JPS5925633B2 - How to treat wastewater - Google Patents

How to treat wastewater

Info

Publication number
JPS5925633B2
JPS5925633B2 JP11559578A JP11559578A JPS5925633B2 JP S5925633 B2 JPS5925633 B2 JP S5925633B2 JP 11559578 A JP11559578 A JP 11559578A JP 11559578 A JP11559578 A JP 11559578A JP S5925633 B2 JPS5925633 B2 JP S5925633B2
Authority
JP
Japan
Prior art keywords
water
tank
reverse osmosis
wastewater
osmosis treatment
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
Application number
JP11559578A
Other languages
Japanese (ja)
Other versions
JPS5584586A (en
Inventor
裕 伊藤
曠也 松本
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries 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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP11559578A priority Critical patent/JPS5925633B2/en
Publication of JPS5584586A publication Critical patent/JPS5584586A/en
Publication of JPS5925633B2 publication Critical patent/JPS5925633B2/en
Expired legal-status Critical Current

Links

Description

【発明の詳細な説明】 本発明は、排水を逆浸透処理装置を用(・て効率良く濃
縮処理する方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for efficiently concentrating wastewater using a reverse osmosis treatment device.

原子カプラントから排出される洗濯、手洗℃・およびシ
ャワー排水などの洗浄排水の処理につし・ては、蒸発法
、チャコールペット法、逆浸透処理法などが考えられる
が、この中で逆浸透処理法は、■ 常温で処理が行なわ
れるために腐食などの心配がなし・。
Possible methods for treating washing wastewater such as washing, hand washing, and shower wastewater discharged from the atomic couplant include the evaporation method, charcoal pet method, and reverse osmosis treatment, among which reverse osmosis treatment ■ There is no need to worry about corrosion as the process is carried out at room temperature.

■ 発泡の問題がなく、洗剤を限定する必要がな℃゛。■ There is no problem with foaming, and there is no need to limit the amount of detergent used.

■ 二次廃棄物の発生が少なし・。■ Less secondary waste is generated.

などの利点があるため、特に最近原子カプラントからの
洗浄廃水などの放射性物質を含有する排水を処理する方
法として注目され始めて℃・る。
Because of these advantages, it has recently begun to attract attention as a method for treating wastewater containing radioactive materials, such as washing wastewater from atomic couplants.

従来、洗浄排水を逆浸透処理装置によって濃縮水と清浄
水とに分離し、同清浄水は透過水として回収し、一方濃
縮水は洗浄排水タンクへ戻し所定の濃縮度になるまで逆
浸透処理を繰り返す排水の逆浸透処理方法には、たとえ
ば、第1図に示すような完全バッチ濃縮方式がある。
Conventionally, washing wastewater is separated into concentrated water and clean water using a reverse osmosis treatment device, and the clean water is recovered as permeate water, while the concentrated water is returned to the washing wastewater tank and subjected to reverse osmosis treatment until it reaches a predetermined concentration. Examples of repeated reverse osmosis treatment methods for wastewater include a complete batch concentration method as shown in FIG.

すなわち、第1図におし・て、aは洗浄排水タンクであ
り、同タンクaの上流側には洗浄排水供給管すが配設さ
れ、また同タンクaの底部には逆浸透処理装置供給水管
Cが配設されて℃・る。
That is, in Fig. 1, a is a washing wastewater tank, a washing wastewater supply pipe is installed on the upstream side of tank a, and a reverse osmosis treatment equipment supply pipe is installed at the bottom of tank a. Water pipe C is installed at ℃・℃.

上記逆浸透処理装置供給水管Cの他端は、排水ポンプd
1洗浄排水フィルタeおよび高圧ポンプfを介して逆浸
透処理装置gに連通している。
The other end of the reverse osmosis treatment equipment supply water pipe C is connected to a drainage pump d.
It is connected to a reverse osmosis treatment device g via a 1-wash drainage filter e and a high-pressure pump f.

上記逆浸透処理装置gには、逆浸透処理で分離する清浄
水(透過水)を流す透過水管りと濃縮水を流す濃縮水循
環管iが配設されており、同濃縮水循環管iは圧力調節
弁Va、冷却器jおよび濃縮水流路切換弁vbを介して
、上記洗浄排水タンクaへ循環するように配設されて(
・る。
The reverse osmosis treatment equipment g is equipped with a permeated water pipe for flowing clean water (permeated water) separated by reverse osmosis treatment and a concentrated water circulation pipe i for flowing concentrated water, and the concentrated water circulation pipe i is used for pressure adjustment. It is arranged so that it circulates to the washing waste water tank a via the valve Va, the cooler j and the concentrated water flow path switching valve vb (
・Ru.

なお、kは図示されな℃・ドラム諸室に連通された最終
濃縮水排出管である。
Note that k is a final concentrated water discharge pipe connected to various chambers of the temperature drum (not shown).

