について造粒機で造粒したところ、物性の良好なペ
レットが作成できた。
When radioactive laundry waste containing detergent was treated with a water-soluble salt compound of alkaline earth metals and mineral acids in a centrifugal thin film dryer, foaming disappeared during drying, and the D
F became equivalent to the waste liquid that did not contain detergent. Furthermore, when the resulting powder was granulated using a granulator, pellets with good physical properties were created.

本発明は、この実験結果に基づいてなされたものである
。この実験結果について以下に示す。
The present invention was made based on the results of this experiment. The results of this experiment are shown below.

洗剤に対するアルカリ土類金Bc塩の適正添加量を検討
した結果を第2図に示す。
Figure 2 shows the results of a study on the appropriate amount of alkaline earth gold Bc salt to be added to detergents.

洗剤に対するアルカリ土類金属塩の添加量と蒸留時に蒸
留側に移行する洗剤濃度の関係を示すが。
It shows the relationship between the amount of alkaline earth metal salt added to detergent and the concentration of detergent transferred to the distillation side during distillation.

第2図から明らかなように、洗剤に対し10重量%以上
添加すれば蒸留側に移行する洗剤濃度を大幅に低くおさ
えられることがわかった。
As is clear from FIG. 2, it was found that if 10% by weight or more of detergent was added to the detergent, the detergent concentration transferred to the distillation side could be kept significantly low.

上記結果を基に、アルカリ土類金属塩のうち、1種以上
を、消泡効果が発現する最小量混合しくアルカリ土類金
属塩の種類により若干差がある)、伝熱面精1.2dの
遠心薄W4乾燥機に、流量50kg/hrで供給し、蒸
発乾燥処理した。
Based on the above results, one or more of the alkaline earth metal salts should be mixed in the minimum amount to achieve the defoaming effect (there may be slight differences depending on the type of alkaline earth metal salt), and the heat transfer surface roughness should be 1.2 d. It was supplied to a centrifugal thin W4 dryer at a flow rate of 50 kg/hr, and subjected to evaporation drying.

上記粉体を打錠機(タブレット型造粒機)で造粒した結
果を第3図に示す。
The result of granulating the above powder using a tablet machine (tablet type granulator) is shown in FIG.

全固形分中の洗剤濃度とペレット強度(相対比)の関係
について示すが、第3図から明らかなように、洗剤濃度
が全固形分中で大きくなるほど、ベレット強度が低下す
る傾向にある。さらに限界を越えて洗剤が多量に含まれ
ると、造粒時に座屈し成型することが不可能となる。こ
の実験結果から廃液の全固形分中の洗剤含有濃度が16
重量%以下であれば、造粒可能であることがbかった。
The relationship between the detergent concentration in the total solid content and pellet strength (relative ratio) will be shown. As is clear from FIG. 3, the pellet strength tends to decrease as the detergent concentration increases in the total solid content. Furthermore, if a large amount of detergent is contained beyond the limit, the pellets will buckle during granulation, making it impossible to mold them. From the results of this experiment, the concentration of detergent in the total solid content of the waste liquid was 16
It was found that granulation was possible if the amount was less than % by weight.

以下に具体的実施例を示す。Specific examples are shown below.

〈実施例1〉 本発明の実施例1を第1図を基に説明する。<Example 1> Embodiment 1 of the present invention will be explained based on FIG.

供給タンク5に、ホウ酸廃液2と界面活性剤を含有する
洗濯廃液1を混合し、10重量%の廃液とする。塩化バ
リウム3をあらかじめ消泡に必要な量を測定した値だけ
供給タンク5へ添加する。
A boric acid waste liquid 2 and a washing waste liquid 1 containing a surfactant are mixed in a supply tank 5 to form a 10% by weight waste liquid. Barium chloride 3 is added to the supply tank 5 in a predetermined amount necessary for defoaming.

