JPH0139079B2 - - Google Patents
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- Publication number
- JPH0139079B2 JPH0139079B2 JP17290583A JP17290583A JPH0139079B2 JP H0139079 B2 JPH0139079 B2 JP H0139079B2 JP 17290583 A JP17290583 A JP 17290583A JP 17290583 A JP17290583 A JP 17290583A JP H0139079 B2 JPH0139079 B2 JP H0139079B2
- Authority
- JP
- Japan
- Prior art keywords
- cleaning
- waste liquid
- drying device
- water
- conduit
- 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.)
- Expired
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 42
- 238000004140 cleaning Methods 0.000 claims description 40
- 239000007788 liquid Substances 0.000 claims description 39
- 238000001035 drying Methods 0.000 claims description 26
- 239000002699 waste material Substances 0.000 claims description 19
- 238000000034 method Methods 0.000 claims description 18
- 238000005406 washing Methods 0.000 claims description 16
- 239000002901 radioactive waste Substances 0.000 claims description 15
- 239000007787 solid Substances 0.000 claims description 15
- 239000007921 spray Substances 0.000 claims description 8
- 238000010438 heat treatment Methods 0.000 claims description 5
- 239000000463 material Substances 0.000 description 7
- 238000010586 diagram Methods 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 239000000498 cooling water Substances 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 238000007711 solidification Methods 0.000 description 2
- 230000008023 solidification Effects 0.000 description 2
- 238000001816 cooling Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 230000036449 good health Effects 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 230000035939 shock Effects 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 239000010409 thin film Substances 0.000 description 1
Landscapes
- Fertilizers (AREA)
- Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)
Description
【発明の詳細な説明】
〔発明の利用分野〕
本発明は、放射性廃液処理装置の洗浄方法に係
り、特に、原子力発電所にて発生した放射性廃液
又はスラリを蒸発乾燥させ、乾燥物を固化処理す
る放射性廃液処理装置に好適なものである。Detailed Description of the Invention [Field of Application of the Invention] The present invention relates to a method for cleaning radioactive waste liquid processing equipment, and in particular, a method for evaporating and drying radioactive waste liquid or slurry generated at a nuclear power plant and solidifying the dried product. It is suitable for radioactive waste liquid treatment equipment.
従来の放射性廃液処理装置およびその洗浄方法
例を第1図により説明する。
An example of a conventional radioactive waste liquid treatment device and its cleaning method will be explained with reference to FIG.
第1図は、放射性廃液処理装置の系統図で、廃
液供給タンク1には廃液元弁30、給液ポンプ1
0、導管50が連結され、熱媒供給用、排出用の
導管51,52が連結された加熱ジヤケツト11
が包設されるとともに電動機等の駆動装置12で
駆動される回転翼13が回転可能に内設された乾
燥装置14が設けられ、この乾燥装置14は乾燥
物出口管53を介して乾燥物ホツパ15に連結さ
れ、さらに乾燥物弁32を介してフイーダ16に
連結され、フイーダ16はフイーダ出口弁32を
介して固化処理装置17、固化物充填缶18に連
結される。一方、冷却水の供給用、排出用の導管
58,59が連結された復水器19と乾燥装置1
4は導管55で連結されている。 FIG. 1 is a system diagram of the radioactive waste liquid processing equipment, in which the waste liquid supply tank 1 includes a waste liquid source valve 30 and a liquid supply pump 1.
0, a heating jacket 11 to which a conduit 50 is connected and conduits 51 and 52 for heat medium supply and discharge are connected;
A drying device 14 is provided, in which a rotary blade 13 driven by a drive device 12 such as an electric motor is rotatably installed. 15 and further connected to a feeder 16 via a dry matter valve 32, and the feeder 16 is connected to a solidification processing device 17 and a solidified matter filling can 18 through a feeder outlet valve 32. On the other hand, a condenser 19 and a drying device 1 are connected to conduits 58 and 59 for supplying and discharging cooling water.
4 are connected by a conduit 55.
