JPS60178397A - Method of treating radioactive waste liquor - Google Patents

Method of treating radioactive waste liquor

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Publication number
JPS60178397A
JPS60178397A JP3360884A JP3360884A JPS60178397A JP S60178397 A JPS60178397 A JP S60178397A JP 3360884 A JP3360884 A JP 3360884A JP 3360884 A JP3360884 A JP 3360884A JP S60178397 A JPS60178397 A JP S60178397A
Authority
JP
Japan
Prior art keywords
waste liquid
waste
dryer
radioactive
cleaning
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
JP3360884A
Other languages
Japanese (ja)
Inventor
尚実 豊原
戸村 寿
健 松田
坂本 清次
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
Nippon Genshiryoku Jigyo KK
Nippon Atomic Industry Group Co Ltd
Original Assignee
Toshiba Corp
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, Nippon Genshiryoku Jigyo KK, Nippon Atomic Industry Group Co Ltd filed Critical Toshiba Corp
Priority to JP3360884A priority Critical patent/JPS60178397A/en
Publication of JPS60178397A publication Critical patent/JPS60178397A/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] 本発明は沸騰水形原子力発電所等の放射性物質取扱い施
設においで発生する放射性廃液を処理(る方法に係り、
特に芒硝等の析出性物質を含む放q4性廃液を乾燥処理
する放射性廃液の処理方法に関りる。
[Detailed Description of the Invention] [Technical Field of the Invention] The present invention relates to a method for treating radioactive waste liquid generated in facilities handling radioactive materials such as boiling water nuclear power plants.
In particular, the present invention relates to a method for treating radioactive waste liquid, which involves drying radioactive waste liquid containing precipitable substances such as Glauber's salt.

[発明の技術的背景とその問題点] 一般に、原子力発電所等の放射性物質取扱い施設におい
ては、放射性廃液処理系その他に大量のイオン交換樹脂
が使用されており、これらのイオン交換樹脂は定期的に
硫酸および水酸化す[・リウムC洗浄して再生する必要
がある。
[Technical background of the invention and its problems] In general, in facilities that handle radioactive materials such as nuclear power plants, large amounts of ion exchange resins are used in radioactive waste liquid treatment systems and other areas, and these ion exchange resins are periodically It is necessary to regenerate by cleaning with sulfuric acid and hydroxide.

このJ、うな樹脂の再生に用いられた@酸および水酸化
ナトリウムは、混合されて芒硝を含む廃液どなり、この
廃液中にはイオン交換されたイオン状の放射性物質や樹
脂表面に付着していたクラッドど叶ばれる放射性の金属
酸化物等が含まれている。
The @acid and sodium hydroxide used to regenerate Eel resin were mixed into a waste liquid containing mirabilite, and this waste liquid contained ion-exchanged ionic radioactive substances and adhering to the resin surface. The cladding contains radioactive metal oxides, etc.

そのlこめ、このようなtIl躬性廃液は、蒸発濃縮器
にJこり濃縮された後、乾燥機例えば竪型薄膜乾燥機に
送られ、ここで乾燥されて乾燥機の内壁に芒硝を主成分
とする固化体として析出され、この固化体が機械的に掻
取られて粒径1〜50μmに粉体化された後、プラスナ
ック同化装置等に送られて同化処理される。
After that, such a turbulent waste liquid is concentrated in an evaporative concentrator and then sent to a dryer, for example, a vertical thin film dryer, where it is dried and coated on the inner wall of the dryer with mirabilite as the main component. This solidified material is mechanically scraped and pulverized to a particle size of 1 to 50 μm, and then sent to a Plasnac assimilation device or the like for assimilation treatment.

しかしながら、このような方法にa3いては、乾燥機の
内壁に析出づる固化体は、芒硝の他にクラッドの主成分
とされるFe (ON>3やCa 、 Si等を含むた
め極めて硬り、一部は壁面に析出したまま残存し、それ
が乾燥機に過大な負荷をか(〕ることになる、。
However, in this method, the solidified material deposited on the inner wall of the dryer is extremely hard because it contains Fe (ON>3, Ca, Si, etc., which are the main components of the cladding, in addition to Glauber's salt). Some of it remains deposited on the wall, putting an excessive load on the dryer.