(本実施例の場合は、洗剤量に対し45重量%の塩化バ
リウムを添加した。)作成した廃液の固定分量の16重
量%が、洗剤であるように混合した。
(In the case of this example, barium chloride was added in an amount of 45% by weight based on the amount of detergent.) The detergent was mixed in such a way that 16% by weight of the fixed amount of the prepared waste liquid was detergent.

1.2ポの乾燥機5oに上記廃液を供給し。1. Supply the above waste liquid to a 2-pot dryer 5o.

50kg/hrで乾燥粉体化した。蒸気は、ミストセパ
レータ11で固形分を除去され、復水器12で液化され
、濃縮器へ戻される。生成した粉体は、粉体ホッパー6
へ充填され、造粒機8でバインダホッパー7内のバイン
ダと混合した後1円柱形(φ28X28t)に成型され
る。成型されたペレットはホッパー9で計量しドラム缶
1°0に充填される。
It was dried and powdered at a rate of 50 kg/hr. The solid content of the steam is removed by a mist separator 11, liquefied by a condenser 12, and returned to the concentrator. The generated powder is transferred to powder hopper 6
After being mixed with the binder in the binder hopper 7 in the granulator 8, it is molded into a cylindrical shape (φ28×28t). The molded pellets are weighed in a hopper 9 and filled into a drum 1°0.

第1図のAとBをサンプリングし乾燥機50の除染係数
を測定したところ、消泡剤添加前に比べて除染係数が7
倍になった。
When we sampled A and B in Figure 1 and measured the decontamination coefficient of the dryer 50, we found that the decontamination coefficient was 7 compared to before adding the antifoaming agent.
It's doubled.

また生成したペレットは、造粒時に座屈することなく、
比重2強度とも十分なペレットであった。
In addition, the generated pellets do not buckle during granulation,
The pellets had sufficient specific gravity and strength.

さらに1発泡が完全に抑制されたので、洗剤が蒸気とい
っしょにミストセパレータや復水器側に移行する量が、
大幅に低減でき、液化後の濃縮器への悪影響も阻止でき
た。
Furthermore, since foaming has been completely suppressed, the amount of detergent that migrates to the mist separator and condenser side with steam is reduced.
It was possible to significantly reduce the amount of water and prevent any adverse effects on the concentrator after liquefaction.

〈実施例2〉 本実施例2を第4図を基に説明する。<Example 2> The second embodiment will be explained based on FIG. 4.

供給タンク5に、ホウ酸廃液2と界面活性剤を含有する
洗濯廃液1を混合し、固形分が10ffi量%の廃液と
する。塩化バリウム3を供給タンク5へ混合して消泡す
る。作成した廃液の固形分量の16重量%が洗剤である
ように混合した。
A boric acid waste liquid 2 and a washing waste liquid 1 containing a surfactant are mixed in a supply tank 5 to form a waste liquid having a solid content of 10ffi%. Barium chloride 3 is mixed into the supply tank 5 and defoamed. The resulting waste liquid was mixed so that 16% by weight of the solid content was detergent.

炉床上の同化粒子(流動媒体)をヒータ16で加熱した
空気を仮焼炉ガスブロア17で浮遊させた流動層を有す
る仮焼炉13へ、上記廃液を噴霧供給する。噴霧液滴は
流動媒体に接触して乾燥。
The waste liquid is sprayed and supplied to a calciner 13 having a fluidized bed in which air in which assimilated particles (fluidized medium) on the hearth are heated by a heater 16 is suspended by a calciner gas blower 17 . The spray droplets dry on contact with the fluidizing medium.