このような構成にお℃・て、洗浄排水は洗浄排水供給管
すから洗浄排水タンクaへ流れ込み所定量貯留されると
図示されなし・洗浄排水供給開閉弁を閉の状態にして洗
浄排水の供給を断ちつ℃・で排水ポンプdおよび高圧ポ
ンプfを駆動させ排水フィルターeで排水中の粗浮遊物
質を除去したのち高圧な排水として逆浸透処理装置gに
送り込み、上記排水を清浄水と濃縮水とに分離する。
In such a configuration, the cleaning wastewater flows from the cleaning wastewater supply pipe to the cleaning wastewater tank a and is stored in a predetermined amount. The drainage pump d and the high-pressure pump f are driven at ℃・, coarse suspended solids in the drainage are removed by the drainage filter e, and the wastewater is sent to the reverse osmosis treatment device g as high-pressure drainage, and the above drainage is purified water and concentrated water. Separate into two parts.

上記清浄水は透過水として透過水管りから系外へ放出さ
れる。
The above-mentioned clean water is discharged out of the system from the permeate pipe as permeate water.

この際、透過水の水質が、再利用または放流するに不適
の場合には、さらに高次の処理をして再利用または放流
して℃・た。
At this time, if the quality of the permeated water is unsuitable for reuse or discharge, it is treated at a higher level and then reused or discharged.

一方、濃縮水は濃縮水循環管iを通り、逆浸透処理装置
gにかかる水圧差が過大にならぬように圧力調節弁Va
で水圧調節がなされ、つ℃・で冷却器jで冷却されたの
ち濃縮水流路切換弁vbを通って洗浄排水タンクaに循
環返送されて(・た。
On the other hand, the concentrated water passes through the concentrated water circulation pipe i, and the pressure regulating valve Va
The water pressure is adjusted at 10°C, and after being cooled in a cooler j at 10°C, it is circulated back to the wash water tank a through a concentrated water flow path switching valve vb.

つし・で、上記の逆浸透処理工程を繰り返すことによっ
て、濃縮水は引続き濃縮され続ける。
The concentrated water continues to be concentrated by repeating the above reverse osmosis treatment process.

この工程におし・ては、洗浄排水タンクaの水位は逆浸
透処理が繰り返えされるにつれて順次低下して行く。
In this process, the water level in the wash water tank a gradually decreases as the reverse osmosis treatment is repeated.

所定の濃縮度になったとき、濃縮水流路切換弁vbを切
換えて、濃縮水循環管iを最終濃縮水排出管にへ連通さ
せ高圧ポンプfの稼動を停止したのち、図示されなし・
洗浄排水供給開閉弁を開の状態にして洗浄排水を洗浄排
水タンクaの所定の水位まで水張りし、再び高圧ポンプ
fを駆動させ、洗浄排水タンクa、高圧ポンプfおよび
逆浸透処理装置供給水管Cなどの逆浸透処理装置供給水
系や逆浸透処理装置gならびに冷却器jや濃縮水循環管
iなどの濃縮水循環系に残存する数十倍〜数百倍に濃縮
された最終濃縮水を洗浄排水のピストンフロー作用によ
って最終濃縮水排出管kを介して図示されな℃・ドラム
諸室へ移送する。
When a predetermined concentration level is reached, the concentrated water flow path switching valve vb is switched, the concentrated water circulation pipe i is connected to the final concentrated water discharge pipe, and the operation of the high pressure pump f is stopped.
The cleaning drainage supply on/off valve is opened, cleaning drainage tank a is filled with cleaning drainage tank a to a predetermined water level, high pressure pump f is driven again, cleaning drainage tank a, high pressure pump f and reverse osmosis treatment equipment supply water pipe C. The final concentrated water concentrated tens to hundreds of times remaining in the reverse osmosis treatment equipment supply water system, reverse osmosis treatment equipment g, and the concentrated water circulation system such as cooler j and concentrated water circulation pipe i is used to clean the wastewater piston. By flow action, the concentrated water is transferred to various drum chambers (not shown) via the final concentrated water discharge pipe k.

しかし、この完全バッチ濃縮方式によれば、直接ドラム
詰が可能な最終濃縮水を得るまでには長時間を要するの
で、処理する排水が大量に放出される場合には、1バツ
チでの処理量を増大させる必要があり、したがって、大
容量の洗浄排水タンクの設置などコスト的に高価なもの
となって℃・た。
However, according to this complete batch concentration method, it takes a long time to obtain the final concentrated water that can be directly packed in drums, so when a large amount of wastewater is released, it is difficult to process the amount in one batch. Therefore, the cost of installing a large-capacity washing and drainage tank becomes expensive.

また、1バツチで処理する間には、放出される排水を貯
留させておく貯留タンクが必要であり、この設備費も放
出される排水の量によってはかなり高価なものとなって
℃・た。
Furthermore, during one batch treatment, a storage tank is required to store the discharged wastewater, and the cost of this equipment can be quite expensive depending on the amount of discharged wastewater.

”さらに、完全バッチ方式では洗浄排水供給弁、
濃縮水流路切換弁などの弁操作を頻繁に行なう必要があ
って、運転操作が非常に煩雑となるなどの欠点を有して
(・た。
``Furthermore, in the complete batch system, the cleaning drainage supply valve,
It has the disadvantage that it is necessary to frequently operate valves such as the concentrated water flow path switching valve, making the operation extremely complicated.