そのため、通常乾燥機は一定の廃液処理の後、温水等に
よる洗浄を行なって残存しくいる析出体を除去し、再び
廃液処理をt′jなうという処理、洗浄をリサイクルづ
る運転]゛稈がとられている。
Therefore, after a certain amount of waste liquid treatment, dryers are usually washed with warm water to remove any remaining precipitates, and then the waste liquid is treated again. It is taken.

このように廃液処理の連続運転が不可能なことは、廃液
処理効率の低下を意味するとともに、洗浄に伴う大量の
放射性洗浄廃液の増加に繋がる。
The impossibility of continuous operation of waste liquid treatment in this way means a decrease in waste liquid treatment efficiency, and also leads to an increase in a large amount of radioactive cleaning waste liquid accompanying cleaning.

ずなわら、この洗浄廃液は二次廃棄物として再び廃液処
理系に送られる。
However, this washing waste liquid is sent back to the waste liquid treatment system as secondary waste.

しかも、従来の温水洗浄法では、乾燥機57面の析出固
化体を完全に除去することができず、洗浄後に残存した
析出固化体はいっそう硬化けるどともに次の廃液処理工
程における析出固化体の残存率を高めることになる。こ
の対策として、「wi4水洗浄法」が考えられているが
、乾燥機構造が複雑になり、また洗浄廃液が増加する等
の欠点がある。
Moreover, with the conventional hot water washing method, it is not possible to completely remove the precipitated solids on the surface of the dryer 57, and the precipitated solids that remain after washing are further hardened, and the precipitated solids are removed in the next waste liquid treatment process. This will increase the survival rate. As a countermeasure to this problem, the "wi4 water washing method" has been considered, but it has drawbacks such as a complicated dryer structure and an increase in washing waste liquid.

−jj、このような乾燥機は、上述の芒硝を含む敢0・
1竹廃液の他に、廃樹脂や廃スラツジを含む廃液の乾燥
処理を11なうことができるように構成されている。そ
しにの場合には、乾燥機の壁面に廃樹脂等が激しく衝突
しつつ乾燥されるだけで表面に固化体が析出づることは
ない。
-jj, such a dryer is suitable for drying dryers containing mirabilite mentioned above.
In addition to bamboo waste liquid, the drying process can also be carried out for waste liquid including waste resin and waste sludge. In the case of drying, the waste resin etc. is simply dried while violently colliding with the wall of the dryer, and no solidified material is deposited on the surface.

1梵明の目的] 本弁明はこのような従来の事情に対処してなされ!ζも
のC1廃液処理後の洗浄工程を省略して長!に’i間の
連続廃液処理を可能とし、かつ洗浄廃液の発生を減少さ
せた放射性廃液の処理方法を提供しJ:うとりるもので
ある。
1. Purpose of Brahma] This defense is made in response to these conventional circumstances! ζ Mono C1 Save time by omitting the cleaning process after waste liquid treatment! The present invention provides a method for treating radioactive waste liquid that enables continuous waste liquid treatment between 1 and 2 and reduces the generation of cleaning waste liquid.

「光用の概要] づなわち本発明の放射性廃液の処理方法は、乾燥機にJ
、り放射性廃液を乾燥処理するにあたり、前記乾燥機に
析出性物質を含むfi耐性廃液を供給しこれを乾燥覆る
第1の工程と、非析出性粒子物質を含む液体を供給しこ
れを乾燥する第2の1゛稈を交互に繰り返し行なうこと
を特徴としている。
"Overview of light use" In other words, the method for treating radioactive waste liquid of the present invention is to
In drying the radioactive waste liquid, a first step is to supply the fi-resistant waste liquid containing a precipitable substance to the dryer and dry and cover it, and to supply a liquid containing a non-precipitable particulate substance and dry it. It is characterized by repeating the second 1' culm alternately.