仮焼され、仮焼生成物は流動媒体表面に包状に付着、生
成する。これにより流、vJa体は成長し、相互衝突等
により小片を生ずる。このうち微細なものは気流に同伴
されて炉外へ排出されサイクロンセパレータ18で固形
分を捕取し粉体ホッパ−6に集められる。造粒機8でペ
レット状に造粒しペレットホッパー9に充填した後、ド
ラム缶10へ充填される。さらにスクラバー19で固形
分が分解され、復水器21で液化される6 本実施例によれば、泡が気層へ同伴されることなく、粉
体化され、生成した粉体は造粒時に座屈することなく、
比重2強度とも従来と同様十分なペレットを成型するこ
とができた。
The calcined product adheres to and forms a envelope on the surface of the fluid medium. As a result, the vJa bodies grow and produce small pieces due to mutual collisions and the like. Among these, fine particles are discharged out of the furnace along with the air current, and the solid content is captured by the cyclone separator 18 and collected in the powder hopper 6. After being granulated into pellets by a granulator 8 and filled into a pellet hopper 9, the pellets are filled into a drum 10. Further, the solid content is decomposed in the scrubber 19 and liquefied in the condenser 21.6 According to this embodiment, the bubbles are not entrained into the air layer and are pulverized, and the generated powder is used during granulation. without buckling,
It was possible to mold sufficient pellets in both specific gravity and strength as in the conventional method.

〈実施例3〉 実施例1,2では、ダブレット型造粒機で円應形のペレ
ットを作成したが、ブリケット型造粒機でアーモンド型
に造粒しても同様の効果が得られる。
<Example 3> In Examples 1 and 2, round-shaped pellets were produced using a doublet-type granulator, but similar effects can be obtained by granulating the pellets into an almond-shape using a briquette-type granulator.

〈実施例4〉 実施例1.2では、PWR型発電プラントから発生する
濃縮廃液の主成分であるホウ酸廃液と洗濯廃液を混合処
理したが、他の廃液(硫酸ソーダ廃液、硝酸ソーダ廃液
、樹脂)でも同様の効果が得られる。
<Example 4> In Example 1.2, boric acid waste liquid, which is the main component of concentrated waste liquid generated from a PWR power plant, and laundry waste liquid were mixed and treated, but other waste liquids (sodium sulfate waste liquid, sodium nitrate waste liquid, A similar effect can be obtained with resin).

〈実施例5〉 本実施例1,2では、塩化バリウムを添加剤として使用
したが、アルカリ土類金属と鉱酸との塩類化合物で、水
溶性のものであれば、同様の効果が得られる。添加量は
、本実験で使用した塩化バリウムと等モルでよい。
<Example 5> In Examples 1 and 2, barium chloride was used as an additive, but the same effect can be obtained if it is a water-soluble salt compound of an alkaline earth metal and a mineral acid. . The amount added may be equimolar to the barium chloride used in this experiment.

〔発明の効果〕〔Effect of the invention〕

本発明によれば、アルカリ土類金属と鉱酸との水溶性塩
類化合物を添加することにより、乾燥時の発泡を抑制で
きるので、乾燥機のpFを向上させる効果がある。
According to the present invention, by adding a water-soluble salt compound of an alkaline earth metal and a mineral acid, foaming during drying can be suppressed, so that there is an effect of improving the pF of the dryer.

また、固形分に対する洗剤の混合量を16重量%まで、
多くすることができ、減容性に優れたペレットが造粒で
きる。
In addition, the amount of detergent mixed with the solid content can be up to 16% by weight.
Pellets with excellent volume reduction properties can be granulated.

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

第1図は本発明方法を実施するための減容処理設備の構
成の一例を示すプロセスフロー、第2図は洗剤に対する
アルカリ土類金属塩の添加量(相対比)と蒸留時に蒸留
側に移行する洗剤量との関係を示す図、第3図は廃液の
全固形分中の洗剤濃度とペレット強度相対比との関係を
示す図、第4図は本発明方法を実施するための減容処理
設備の構成の他の例を示すプロセスフローである。 4・・・助剤タンク、13・・・仮焼炉、50・・・乾
燥機。
Figure 1 shows a process flow showing an example of the configuration of a volume reduction treatment facility for carrying out the method of the present invention, and Figure 2 shows the amount (relative ratio) of alkaline earth metal salt added to the detergent and the amount transferred to the distillation side during distillation. Figure 3 is a diagram showing the relationship between the detergent concentration in the total solid content of the waste liquid and the relative pellet strength ratio, and Figure 4 is the volume reduction treatment for carrying out the method of the present invention. It is a process flow which shows another example of a structure of equipment. 4... Auxiliary tank, 13... Calciner, 50... Dryer.