さらにまた、逆浸透処理装置gから圧出される透過水中
の不純物の含有率は逆浸透処理装置の膜面に供給される
逆浸透処理装置供給水の不純物の含有率に比例しており
、従来の完全バッチ濃縮方式では膜面に供給される逆浸
透処理装置供給水中の不純物の含有率は早急に高くなる
ので、それに比例して透過水中の不純物の含有率も早急
に高(なり、したがって、透過水の水質は急激に悪化し
1バッチ当りそのまま再使用又は放流出来る良質の透過
水の量は僅かなものであった。
Furthermore, the content of impurities in the permeate water pumped out from the reverse osmosis treatment device g is proportional to the content of impurities in the water supplied to the reverse osmosis treatment device that is supplied to the membrane surface of the reverse osmosis treatment device. In the complete batch concentration method, the content of impurities in the reverse osmosis treatment equipment feed water that is supplied to the membrane surface increases rapidly, so the content of impurities in the permeate water also increases rapidly in proportion to this. The quality of the water deteriorated rapidly, and the amount of good quality permeate water that could be reused or discharged per batch was small.

本発明は、洗浄排水タンクの下流側に設けた所定容量の
循環タンクに供給された被処理排水を高圧ポンプを介し
て逆浸透処理装置に供給して上記排水を濃縮水と透過水
とに分離し、ついで上記濃縮水を冷却器を通したのち上
記循環タンクへ返送する工程を繰返して濃縮を行℃・、
濃縮倍率が数十倍迄は、上記排水タンクから上記排水を
供給して上記循環タンクの水位を一定に保持して引続き
濃縮を行なし・、つ℃・で上記排水タンクと上記循環タ
ンクとの連通を断ち引続き濃縮を行なうことを特徴とし
、その目的とする処は、上記従来の欠点を解消し、大量
の排水を効率良く処理する方法を提供するものである。
In the present invention, wastewater to be treated is supplied to a circulation tank with a predetermined capacity provided downstream of a cleaning wastewater tank, and is then supplied to a reverse osmosis treatment device via a high-pressure pump to separate the wastewater into concentrated water and permeated water. Then, the concentrated water is concentrated by repeating the process of passing it through the cooler and returning it to the circulation tank.
Until the concentration ratio is several tens of times, the water level in the circulation tank is kept constant by supplying the waste water from the waste water tank to continue concentration. It is characterized by cutting off the communication and continuing concentration, and its purpose is to eliminate the above-mentioned conventional drawbacks and provide a method for efficiently treating a large amount of wastewater.

なお、本発明は、このように洗浄排水タンクの下流側に
設けた所定容量の循環タンクに供給された被処理排水を
高圧ポンプを介して逆浸透処理装置に供給して上記排水
を濃縮水と透過水とに分離し、つし・て上記濃縮水を冷
却器を通したのち上記循環タンクへ返送する工程を繰返
して濃縮を行℃・、濃縮倍率が数十倍迄は、上記排水タ
ンクから上記排水を供給して上記循環タンクの水位を一
定に保持して引続き濃縮を行なうので、大量な排水を効
率良く処理することが出来、また、循環タンク内の濃縮
水は洗浄排水タンクからの排水によって希稀され続ける
ので透過水の水質も急激に悪化せず、゛良質の透過水を
大量に得ることが出来る。
In addition, in the present invention, the wastewater to be treated is thus supplied to the circulation tank of a predetermined capacity provided downstream of the washing wastewater tank to the reverse osmosis treatment device via the high-pressure pump, and the wastewater is converted into concentrated water. Concentration is carried out by repeating the process of separating the water from the permeated water, passing it through a cooler, and then returning it to the circulation tank. Since the water level in the circulation tank is kept constant by supplying the waste water and concentrating it continuously, a large amount of waste water can be efficiently treated. Also, the concentrated water in the circulation tank can be used as waste water from the cleaning waste water tank. Since the permeate water continues to be diluted, the quality of the permeate water does not deteriorate rapidly, and a large amount of high-quality permeate water can be obtained.

さらに、濃縮倍率が数十倍になった後は、上記排水タン
クと上記循環タンクとの連通を断ち引続℃・て排水を濃
縮するので、濃縮水の最終濃縮倍率が急速に高し・もの
となり、そのままドラム詰め可能な最終濃縮水を早急に
得ることが出来る。
Furthermore, after the concentration ratio increases to several tens of times, the communication between the wastewater tank and the circulation tank is cut off and the wastewater is concentrated at ℃, so the final concentration ratio of the concentrated water rapidly increases. , it is possible to quickly obtain final concentrated water that can be packed into drums as is.

以下、この発明の最も好まし℃・一実施例として第2図
に示す図示実施例にて説明すると、1は洗浄排水タンク
であり、同タンク1の上流側には、洗浄排水供給管2が
配設されて℃・る。
The most preferred embodiment of the present invention will be described below with reference to the illustrated embodiment shown in FIG. It is arranged at ℃・ru.