[発明の実施例] 以下本発明の詳細を図面に示覆−実施例について説明す
る。
[Embodiments of the Invention] The details of the present invention will be described below with reference to the drawings and embodiments.

第1図は本発明方法を実施す゛るにあたり使用される竪
型薄膜乾燥機を備えた乾燥処理装置である。
FIG. 1 shows a drying apparatus equipped with a vertical thin film dryer used in carrying out the method of the present invention.

第1図において、符号1は容器本体2と、この容器本体
2の内部に挿通され上端が容器本体2上方のプーリー3
に固着され可動翼4を有するシレフト5と、容器本体2
を囲繞して形成され内部に高熱の蒸気が循環されている
加熱ダクト6とから構成される竪型薄膜乾燥機を示して
いる。
In FIG. 1, reference numeral 1 denotes a container body 2 and a pulley 3 that is inserted into the container body 2 and whose upper end is above the container body 2.
a shaft 5 having a movable wing 4 fixed to the container body 2;
This figure shows a vertical thin film dryer comprising a heating duct 6 that surrounds a heating duct 6 and in which high-temperature steam is circulated.

この竪型薄膜乾燥機1底部出口側には、竪型薄膜乾燥機
1にJ二り乾燥された放射性粉体を移送する粉体輸送器
、例えば粉体フィーダ7が配設されている。この粉体フ
ィーダ7には、同化装置測用ロア1と洗浄廃液を貯蔵す
る洗浄廃液タンク8への出ロア2が開口している。
A powder transport device, for example, a powder feeder 7, for transporting the radioactive powder dried to the vertical thin film dryer 1 is disposed on the bottom exit side of the vertical thin film dryer 1. The powder feeder 7 has an assimilation device measuring lower 1 and an outlet lower 2 opening to a cleaning waste liquid tank 8 that stores cleaning waste liquid.

また、竪型薄膜乾燥機1の側壁」一方には、芒硝を含む
放射性廃液の濃縮廃液が貯蔵された濃縮廃液貯蔵タンク
9および廃樹脂または廃スラツジ貯蔵タンク10から、
濃縮廃液移送ポンプP1および廃樹脂または廃スラツジ
移送ポンプP2により移送されて廃液供給タンク11に
貯蔵された濃縮廃液J3よび廃樹脂または廃スラツジを
、廃液供給ポンプ1ツ3により竪型薄膜乾燥I11の容
器本体2へ供給りる配管12が接続されている。
In addition, on one side of the vertical thin film dryer 1, from a concentrated waste liquid storage tank 9 in which concentrated radioactive waste liquid containing mirabilite is stored and a waste resin or waste sludge storage tank 10,
The concentrated waste liquid J3 and waste resin or waste sludge transferred by the concentrated waste liquid transfer pump P1 and waste resin or waste sludge transfer pump P2 and stored in the waste liquid supply tank 11 are transferred to the vertical thin film dryer I11 by one waste liquid supply pump 3. A pipe 12 that supplies the container body 2 is connected.

さらに、竪型薄膜乾燥機1の側壁上方には、容器本体2
で蒸発した成分を復水器13へ導く配管14が接続され
ている。この蒸発成分は復水器13によって凝結され、
再び放射性廃液として高電導瓜廃液系へ移送される。ま
た、この竪型薄膜乾燥機1には洗浄ノズル15から容器
本体2に洗浄用温水を放出づる洗浄装置16が配設され
ている。
Further, above the side wall of the vertical thin film dryer 1, a container body 2 is provided.
A pipe 14 is connected to the condenser 13 for guiding the components evaporated in the condenser 13 to the condenser 13. This evaporated component is condensed by the condenser 13,
It is transferred again to the high-conductivity melon waste liquid system as radioactive waste liquid. Further, this vertical thin film dryer 1 is provided with a cleaning device 16 that discharges hot water for cleaning from a cleaning nozzle 15 into the container body 2.