Claims (1)

【特許請求の範囲】 1、少なくとも洗濯液を含む放射性廃液に、アルカリ土
類金属と鉱酸との水溶性塩類化合物を添加し洗剤成分を
沈澱性塩類に変化させる工程と、前記塩類が混合されて
いる前記放射性廃液を加熱により濃縮乾燥させて粉体化
する工程と、上記生成した粉体を造粒する工程と からなる放射性洗濯廃液の処理方法。 2、特許請求の範囲第1項において、 前記放射性廃液が、 前記放射性洗濯廃液と、 他の放射性廃液であるホウ酸廃液、硫酸ソーダ廃液、硝
酸ソーダ廃液等と を混合した廃液からなることを特徴とする放射性洗濯液
の処理方法。 3、特許請求の範囲第1項または第2項において、前記
水溶性塩類化合物の添加量が、 前記放射性洗濯廃液の洗剤成分に対し、10重量%以上
であることを特徴とする放射性洗濯廃液の処理方法。 4、特許請求の範囲第1項〜第3項のいずれか一項にお
いて、 前記粉体化処理工程が、 前記水溶性塩類化合物および他の放射性廃液と混合した
放射性洗濯廃液を、回転羽根を有する回転軸を内部に備
え外周に加熱手段を有する容器に供給し、前記加熱手段
で前記容器内の前記放射性廃液を加熱しながら、前記回
転軸を回転させて前記放射性廃液を粉体化する工程から
なることを特徴とする放射性洗濯廃液の処理方法。 5、特許請求の範囲第1項〜第3項のいずれか一項にお
いて、 前記粉体化処理工程が、 前記水溶性塩類化合物および他の放射性廃液と混合した
放射性洗濯廃液を、固定粒子を加熱空気により下から浮
遊させた流動媒体層を有する仮焼炉内に供給し、前記放
射性廃液を前記流動媒体に接触させて粉体化する工程か
らなることを特徴とする放射性洗濯廃液の処理方法。
[Claims] 1. A step of adding a water-soluble salt compound of an alkaline earth metal and a mineral acid to a radioactive waste liquid containing at least a washing liquid to change detergent components into precipitable salts, and a step in which the salts are mixed. A method for treating radioactive laundry waste liquid, which comprises the steps of: concentrating and drying the radioactive waste liquid by heating and turning it into powder; and granulating the generated powder. 2. Claim 1, characterized in that the radioactive waste liquid is a waste liquid that is a mixture of the radioactive laundry waste liquid and other radioactive waste liquid such as boric acid waste liquid, sodium sulfate waste liquid, sodium nitrate waste liquid, etc. How to dispose of radioactive laundry liquid. 3. The radioactive laundry waste liquid according to claim 1 or 2, wherein the amount of the water-soluble salt compound added is 10% by weight or more based on the detergent component of the radioactive laundry waste liquid. Processing method. 4. In any one of Claims 1 to 3, the pulverization treatment step includes a rotating blade for transferring the radioactive laundry waste mixed with the water-soluble salt compound and other radioactive waste. From the step of supplying the radioactive waste liquid to a container that has a rotating shaft inside and having a heating means on the outer periphery, and rotating the rotating shaft while heating the radioactive waste liquid in the container with the heating means to powderize the radioactive waste liquid. A method for treating radioactive laundry waste liquid, which is characterized by: 5. In any one of claims 1 to 3, the pulverization treatment step comprises heating fixed particles of the radioactive laundry waste liquid mixed with the water-soluble salt compound and other radioactive waste liquid. A method for treating radioactive laundry waste liquid, comprising the steps of supplying the radioactive waste liquid into a calciner having a fluidized medium layer suspended from below by air, and bringing the radioactive waste liquid into contact with the fluidized medium to pulverize it.
JP62088343A 1987-04-10 1987-04-10 Treatment method of radioactive laundry waste liquid Expired - Lifetime JPH0677070B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP62088343A JPH0677070B2 (en) 1987-04-10 1987-04-10 Treatment method of radioactive laundry waste liquid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP62088343A JPH0677070B2 (en) 1987-04-10 1987-04-10 Treatment method of radioactive laundry waste liquid