3は循環タンク供給水管であり、間管3には循環タンク
供給水用ポンプ4、循環タンク供給水用フィルタ5およ
び循環タンク供給水用自動制御弁V、が介装されており
、上流端は上記洗浄排水タンク1の底部に開口し、下流
端は循環タンク6の上部に開口しても・る。
3 is a circulation tank supply water pipe, and the intermediate pipe 3 is equipped with a circulation tank supply water pump 4, a circulation tank supply water filter 5, and a circulation tank supply water automatic control valve V. It opens at the bottom of the cleaning drainage tank 1, and the downstream end opens at the top of the circulation tank 6.

7は、循環タンク供給水用分流管であり、間管7には手
動開閉弁■2が開状態で介装されており、一端は上記フ
ィルタ5と上記弁v1 との中間の上記循環タンク供給
水管3に開口し、他端は上記洗浄排水タンク1の上部に
開口しても・る。
Reference numeral 7 denotes a distribution pipe for supplying water to the circulation tank, and a manual on-off valve 2 is interposed in the intermediate pipe 7 in an open state, and one end is connected to the circulation tank supply water between the filter 5 and the valve v1. It opens into the water pipe 3, and the other end opens into the upper part of the washing and draining tank 1.

8は逆浸透処理装置供給水管であり、間管8には高圧ポ
ンプ9および逆浸透処理装置供給水用自動開閉弁V3が
介装されており上流端は上記循環タンク6の底部に開口
し下流端は逆浸透処理装置10に開口している。
Reference numeral 8 denotes a reverse osmosis treatment equipment supply water pipe, and the intermediate pipe 8 is equipped with a high-pressure pump 9 and an automatic opening/closing valve V3 for the reverse osmosis treatment equipment supply water, and the upstream end opens at the bottom of the circulation tank 6 and the downstream The end opens into the reverse osmosis treatment device 10 .

11は濃縮水循環管であり、間管11には濃縮水圧力自
動制御弁v4、冷却器12および濃縮水流路自動切換弁
v5が介装されており、一端は上記逆浸透処理装置10
に開口し、他端は上記循環タンク6の上部に開口して℃
・る。
11 is a concentrated water circulation pipe, and the intermediate pipe 11 is provided with a concentrated water pressure automatic control valve v4, a cooler 12, and a concentrated water flow path automatic switching valve v5, and one end is connected to the reverse osmosis treatment device 10.
℃, and the other end is opened at the top of the circulation tank 6.
・Ru.

なお、13は上記弁V、から分枝する最終濃縮水排出管
である。
In addition, 13 is a final concentrated water discharge pipe branching from the above-mentioned valve V.

14は;逆浸透処理装置供給水分流管であり、間管14
には逆浸透処理装置供給水分流用自動開閉弁■6が介装
されており、一端は上記高圧ポンプ9と上記弁■3との
中間の上記逆浸透処理装置供給水管8に開口し他端は上
記逆浸透処理装置10と上記弁v4 との中間の上記濃
縮水循環管11に開口して(・る。
14 is a reverse osmosis treatment equipment supply water flow pipe;
is equipped with an automatic opening/closing valve (6) for water flow to the reverse osmosis treatment equipment, one end of which opens into the reverse osmosis treatment equipment supply water pipe 8 located between the high pressure pump 9 and the valve (3), and the other end. It opens into the concentrated water circulation pipe 11 located between the reverse osmosis treatment device 10 and the valve v4.

15は透過水流通管であり、一端は上記逆浸透処理装置
10に開口し他端は透過水タンク16の側壁に開口して
おり、また、17は一端が上記透過水タンク16の底部
に開口する透過水排出管であり、間管17には透過水ポ
ンプ18および透過水流路自動切換弁v7が介装されて
おり、量弁v7は切換によって、その他端が上記洗浄排
水タンク1の上部に開口する透過水タンク19またはそ
の他端が図示されなし・回収水モニタタンクに開口する
回収水供給管20のそれぞれ一端に連通ずるように配設
されて℃・る。
15 is a permeated water distribution pipe, one end of which opens into the reverse osmosis treatment device 10 and the other end into the side wall of the permeated water tank 16; and 17, one end which opens into the bottom of the permeated water tank 16. The intermediate pipe 17 is equipped with a permeate pump 18 and a permeate flow path automatic switching valve v7, and the volume valve v7 is switched so that the other end is connected to the upper part of the cleaning drainage tank 1. The open permeated water tank 19 or the other end is disposed so as to communicate with one end of each of the recovered water supply pipes 20 (not shown) which open to the recovered water monitor tank.

また、FMCIAは上記循環タンク供給水管3に配設さ
れた流量積算指示警報計であり、間管3内に流れる洗浄
排水の流量を計測し積算するとともに所定の濃縮倍率に
応じて供給総流量を指示しかつ所定の指示流量になると
自動的に指令警報を発言するものである。
In addition, FMCIA is a flow rate integration indicator installed in the circulation tank supply water pipe 3, which measures and integrates the flow rate of cleaning wastewater flowing into the water pipe 3, and calculates the total supply flow rate according to a predetermined concentration ratio. When a specified flow rate is reached, a command alarm is automatically issued.