このJ、うに構成された乾燥処理装置を使用して本発明
では、まず芒硝を含む放射性廃液の濃縮廃液が廃液供給
タンク11から廃液供給ポンプP3により竪型薄膜乾燥
機1に供給され詐燥処理される。
In the present invention, using the drying treatment apparatus configured as shown in FIG. be done.

すなわち、11i!縮廃dはモータMにより回転してい
る可動*/Iの遠心力を受けて容器本体2内壁に付着し
薄く膜を作る。この膜は加熱ダクト6からの熱で乾燥さ
れながら流下し、容器本体2低部壁面で・芒硝を主成分
とづる固化体として析出覆る。
That is, 11i! The waste d adheres to the inner wall of the container body 2 under the centrifugal force of the movable */I rotated by the motor M, forming a thin film. This film flows down while being dried by the heat from the heating duct 6, and precipitates and covers the lower wall surface of the container body 2 as a solidified substance mainly composed of mirabilite.

この固化体は、−での大部分が可動翼4によって掻取ら
れ粒径1〜50μmk:粉体化されて落下し、粉体フィ
ーダ7により同化装置へ送られる。また、その一部、σ
なわち容器本体2壁面ど可動翼4の隙間に存在づる固化
体はそのまま残ることになる。
Most of this solidified material is scraped off by the movable blade 4 and falls into powder with a particle size of 1 to 50 .mu.mk, and is sent to the assimilation device by the powder feeder 7. Also, part of it, σ
In other words, the solidified material existing in the gap between the movable blades 4 and the wall surface of the container body 2 remains as is.

ここで従来の方法では、壁面に残存りる固化体を除去す
るために洗浄が行なわれるが、本発明方法においては竪
型薄膜乾燥111に廃樹脂または廃スラツジを含むfi
射性廃液が供給されて乾燥処理が行なわれる。
Here, in the conventional method, cleaning is performed to remove the solidified material remaining on the wall surface, but in the method of the present invention, the vertical thin film dryer 111 is filled with filaments containing waste resin or waste sludge.
The radioactive waste liquid is supplied and a drying process is performed.

覆なわち、高速回転する可動翼4の遠心力により容器本
体2の壁面に激しく衝突し、また可動翼4と容器本体2
間に挾まれ押し潰されながら乾燥粉体化されつつ落下づ
る。この間壁面に残存してい1=芒硝を主成分とりる固
化体を掻落していく。
In other words, the centrifugal force of the movable blades 4 rotating at high speed violently collides with the wall surface of the container body 2, and the movable blades 4 and the container body 2 collide violently.
It falls between them, being crushed and dried into a powder. During this time, the solidified material remaining on the wall and containing 1 = mirabilite as a main component is scraped off.

また、これらの廃樹脂または廃スラツジを含む廃液には
、芒硝性の析出性物質がほとんど含まれていないため、
新たに容器本体2の壁面に固化体が析出りることG;L
 /、、:い。そのため、ぎ硝を含む放射性廃液のよう
な、可動翼4の摩耗やモータ負荷の1+Rは起こらない
、。
In addition, the waste liquid containing these waste resins or waste sludge contains almost no mirabilite precipitable substances, so
New precipitation of solidified material on the wall surface of the container body 2G;L
/,,:stomach. Therefore, the wear of the movable blade 4 and the motor load of 1+R do not occur, as occurs with radioactive waste liquid containing salt.

第2図は竪型薄膜乾燥′a1の壁面に析出する芒硝を主
成分とづる析出性物質の廃液中における濃1.1変化に
対づるモータMの消Fi電力の変化を示4クラノe、析
出性物質濃度が5wt%以上になるど消費電力舶が急上
がし、P−タN4の負荷が増大りることがわかる。
Figure 2 shows the change in the Fi power consumed by the motor M in response to a 1.1 change in the concentration of the precipitable substance mainly composed of mirabilite precipitated on the wall of the vertical thin film dryer 'a1. It can be seen that as the precipitable substance concentration increases to 5 wt% or more, the power consumption of the vessel increases rapidly, and the load on the P-ta N4 increases.