Publications (2)

Publication Number Publication Date
JPS63253298A true JPS63253298A (en) 1988-10-20
JPH0677070B2 JPH0677070B2 (en) 1994-09-28

Family

ID=13940206

Family Applications (1)

Application Number Title Priority Date Filing Date
JP62088343A Expired - Lifetime JPH0677070B2 (en) 1987-04-10 1987-04-10 Treatment method of radioactive laundry waste liquid

Country Status (1)

Country Link
JP (1) JPH0677070B2 (en)

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS51124800A (en) * 1975-04-24 1976-10-30 Tokyo Electric Power Co Inc:The The treating method of the washing waste water containing radioactive substances
JPS54101100A (en) * 1978-01-27 1979-08-09 Hitachi Ltd Processing method of radioactive waste
JPS6050499A (en) * 1983-08-31 1985-03-20 日本碍子株式会社 Method and device for treating radioactive waste

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS51124800A (en) * 1975-04-24 1976-10-30 Tokyo Electric Power Co Inc:The The treating method of the washing waste water containing radioactive substances
JPS54101100A (en) * 1978-01-27 1979-08-09 Hitachi Ltd Processing method of radioactive waste
JPS6050499A (en) * 1983-08-31 1985-03-20 日本碍子株式会社 Method and device for treating radioactive waste

Also Published As

Publication number Publication date
JPH0677070B2 (en) 1994-09-28

Similar Documents

Publication Publication Date Title
CA1204039A (en) Process for preparing detergent compositions containing hydrated inorganic salts
US4246242A (en) Method of removing gaseous pollutants from flue gas
US5458799A (en) Mix process for formulating detergents
US3918921A (en) Process for making granular hydrated alkali metal silicate
US3782906A (en) Process for preparation of agglomerated hydrated alkali metal silicate glass particles
GB2121843A (en) Bentonite agglomerates
DE69207727D1 (en) Process for the production of salt granules
KR950700104A (en) PROCESS FOR PRODUCING GRANULATES USEFUL AS WETTING, WASHING AND / OR CLEANING AGENTS
JP6213978B2 (en) Cesium adsorbent and method for removing cesium using the same
US3783008A (en) Process for preparing coated detergent particles
US4432894A (en) Process for treatment of detergent-containing radioactive liquid wastes
JPS63253298A (en) Method of processing radioactive washing waste liquor
JPH07507718A (en) Method for producing and coating sodium carbonate perhydrate stable in detergent formulations
CA2434767C (en) Process for the preparation of urea granules
JP4194001B2 (en) Acid gas treatment agent and waste gas treatment method using the same
JPS6049124B2 (en) Method for drying aluminosilicate slurry
US5383940A (en) Process of producing solid sodium cyanide
JPS6385498A (en) Method and facility for processing radioactive waste liquor containing surface active agent
JPS62276095A (en) Recovery of caustic soda from alkali pulp waste liquid
US4613578A (en) Porous zeolite granules stable in aqueous solutions
US2815329A (en) Process for preparing humic acid beads and product
TW200415120A (en) Process for producing anhydrous alkali sulfide
WO1995033037A1 (en) Organosilicon modified, water-soluble, amorphous alkali metal silicates
JP2843047B2 (en) Hollow sphere made of sodium sulfate and method for producing the same
WO1995015370A1 (en) Granular alkali metal nitrilotriacetate