LICAは上記循環タンク6に、配設された水位指示調
節警報計であり、同タンク6内の水位を検知するととも
に、上記循環タンク6への洗浄排水の供給による水位の
変化および洗浄排水の濃縮による水位変化によって同タ
ンク6内の指示水位を自動的に調節しかつ同タンク6内
の水位が指示水位になると自動的に指令警報を発信する
ものである。
LICA is a water level indicating adjustment alarm installed in the circulation tank 6, and it detects the water level in the tank 6, and also detects changes in the water level and concentration of the washing waste water by supplying washing waste water to the circulation tank 6. The designated water level in the tank 6 is automatically adjusted according to the water level change caused by the change in water level, and a command alarm is automatically issued when the water level in the tank 6 reaches the designated water level.

CIA−1は上記逆浸透処理装置供給水管8の上記循環
タンク6と上記高圧ポンプ9の中間に配設された逆浸透
処理装置供給水用の電導度指示警報計であり、同供給水
管8内を流れる逆浸透処理装置供給水に含有される不純
物の濃度を電気伝導度で計測するとともに、所定の電導
度を指示しかつ同供給水の電導度が所定の指示値になっ
たとき自動的に指令警報を発信するものである。
CIA-1 is a conductivity indicator and alarm meter for the reverse osmosis treatment equipment supply water, which is disposed between the circulation tank 6 and the high pressure pump 9 of the reverse osmosis treatment equipment supply water pipe 8; In addition to measuring the concentration of impurities contained in the reverse osmosis treatment equipment supply water flowing through the flow through electrical conductivity, it also indicates a predetermined electrical conductivity, and automatically when the electrical conductivity of the supplied water reaches a predetermined indicated value. It is used to send out command warnings.

TIAおよびPIAは上記逆浸透処理装置供給水管8の
上記高圧ポンプ9と上記逆浸透処理装置供給水分流管1
4の分岐点との中間に配設された温度指示警報計および
圧力指示警報計であり、前者は同供給水管8内を流れる
逆浸透処理装置供給水の温度を計測するとともに所定の
温度を指示しかつ同供給水の温度が所定の指示値になっ
たとき自動的に指令警報を発信するものであり、後者は
同供給水の圧力を計測するとともに所定の圧力を指示し
かつ同供給水の圧力が所定の指示値になったとき自動的
に指令警報を発信するものである。
TIA and PIA are the high pressure pump 9 of the reverse osmosis treatment equipment supply water pipe 8 and the reverse osmosis treatment equipment supply water flow pipe 1.
A temperature indicating alarm meter and a pressure indicating alarm meter are disposed between the branch point 4 and the water supply pipe 8, and the former measures the temperature of the reverse osmosis treatment equipment supply water flowing in the supply water pipe 8 and indicates a predetermined temperature. Moreover, when the temperature of the supplied water reaches a predetermined indicated value, a command and alarm is automatically sent out.The latter measures the pressure of the supplied water, indicates the predetermined pressure, and It automatically issues a command alarm when the pressure reaches a predetermined indicated value.

PICは上記濃縮水循環管11の上記逆浸透処理装置1
0と上記濃縮水圧力自動制御弁v4との中間に配設され
た圧力指示調節計であり、濃縮水の圧力を計測するとと
もにその計測値によって同濃縮水の圧力を所定の強さに
自動的に指示調節するものである。
PIC is the reverse osmosis treatment device 1 of the concentrated water circulation pipe 11
This is a pressure indicating regulator installed between 0 and the automatic concentrated water pressure control valve v4, which measures the pressure of concentrated water and automatically adjusts the pressure of the concentrated water to a predetermined strength based on the measured value. This is to adjust the instructions accordingly.

FICおよびCIA−2は上記透過水流通管15に配設
された流量指示調節計および透過水用の電導度指示警報
計であり、前者は同流通管15内を流れる透過水の流量
を計測するとともに、その計測値によって同透過水の流
量を所定の値に指示調節するものであり、後者は同透過
水の電気伝導度を計測するとともに所定の電導度を指示
し、かつ同透過水の電導度が所定の指示値になったとき
自動的に指令警報を発信するものである。
FIC and CIA-2 are a flow rate indicating controller and a conductivity indicating alarm meter for permeated water disposed in the permeated water distribution pipe 15, and the former measures the flow rate of permeated water flowing inside the permeated water distribution pipe 15. At the same time, the flow rate of the permeated water is instructed and adjusted to a predetermined value based on the measured value. It automatically issues a command alarm when the temperature reaches a predetermined indicated value.

LSは上記透過水タンク16に配設された水位スイッチ
であり、同タンク16の水位を検知するとともに同タン
ク16の水位が所定の高さになると作動するものである
LS is a water level switch disposed in the permeated water tank 16, which detects the water level of the tank 16 and is activated when the water level of the tank 16 reaches a predetermined height.