従−)C1本発明にJ5【プる廃樹脂および/′または
廃スラツジを含む廃液は、芒硝(b水酸化カルシウム等
の析出性物質をたとえ含イj L/ ”uいに場合Cも
5wt%未満であることが望ましい。
According to the present invention, the waste liquid containing waste resin and /' or waste sludge may contain precipitable substances such as calcium hydroxide. It is desirable that it is less than %.

なJj第2図の測定値は、竪型薄膜乾燥機の伝熱面積は
0.5+n’であり、モータMの消費電ノコ値は乾t9
.機の運転が定常に達したどきの値である。
The measured values in Figure 2 are that the heat transfer area of the vertical thin film dryer is 0.5 + n', and the power consumption value of the motor M is t9
.. This is the value when the machine operation reaches steady state.

また本発明においては、廃液中の廃樹脂または廃スラツ
ジ等の非析出性粒子物質の好適m度は20 W 1%以
下である。
Further, in the present invention, the preferred m degree of non-precipitable particulate matter such as waste resin or waste sludge in the waste liquid is 20 W 1% or less.

このように1記実施例においては、従来渇水洗浄法等に
より溶解していた残存固化体を、廃樹脂または廃スラツ
ジを含む廃液を供給づることにより、これらの乾燥処理
と同時に固化体を除去させるため、洗浄■稈を加すこと
なく次の芒硝を含む廃液処理を行なうことができる。
In this way, in Example 1, the remaining solidified matter that was previously dissolved by the dry water cleaning method, etc., is removed at the same time as the drying process by supplying waste liquid containing waste resin or waste sludge. Therefore, the next treatment of waste liquid containing Glauber's salt can be carried out without adding washed culms.

第3図は、第1の芒硝を含む廃液処理後に、本発明の廃
樹脂または廃スラツジを含む廃液を供給した場合ど、従
来の渇水洗浄した場合の、その模の第2の芒硝を含む廃
液処理におりる芒硝i11度に対するモーター消費電力
が定常状態になるまでの時間を比較したものであり、本
発明の廃樹脂または廃スラツジを含む廃液処理が渇水洗
浄と変らない効果を持っていることを示している。なお
、第3図において、横軸には芒硝濃度が縦軸には時間が
とられており、・は渇水洗浄の場合をΔは実施例の場合
を示している。また、この実験においても竪型他膜乾m
機の伝熱面積は、第2図の実験と同じ<0.5TI+2
である。
FIG. 3 shows a second waste solution containing Glauber's salt that is similar to that obtained when the waste solution containing the waste resin or waste sludge of the present invention is supplied after the first waste solution containing Glauber's salt is subjected to conventional drought cleaning. This is a comparison of the time it takes for the motor power consumption to reach a steady state when the mirabilite temperature is 11 degrees during treatment, and it shows that the waste liquid treatment containing waste resin or waste sludge of the present invention has the same effect as drought cleaning. It shows. In FIG. 3, the horizontal axis shows the concentration of mirabilite, and the vertical axis shows time, where . is the case of drought cleaning and Δ is the case of the example. In addition, in this experiment, a vertical type other film dryer was also used.
The heat transfer area of the machine is <0.5TI+2, which is the same as the experiment in Figure 2.
It is.