原子力発電所等にて発生した放射性廃液は廃液
供給タンク1に移送されて一時貯えられ、給液ポ
ンプ10により所定の供給容量で廃液元弁30を
介し導管50を経て乾燥装置14に供給される。
ここで放射性廃液は、駆動装置12で駆動され回
転する回転翼13の遠心力作用により乾燥装置1
4内壁面に薄膜状に押拡げられ、導管51、加熱
ジヤケツト11、導管52を流通する熱媒の加熱
により蒸発乾燥する。蒸発物は導管55を経て復
水器19に供給され、ここで導管58より供給さ
れ導管59より排出される冷却水で凝縮され、凝
縮液は凝縮液出口弁34を介し導管60より他系
統に送液される。蒸発物中の非凝縮性ガスはベン
ト出口弁35を介し導管57より他のベント処理
系へ送気される。一方、乾燥物は乾燥物出口管5
3を経て乾燥物ホツパ15に入り、乾燥物弁32
を介してフイーダ16の一端に供給され、その他
端に移送された後フイーダ出口弁33を介し導管
40を経て固化処理装置17に供給され、乾燥物
を長期保管あるいは処分に適した方法で固化処理
し導管41を経て固化物充填缶18へ充填され
る。 Radioactive waste liquid generated at a nuclear power plant or the like is transferred to a waste liquid supply tank 1 and temporarily stored therein, and is supplied to a drying device 14 via a waste liquid main valve 30 and a conduit 50 at a predetermined supply capacity by a liquid supply pump 10. .
Here, the radioactive waste liquid is transferred to the drying device 1 by the centrifugal force of the rotating blades 13 driven by the driving device 12.
4 is spread out into a thin film on the inner wall surface, and is evaporated and dried by the heating of the heating medium flowing through the conduit 51, the heating jacket 11, and the conduit 52. The evaporated matter is supplied to the condenser 19 through the conduit 55, where it is condensed with cooling water supplied through the conduit 58 and discharged through the conduit 59, and the condensate is sent to other systems via the condensate outlet valve 34 through the conduit 60. The liquid is delivered. The non-condensable gas in the evaporated material is sent through the vent outlet valve 35 and through the conduit 57 to other vent processing systems. On the other hand, the dry matter is dried through the dry matter outlet pipe 5.
3, enters the dry material hopper 15, and enters the dry material valve 32.
The dried material is supplied to one end of the feeder 16 through the feeder 16, and after being transferred to the other end, it is supplied to the solidification processing device 17 via the feeder outlet valve 33 and the conduit 40, where the dried material is solidified in a method suitable for long-term storage or disposal. The solidified material is filled into the solidified material filling can 18 through the conduit 41.
これら一連の処理を円滑に行なうためには、放
射性廃液処理装置を健全に保持しなければならな
い。つまり、放射性廃液は蒸発により残留含水率
が数重量%以下まで乾燥されるため乾燥装置の内
部に乾燥物が徐々に付着堆積し、長時間の運転後
には円滑な運転を阻害することになり、定期的に
洗浄する必要がある。 In order to carry out a series of these processes smoothly, the radioactive waste liquid processing equipment must be maintained in good health. In other words, the radioactive waste liquid is dried by evaporation until the residual water content is less than a few percent by weight, so dried matter gradually accumulates inside the drying equipment, impeding smooth operation after long periods of operation. Must be cleaned regularly.
従来の洗浄方法を説明する。まず熱媒の導管5
1への熱媒の供給を停止し、廃液元弁30から導
管50を経て乾燥装置14に至る系統内部を洗浄
するため廃液弁30を閉止し、代わりに洗浄水元
弁31を開いて導管54より洗浄水を供給し、給
液ポンプ10より導管50を介して乾燥装置14
内へ洗浄水を供給する。駆動装置12は廃液処理
中と同じように駆動することで回転翼13は回転
しており、洗浄水は廃液の場合と同様に遠心力の
作用により乾燥装置14内壁面に押拡げられ、廃
液の流通経路を洗浄する。 A conventional cleaning method will be explained. First, heat medium conduit 5
1, the waste liquid valve 30 is closed in order to clean the inside of the system from the waste liquid source valve 30 to the drying device 14 via the conduit 50, and instead, the cleaning water source valve 31 is opened and the conduit 54 is closed. The cleaning water is supplied from the liquid supply pump 10 to the drying device 14 via the conduit 50.
Supply cleaning water inside. The drive device 12 is driven in the same way as during waste liquid treatment, so the rotor blades 13 are rotating, and the washing water is spread out against the inner wall surface of the drying device 14 by the action of centrifugal force, as in the case of waste liquid, and the cleaning water is Clean distribution channels.