また、上記流量積算指示警報FMCIAと上記循環タン
クポンプ4、上記循環タンク供給水用自動制御弁V1
および上記透過水流路自動切換弁V7との間、上記水位
指示調節警報計LICAと上記循環タンク供給水用自動
制御弁v1、上記高圧ポンプ9および上記濃縮水流路自
動切換弁v5 との間、上記逆浸透処理装置供給水用の
電導塵指示警報計ClA1と上記濃縮水流路自動切換弁
V5および循環タンク供給水用自動制御弁v1 との
間、上記温度指示警報計TIAと上記逆浸透処理装置供
給水用自動開閉弁v3および上記逆浸透処理装置供給水
分流用自動開閉弁V6どの間、上記圧力指示警報計PI
Aと上記逆浸透処理装置供給水用自動開閉弁V3および
上記逆浸透処理装置供給水分流用自動開閉弁■6どの間
、上記圧力指示調節計PICと上記濃縮水圧力自動制御
弁v4 との間、上記流量指示調節計FICと上記濃縮
水圧力自動制御弁v4 との間、上記透過水用の電導塵
指示警報計CIA−2と上記透過水流路自動切換弁V7
との間、上記水位スイッチLSと上記透過水ポンプ18
との間がそれぞれ電気信号伝達線により連結されて℃・
る。
In addition, the above-mentioned flow rate integration instruction alarm FMCIA, the above-mentioned circulation tank pump 4, and the above-mentioned circulation tank supply water automatic control valve V1
and the permeated water flow path automatic switching valve V7, between the water level indication adjustment alarm meter LICA and the circulation tank supply water automatic control valve v1, the high pressure pump 9 and the concentrated water flow path automatic switching valve v5, Between the conductive dust indicator and alarm meter ClA1 for the reverse osmosis treatment equipment supply water, the concentrated water flow path automatic switching valve V5 and the automatic control valve V1 for the circulation tank supply water, the temperature indication and alarm meter TIA and the reverse osmosis treatment equipment supply Automatic on-off valve V3 for water and automatic on-off valve V6 for the flow of water supplied to the reverse osmosis treatment equipment, and the pressure indicator and alarm meter PI
Between A and the automatic opening/closing valve V3 for water supplied to the reverse osmosis treatment equipment and the automatic opening/closing valve ■6 for water flow supplied to the reverse osmosis treatment equipment, between the pressure indicating regulator PIC and the automatic concentrated water pressure control valve v4, Between the flow rate indicating controller FIC and the concentrated water pressure automatic control valve v4, the permeated water conductive dust indicator and alarm meter CIA-2 and the permeated water flow path automatic switching valve V7
between the water level switch LS and the permeated water pump 18.
are connected by electrical signal transmission lines to
Ru.

本実施例はこのように構成されて℃・るため、原子プラ
ントから排出される洗濯、手洗℃・およびシャワー排水
などのように放射性物質を不純物として含む洗浄排水は
洗浄排水供給管2から洗浄排水タンク1に注入貯留され
たのち、循環タンクポンプ4の稼動により循環タンク供
給水管3内を流れ循環タンクフィルタ5によって水中の
粗浮遊物が除去されたのち開状態の循環タンク供給水用
自動制御弁V1を流過し流量積算指示警報計 FMCIAで流過する流量を積算して計測されつ**つ
、循環タンク6内に所定水位まで供給される。
Since this embodiment is configured as described above, cleaning wastewater containing radioactive substances as impurities such as laundry, hand washing and shower wastewater discharged from a nuclear plant is transferred from the washing wastewater supply pipe 2 to the washing wastewater. After the water is injected and stored in the tank 1, it flows through the circulation tank supply water pipe 3 by the operation of the circulation tank pump 4, and after coarse suspended matter in the water is removed by the circulation tank filter 5, the automatic control valve for the circulation tank supply water is opened. The flow rate flowing through V1 is integrated and measured by the flow rate integration indicator FMCIA, and is supplied to the circulation tank 6 up to a predetermined water level.

つ℃・で、同排水は、逆浸透処理装置供給水として循環
タンク6底部から逆浸透処理装置供給水管8内に流出し
電導塵指示警報計CIA−1で電導塵を計測され高圧ポ
ンプ9で昇圧され温度指示警報計TIAおよび圧力指示
警報計PIAで温度および圧力が計測され開状態の弁V
3を流過したのち逆浸透処理装置10に圧入され清浄水
と濃縮水とに分離される。
The waste water flows out from the bottom of the circulation tank 6 into the reverse osmosis treatment equipment supply water pipe 8 as reverse osmosis treatment equipment supply water, conductive dust is measured by the conductive dust indicator and alarm meter CIA-1, and the high pressure pump 9 The pressure is increased and the temperature and pressure are measured by the temperature indicator and alarm meter TIA and the pressure indicator and alarm meter PIA, and the valve V is in the open state.
3, the water is pressurized into a reverse osmosis treatment device 10 and separated into clean water and concentrated water.

上記濃縮水は濃縮水循環管11内を流れ、圧力指示調節
計PICで圧力が計測され弁V4で所定の圧力に調節さ
れたのち、冷却器12で冷却され、つ℃・で弁v5を通
過して循環タンク6へ返送される。
The concentrated water flows through the concentrated water circulation pipe 11, the pressure is measured by the pressure indicator controller PIC, and the pressure is adjusted to a predetermined pressure by the valve V4, then cooled by the cooler 12, and passed through the valve V5 at 10°C. and is returned to the circulation tank 6.