以上は竪型薄膜乾燥機を連続稼動さける場合の本発明方
法について述べたが、本発明においCは乾燥機の運転を
停止−する場合には、芒硝を含む放射性廃液を処理した
後、最終的に廃樹脂または廃スラツジを含むillll
痴性廃液給し、しかる後、洗浄装昆16の洗浄ノズル1
5から温水を放出しC竪型1す薄膜乾燥機1の内部を洗
浄し、次いで空運転に二、J:り竪型@膜乾燥機1内の
乾燥を行なって停止さUる。このように洗浄工程前に析
出性物質を含まない廃樹脂または廃スラツジを含む廃液
を供給し乾燥機1を稼動させることで、残存していた析
出固化体がほぼ完全に除去されるため、洗浄に競りる渇
水は少ff1T−よい。
The above has described the method of the present invention in which continuous operation of the vertical thin film dryer is avoided. However, in the present invention, when the operation of the dryer is stopped, after treating the radioactive waste liquid containing mirabilite, containing waste resin or waste sludge
After supplying the waste liquid, the cleaning nozzle 1 of the cleaning unit 16
Hot water is discharged from 5 to clean the inside of the C vertical thin film dryer 1, and then the inside of the C vertical thin film dryer 1 is dried and then stopped. In this way, by supplying waste liquid containing waste resin or waste sludge that does not contain precipitable substances and operating the dryer 1 before the cleaning process, the remaining precipitated solidified material is almost completely removed, so that the cleaning process is easy. The drought that is going on is a little ff1T-good.

なJ3以、tの実施例では、乾燥機に竪型m膜乾燥機を
用いた例を示したが、芒硝のような析出性物質を含む廃
液を加熱蒸発により加熱乾燥させ、蒸発面に析出した固
化体を機械的に掻取り粉体化する賛同Cあれば、いかな
る乾燥機にも適用でき、例えば溝形および円筒攪拌乾燥
機、ドラムおよび円筒乾燥機等がある。
In the examples from J3 to t, an example was shown in which a vertical m-membrane dryer was used as the dryer. Any dryer capable of mechanically scraping and pulverizing the solidified material can be applied, such as groove type and cylindrical stirring dryers, drum and cylindrical dryers, etc.

また本発明の非析出性粒子物質を含む液体としては、上
記実施例に示した廃樹脂または廃スラツジを含む放射性
廃液が廃′a処理を兼ねるうえで好適づるが、その他ガ
ラス状の粒体、セラミック粉体等を含む液体を使用づる
こともできる。
In addition, as the liquid containing non-precipitating particulate matter of the present invention, the radioactive waste liquid containing the waste resin or waste sludge shown in the above examples is suitable as it also serves as waste 'a treatment, but other liquids such as glass-like particles, It is also possible to use a liquid containing ceramic powder or the like.

[発明の効果1 以上説明しICように本発明によれば、廃液処理の都度
行なっていた洗浄を不要とし、かつ従来のように洗浄の
不十分さからくる乾燥機の負荷の増大がないので、長時
間にわたる連続廃液処理が可能となり、しかも洗浄廃液
等の二次廃棄物の発/1を著しく減少させることができ
る。
[Effect of the invention 1 As explained above, according to the present invention, there is no need for cleaning that was performed every time waste liquid treatment is performed, and there is no increase in the load on the dryer due to insufficient cleaning as in the past. This makes it possible to carry out continuous waste liquid treatment over a long period of time, and to significantly reduce the generation rate of secondary waste such as cleaning waste liquid.