上記従来の洗浄方法では、廃液の給液量に対し
数倍の洗浄水量で洗浄するため廃液の流通経路は
十分に洗浄できるが、洗浄水が遠心力の作用によ
つて円筒壁部に集まるため回転翼13の中心部あ
るいは回転翼を構成する部材の隅々までの洗浄は
むずかしく、通水洗浄後に乾燥装置14の内部に
満液状態にして洗浄した場合でも尚洗浄水中の固
形分の濃度は高く、洗浄が完全に行なわれないと
いつた欠点があつた。 In the conventional cleaning method described above, the flow path of the waste liquid can be sufficiently cleaned because the amount of washing water is several times the amount of the waste liquid supplied, but the washing water collects on the cylindrical wall due to the action of centrifugal force. It is difficult to clean the center of the rotor blade 13 or every corner of the parts that make up the rotor blade, and even if the inside of the drying device 14 is filled with liquid after washing with water, the concentration of solids in the cleaning water is still low. The disadvantages were that it was expensive and that cleaning was not thorough.
本発明は上記欠点の除去を目的としたもので、
放射性廃液処理装置の乾燥装置の内部に至るまで
の洗浄を容易にし、洗浄水量を最少限度におさえ
るとともに短時間でより完全な洗浄ができる洗浄
方法をを提供することにある。
The present invention aims to eliminate the above-mentioned drawbacks.
To provide a cleaning method that facilitates cleaning up to the inside of a drying device of a radioactive waste liquid treatment device, minimizes the amount of cleaning water, and enables more complete cleaning in a short time.
本発明は、従来の洗浄方法では洗浄水が行き届
かなかつた回転翼の中央部および回転翼を構成す
る部材に対しても洗浄水が流通するようにしたも
ので、その要点は以下の通りである。
The present invention allows cleaning water to flow to the central part of the rotor blade and the members that make up the rotor blade, which could not be reached by conventional cleaning methods.The main points are as follows. be.
(1) 洗浄水の供給導管を、廃液の給液と共通の導
管50とは別個に洗浄水供給導管20およびス
プレー管21を乾燥装置14の上部へ設け、回
転翼13へ均一に洗浄水を分散させる。(1) A cleaning water supply conduit 20 and a spray pipe 21 are installed in the upper part of the drying device 14 separately from the conduit 50 that is common to the waste liquid supply, and the cleaning water is uniformly supplied to the rotary blades 13. disperse.
(2) 駆動装置12を可変速装置により構成し、廃
液処理運転中より低速での回転を可能とし、駆
動装置に対する負荷GD2(回転翼のはずみ車効
果)小さくし駆動装置の回転停止、再起動時の
負荷を低減し、短時間での再起動(ホツトスタ
ート)を容易にする。(2) The drive device 12 is configured with a variable speed device, which enables rotation at a lower speed than during waste liquid treatment operation, reduces the load GD 2 (flywheel effect of rotary blades) on the drive device, and stops and restarts rotation of the drive device. This reduces the time load and facilitates a quick restart (hot start).
尚、処理運転中の回転数をN1、低速回転数
をN2とすると、回転数N1で起動する時の駆動
装置に加わる〔GD2〕1に対し回転数N2で起動
する時の駆動装置に加わる〔GD2〕2は次式の如
く低減できた。 Furthermore, if the number of revolutions during processing operation is N 1 and the number of low-speed revolutions is N 2 , the amount applied to the drive device when starting at the number of revolutions N 1 is [GD 2 ] 1 , whereas when starting at the number of revolutions N 2 , the [GD 2 ] 2 applied to the drive device could be reduced as shown in the following equation.
〔GD2〕2=(N2/N1)2×〔GD2〕1
電動機の再起動の頻度は負荷GD2によつて決
まるので、再起動時の回転数を低速とすること
によつて負荷GD2を小くさし、再起動を容易に
することができる。 [GD 2 ] 2 = (N 2 / N 1 ) 2 × [GD 2 ] 1 The frequency of restarting the motor is determined by the load GD 2 , so by setting the rotation speed at restart to a low speed, The load GD 2 can be reduced and restarts can be made easier.
(3) 回転翼13を一旦停止させることによつて、
洗浄水を回転翼の中央部まで行きわたらせるこ
とができる。(3) By temporarily stopping the rotor 13,
Cleaning water can be distributed all the way to the center of the rotor.