さらに、循環タンク6へ返送された濃縮水は、水位指示
調節警報計LICAおよび弁v1 によって一定水位に
なるまで供給されつづける洗浄排水で薄められながら再
び高圧ポンプ9の作動によって逆浸透処理装置10へ送
り込まれ、引続き濃縮され続ける。
Furthermore, the concentrated water returned to the circulation tank 6 is diluted with washing waste water that is continuously supplied until a constant water level is reached by the water level indicator LICA and the valve v1, and is then sent to the reverse osmosis treatment device 10 again by the operation of the high pressure pump 9. It continues to be concentrated.

このような逆浸透処理工程の繰り返)しによって濃縮処
理される洗浄排水の濃縮倍率が数十倍すなわち循環タン
ク内水位一定時の系内ホールドアツプ量の数十倍程度の
洗浄排水が循環タンク6に供給されたことが、流量積算
指示警報計FMCIAで計測されると同警報計FMCI
Aの1 信号により弁V1は開状態となり洗浄排水タン
ク1と循環タンク6との連通は断たれ洗浄排水は洗浄排
水分流管7を通って洗浄排水タンク1へ返送される。
By repeating such reverse osmosis treatment process, the concentration ratio of the cleaning wastewater is several tens of times, that is, when the water level in the circulation tank is constant, the amount of cleaning wastewater that is held up in the system is several tens of times as much as the circulation tank. 6 is measured by the flow rate integration indicator alarm meter FMCIA, the same alarm meter FMCI
The valve V1 is opened by the A-1 signal, the communication between the cleaning drainage tank 1 and the circulation tank 6 is cut off, and the cleaning drainage water is returned to the cleaning drainage tank 1 through the cleaning drainage distribution pipe 7.

なお、上記濃縮倍率とは、次式で示されるものである。In addition, the said concentration magnification is shown by the following formula.

但、系内ホールドアツプ量;上記循環タンク、上記高圧
ポンプ、上記逆浸透処理装置、上記冷却器および上記各
装置などを連通ずる配管内に保持されて℃・る容積総量
However, the amount of hold-up in the system is the total volume held in the piping that communicates the circulation tank, the high-pressure pump, the reverse osmosis treatment equipment, the cooler, and each of the above devices, etc. in °C.

この場合、警報計FMCIAの信号によって循環ポンプ
4の作動を停止することによって洗浄排水タンク1と循
環タンク6との連通な断っても良し・し、あるし・は逆
浸透処理装置供給水用の電導塵指示警報計CIA−1の
計測値が指示型導度になったとき、信号によって弁V1
を閉にして洗浄排水タンク1と循環タンク6との連通
を断っても良℃・。
In this case, the communication between the wash water tank 1 and the circulation tank 6 may be cut off by stopping the operation of the circulation pump 4 in response to a signal from the alarm meter FMCIA, or the communication between the wash water tank 1 and the circulation tank 6 may be interrupted. When the measured value of the conductive dust indicator and alarm meter CIA-1 reaches the indicator type conductivity, a signal closes the valve V1.
It is also possible to cut off the communication between the cleaning drainage tank 1 and the circulation tank 6 by closing the tank.

この状態で、第1図に示すような循環タンク6→高圧ポ
ンプ9→弁v3→逆浸透処理装置10→弁v4→冷却器
12→弁v5→循環タンク6と℃・うクロードシステム
で逆浸透処理を繰り返しながら、引き続き濃縮工程を続
ける。
In this state, as shown in Fig. 1, reverse osmosis is carried out using the circulation tank 6 → high pressure pump 9 → valve v3 → reverse osmosis treatment device 10 → valve v4 → cooler 12 → valve v5 → circulation tank 6 and the C/C load system. Continue the concentration process by repeating the process.

(以下、最終濃縮工程と云う。(Hereinafter referred to as the final concentration step.

)この最終濃縮工程では、循環タンク6の水位を下げな
がら、最終濃縮倍率が数十倍〜数百倍迄になるまで処理
される。
) In this final concentration step, the water level in the circulation tank 6 is lowered until the final concentration ratio reaches several tens to hundreds of times.

なお、最終濃縮倍率とは、次式で表わされるものである
Note that the final concentration ratio is expressed by the following formula.

この最終濃縮倍率は水位指示調節警報計几ICAで循環
タンク6の水位を計測することによって計測されるもの
であり、濃縮によって循環タンク6の水位が低下し、所
定の最終濃縮倍率に対応する水位が計測されると水位指
示調節警報計LICAの信号によって高圧ポンプ9が停
止されまた弁■5が切換えられ濃縮水循環管11は最終
濃縮水排出管13へ連通するようになる。
This final concentration magnification is measured by measuring the water level in the circulation tank 6 with the water level indication adjustment alarm meter ICA, and the water level in the circulation tank 6 decreases due to concentration, and the water level corresponds to the predetermined final concentration magnification. When this is measured, the high pressure pump 9 is stopped by a signal from the water level indication adjustment alarm meter LICA, and the valve 5 is switched so that the concentrated water circulation pipe 11 is brought into communication with the final concentrated water discharge pipe 13.