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

第1図は本発明方法が適用される乾燥処理装置の配管系
統図、第2図は廃液中の析出性物質濃度に対する乾燥機
の負荷の変化を示すグラフ、第3図は本発明方法による
洗浄効果(析出固化休除去効果)を示づグラフである。 1・・・・・・・・・・・・竪型薄膜乾燥機2・・・・
・・・・・・・・容器本体 3・・・・・・・・・・・・プーリー 4・・・・・・・・・・・・可動翼 5j・・・・・・・・・・・・シVフト6・・・・・・
・・・・・・加熱ダクト7・・・・・・・・・・・・粉
体フィーダ9・・・・・・・・・・・・濃縮廃液貯蔵タ
ンク10・・・・・・・・・・・・廃樹脂または廃スラ
ツジ貯蔵タンク + 1・・・・・・・・・・・・廃液供給タンク′12
.14・・・配 管 13・・・・・・・・・・・・復水器 1)+・・・・・・・・・・・・濃縮廃液移送ポンプ1
〕2・・・・・・・・・・・・廃樹脂または廃スラツジ
移送ポンプ ]〕3・・・・・・・・・・・・廃液供給ポンプM・・
・・・・・・・・・・・・・モータ代理人弁理士 須 
山 佐 − 第1図 第2図 〇 五硝遭嵐 第1頁の続き 0発 明 者 坂 本 清 次 東京都千代田区内幸町
1東京事務所内 の1の6 東京芝浦電気株式会社
Figure 1 is a piping system diagram of the drying equipment to which the method of the present invention is applied, Figure 2 is a graph showing changes in the load on the dryer with respect to the concentration of precipitable substances in the waste liquid, and Figure 3 is the cleaning method according to the present invention. It is a graph showing the effect (precipitation solidification removal effect). 1... Vertical thin film dryer 2...
......Container body 3...Pulley 4...Movable wing 5j...・・Shift 6・・・・・
...... Heating duct 7 ...... Powder feeder 9 ...... Concentrated waste liquid storage tank 10 ...... ...Waste resin or waste sludge storage tank + 1 ...Waste liquid supply tank '12
.. 14... Piping 13... Condenser 1) +... Concentrated waste liquid transfer pump 1
〕2・・・・・・・・・Waste resin or waste sludge transfer pump】〕3・・・・・・・・・・・・Waste liquid supply pump M...
・・・・・・・・・・・・・Motor's Patent Attorney Su
Yamasa - Figure 1 Figure 2 〇 Gosoku Storm Page 1 continued 0 Inventor Kiyoji Sakamoto 1-6 Tokyo Office, 1 Uchisaiwai-cho, Chiyoda-ku, Tokyo Tokyo Shibaura Electric Co., Ltd.

Claims (3)

【特許請求の範囲】[Claims] (1)乾燥機によりtIi剣士1廃液を乾燥処理りるに
あたり、前記乾燥機に析出性物質を含む放射性廃液を供
給しこれを乾燥する第1の工程ど、非析出性粒子物質を
含む液体を供給しこれを乾燥する第2の]二程を交互に
繰り返し行なうごどを特徴と覆る放射性廃液の処理方法
(1) When drying the tIi Swordsman 1 waste liquid using a dryer, the first step of supplying the radioactive waste liquid containing precipitable substances to the dryer and drying it, removes the liquid containing non-precipitable particulate substances. A method for treating radioactive waste liquid characterized by alternately repeating two steps of supplying and drying the same.
(2)乾燥機運転停止J一時においては第2の1稈の後
、洗浄処理を行なう4とを特徴とする特許請求の範囲第
1項記載の放射性廃液の処理方法。
(2) The method for treating radioactive waste liquid according to claim 1, characterized in that (4) when the dryer operation is temporarily stopped, a cleaning treatment is performed after the second culm.
(3)非析出性粒子物質を含む液体は廃樹脂j3よび/
または廃スラツジを含む放射Ti廃液である特許請求の
範囲第1項または第2項記載の放射性廃液の処理方法。
(3) Liquid containing non-precipitable particulate matter is waste resin j3 and/or
The method for treating a radioactive waste liquid according to claim 1 or 2, which is a radioactive Ti waste liquid containing waste sludge.
JP3360884A 1984-02-24 1984-02-24 Method of treating radioactive waste liquor Pending JPS60178397A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3360884A JPS60178397A (en) 1984-02-24 1984-02-24 Method of treating radioactive waste liquor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3360884A JPS60178397A (en) 1984-02-24 1984-02-24 Method of treating radioactive waste liquor

Publications (1)

Publication Number Publication Date
JPS60178397A true JPS60178397A (en) 1985-09-12

Family

ID=12391174

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3360884A Pending JPS60178397A (en) 1984-02-24 1984-02-24 Method of treating radioactive waste liquor

Country Status (1)

Country Link
JP (1) JPS60178397A (en)

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