本発明の一実施例を第2図により説明する。熱
媒の導管51への熱媒の供給を停止し、廃液元弁
30を閉止する。次いで洗浄水元弁31を開き、
洗浄水を乾燥装置14へ供給する。(時間T0)。
最初の洗浄水量は、廃液の供給量とほぼ同じとす
るのが乾燥装置14の急冷による熱衝撃を防ぐた
めから望ましい。時間T1にて洗浄水量を増加さ
せる。洗浄水量としては廃液供給量の3〜5倍程
度が良好であり、少な過ぎると洗浄効果が悪く、
反対に多すぎると駆動装置12に対する負荷が増
大するので好ましくない。時間T2で回転数を下
げ、時間T3にて一旦停止する。次いで、乾燥装
置14上部に設けた洗浄水供給導管20およびス
プレー管21より洗浄水をスプレーする。これに
よつて、回転翼13の回転中には洗浄水が流通し
なかつた部分にまで洗浄水を行きわたらせること
ができる。スプレー水量としては、廃液供給量の
10〜20倍程度の大量の洗浄水を短時間に噴霧する
のが良好である。
An embodiment of the present invention will be described with reference to FIG. The supply of the heat medium to the heat medium conduit 51 is stopped, and the waste liquid main valve 30 is closed. Next, open the washing water source valve 31,
Washing water is supplied to the drying device 14. (time T 0 ).
It is desirable that the initial amount of washing water be approximately the same as the amount of waste liquid supplied in order to prevent thermal shock caused by rapid cooling of the drying device 14. The amount of washing water is increased at time T1 . The amount of cleaning water should be about 3 to 5 times the amount of waste liquid supplied, and if it is too small, the cleaning effect will be poor.
On the other hand, if it is too large, the load on the drive device 12 will increase, which is not preferable. The rotation speed is lowered at time T 2 and stopped once at time T 3 . Next, cleaning water is sprayed from the cleaning water supply conduit 20 and the spray pipe 21 provided at the top of the drying device 14. Thereby, the cleaning water can be distributed even to the parts where the cleaning water did not flow while the rotary blade 13 is rotating. The amount of spray water depends on the amount of waste liquid supplied.
It is best to spray a 10 to 20 times larger amount of cleaning water in a short period of time.
次いで、時間T4においてスプレー水を停止し
駆動装置12を再起動し、時間T5にて回転数を
廃液処理運転時と同じ回転数とする。これは、廃
液処理中に固着した固形物を完全に洗浄するため
には、低速より高速の方がより効果的であるため
である。時間T6において再び低速回転とし、時
間T7において洗浄水の供給を停止し、回転翼に
付着している水分を振り切つた後に時間T5で停
止する。本発明の一実施例である第2図と比較を
容易にするため、従来例を第3図に示した。 Next, at time T4 , the spray water is stopped and the drive device 12 is restarted, and at time T5 , the rotational speed is set to the same rotational speed as during the waste liquid treatment operation. This is because a high speed is more effective than a low speed in order to completely clean solid matter stuck during waste liquid treatment. At time T6 , the rotor rotates at a low speed again, at time T7 , the supply of cleaning water is stopped, and after shaking off the water adhering to the rotor blade, it is stopped at time T5 . In order to facilitate comparison with FIG. 2, which is an embodiment of the present invention, a conventional example is shown in FIG. 3.
本発明の効果を明確にするために、本発明の一
実施例である第2図の洗浄方法と従来例である第
3図の洗浄方法に対する各時間毎の洗浄水中に含
有される固形分濃度すなわち洗浄された固形分量
の測定結果を第4図に示す。第4図中〇印及び実
線は本発明の実施例で、△印及び破線は従来例で
ある。従来例においては、時間の経過とともに洗
浄水中の固形分濃度は低下しており、時間T7ま
で固形分濃度の低下はつづく。その後、乾燥装置
14内の残存固形分量を計測するために乾燥装置
14内を満水状態にし、乾燥装置14の隅々に至
るまで付着した固形分量を溶解洗浄させた後の満
水洗浄水中の固形分濃度を時間T10に示す。一
方、本発明実施例については、時間T3までは従
来例と同じであるが、時間T4で再び固形分濃度
は上昇している。すなわち、時間T3からT4まで
回転を停止したために、付着した固形分がよく洗
浄されていることを示している。このことは、時
間T10満液洗浄後の固形分濃度が低くなつている
ことからも判る。 In order to clarify the effects of the present invention, the solid content concentration contained in the cleaning water at each hour for the cleaning method shown in FIG. 2, which is an embodiment of the present invention, and the cleaning method shown in FIG. 3, which is a conventional example. That is, FIG. 4 shows the measurement results of the amount of washed solids. In FIG. 4, the ◯ mark and the solid line are the embodiment of the present invention, and the △ mark and the broken line are the conventional example. In the conventional example, the solid content concentration in the wash water decreases with the passage of time, and the decrease in solid content concentration continues until time T7 . After that, in order to measure the amount of solids remaining in the drying device 14, the inside of the drying device 14 is filled with water, and the amount of solids that have adhered to every corner of the drying device 14 is dissolved and washed, and the solid content in the full-water washing water is The concentration is shown at time T10 . On the other hand, the example of the present invention is the same as the conventional example up to time T3 , but the solid content concentration increases again at time T4 . That is, since the rotation was stopped from time T 3 to T 4 , it is shown that the attached solids are well washed away. This can also be seen from the fact that the solid content concentration after time T 10 full liquid washing became lower.
本発明は以上説明したように、放射性廃液処理
装置の洗浄水を乾燥装置の上部に設けたスプレー
ノズルから供給し、かつ回転翼に回転及び停止を
行なわせることにより、乾燥装置内に付着した固
形分を十分に洗浄除去できる効果がある。
As explained above, the present invention supplies cleaning water for the radioactive waste liquid treatment equipment from the spray nozzle installed at the top of the drying equipment, and causes the rotary blades to rotate and stop, thereby eliminating the solid matter that has adhered inside the drying equipment. It has the effect of sufficiently cleaning and removing the components.
第1図は放射性廃液処理装置の系統図、第2図
は本発明の洗浄方法の一実施例を説明する状態
図、第3図は従来の洗浄方法を説明する状態図、
第4図は本発明の一実施例と従来の洗浄方法を比
較する洗浄水中の固形分濃度のデータを示す線図
である。
12……駆動装置、13……回転翼、14……
乾燥装置、16……フイーダ、19……復水器、
20……洗浄水供給導管、21……スプレー管。
FIG. 1 is a system diagram of a radioactive waste liquid treatment device, FIG. 2 is a state diagram explaining an embodiment of the cleaning method of the present invention, and FIG. 3 is a state diagram explaining a conventional cleaning method.
FIG. 4 is a diagram showing data on solid content concentration in washing water comparing an embodiment of the present invention with a conventional washing method. 12... Drive device, 13... Rotor blade, 14...
Drying device, 16... feeder, 19... condenser,
20...Washing water supply conduit, 21...Spray pipe.
Claims (1)
流通する加熱ジヤケツトが包設された放射性廃液
を乾燥する乾燥装置の内部に付着する放射性廃液
の固形分洗浄方法において、放射性廃液の給液導
管から供給する廃液と洗浄水を切替えて乾燥装置
内に洗浄水を供給するとともに、乾燥装置の上部
に設けたスプレーノズルから洗浄水を供給し、か
つ、乾燥装置の回転翼の回転数を可変に制御する
とともに、洗浄水供給中に一旦停止させ、さらに
回転させるようにしたことを特徴とする放射性廃
液処理装置の洗浄方法。1. In a method for cleaning solid content of radioactive waste adhering to the inside of a drying device for drying radioactive waste in which a rotor is rotatably installed and a heating jacket through which a heat medium flows is enclosed, In addition to supplying washing water into the drying device by switching between waste liquid and washing water supplied from the liquid conduit, washing water is supplied from the spray nozzle installed at the top of the drying device, and the rotation speed of the rotary blades of the drying device is controlled. A method for cleaning a radioactive waste liquid processing equipment, characterized in that the cleaning method is variably controlled, the cleaning water is temporarily stopped during the supply of cleaning water, and the cleaning method is further rotated.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP17290583A JPS6066200A (en) | 1983-09-21 | 1983-09-21 | Method of washing radioactive waste liquor treater |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP17290583A JPS6066200A (en) | 1983-09-21 | 1983-09-21 | Method of washing radioactive waste liquor treater |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6066200A JPS6066200A (en) | 1985-04-16 |
| JPH0139079B2 true JPH0139079B2 (en) | 1989-08-17 |
Family
ID=15950513
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP17290583A Granted JPS6066200A (en) | 1983-09-21 | 1983-09-21 | Method of washing radioactive waste liquor treater |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6066200A (en) |
-
1983
- 1983-09-21 JP JP17290583A patent/JPS6066200A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6066200A (en) | 1985-04-16 |
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