なお、この場合、逆浸透処理装置供給水用の電導度指示
警報計CIA−1の計測値により高圧ポンプ9の停止や
V5の切換えを行なっても良し・。
In this case, the high pressure pump 9 may be stopped or V5 may be switched based on the measured value of the conductivity indicator/alarm meter CIA-1 for the water supplied to the reverse osmosis treatment equipment.

つし・で、水位指示調節警報計LICAまたは電導度指
示警報計CIA−1の電気信号によって弁V1 を開の
状態にし洗浄排水を循環タンク6の所定の水位まで水張
りし、所定水位になったことを水位指示調節警報計I、
I CAで確認したのち、その信号によって高圧ポンプ
9を作動し、洗浄排水のピストンフロー作用によって、
最終濃縮状態で系内にホールドアツプされて℃・る最終
濃縮水を最終濃縮水排出管13から図示されな℃・ドラ
ム諸室へ送り込む。
At the water level, the valve V1 was opened by the electric signal from the water level indicator/adjustment alarm meter LICA or the conductivity indicator/alarm meter CIA-1, and the cleaning waste water was filled to the specified water level in the circulation tank 6, and the specified water level was reached. Water level indication adjustment alarm meter I,
After checking with ICA, the high-pressure pump 9 is operated based on the signal, and the piston flow action of the cleaning waste water is used to
The final concentrated water held up in the system in the final concentrated state at a temperature of .degree. C. is sent from the final concentrated water discharge pipe 13 to various chambers of a drum, not shown.

系内の最終濃縮水が完全にフ霜−されたことは、循環タ
ンク6の水位変化を水位指示調節警報計LICAによっ
て計測することによって確認できる。
Whether the final concentrated water in the system has been completely defrosted can be confirmed by measuring changes in the water level in the circulation tank 6 using the water level indicator adjustment alarm meter LICA.

一方、上記清浄水は透過水となって透過水流通管15内
を流れ流量指示調節計FICで間管15内の流量を計測
しその計測値によって弁v4の圧力を圧力指示調節計P
ICによって調節しそれによって透過水流通管15内の
流量が同一流量になるよう自動的に調節され、また電導
度指示警報計CIA−2で電導度を計測されつつ透過水
タンク16へ供給される。
On the other hand, the above-mentioned clean water becomes permeated water and flows through the permeated water distribution pipe 15, and the flow rate in the interpipe 15 is measured by the flow rate indicating controller FIC, and the pressure of the valve v4 is adjusted based on the measured value by the pressure indicating regulator P.
The permeate water is adjusted by the IC so that the flow rate in the permeate flow pipe 15 is automatically adjusted to the same flow rate, and the permeate water is supplied to the permeate tank 16 while its conductivity is measured by the conductivity indicator and alarm meter CIA-2. .

さらに、同タンク16に貯留された上記透過水は水位が
上昇して逆浸透処理装置10の設置位置と同じレベルに
なると水位スイッチLSが作動し同水位スイッチLSに
電気的に連結された透過水ポンプ18が稼動することに
よって透過水タンク16の底部から透過水排出管17へ
流れ込み弁■7を通り図示されな℃・回収水モニタタン
クに貯留されたのち洗浄水などとして再使用または放流
される。
Further, when the water level of the permeated water stored in the tank 16 rises to the same level as the installation position of the reverse osmosis treatment device 10, the water level switch LS is activated, and the permeated water electrically connected to the water level switch LS is activated. When the pump 18 operates, the permeated water flows from the bottom of the permeated water tank 16 to the permeated water discharge pipe 17, passes through the valve 7, is stored in a temperature/recovered water monitor tank (not shown), and is then reused or discharged as cleaning water, etc. .

また、洗浄排水が上記の濃縮処理工程によって所定の濃
縮倍率(約数十倍程度)に濃縮されると、流量積算指示
警報計FMCIAの電気信号によって弁v1 が閉状態
になり洗浄排水タンク1と循環タンク6との連通が断た
れ、それと同時に、同警報計FMCIAからは電気信号
によって弁V7が切換えられ透過水排出管17は透過水
返送管19に連通し、透過水は透過水返送管19によっ
て洗浄排水タンク1へ返送される。
In addition, when the cleaning wastewater is concentrated to a predetermined concentration ratio (approximately several tens of times) through the above-mentioned concentration process, the valve v1 is closed by the electrical signal from the flow integration indicator FMCIA, and the cleaning wastewater tank 1 is closed. Communication with the circulation tank 6 is cut off, and at the same time, the valve V7 is switched by an electric signal from the alarm meter FMCIA, and the permeated water discharge pipe 17 is communicated with the permeated water return pipe 19. is returned to the cleaning drainage tank 1.

なお、この場合、透過水流通管15内を流れる透過水の
電導度を透過水用の電導度指示警報計CI A−2で計
測し、計測値が指示型導度になったとき同警報計CIA
−2の信号によって弁v7を切換えても良℃・0また、
逆浸透処理装置供給水の温度または圧力が指示値になる
と温度指示警報計TIAまたは圧力指示警報計PIAの
電気信号によって弁V3は閉状態、弁V6は開状態とな
り逆浸透処理装置供給水は逆浸透処理装置供給水分流管
14を通り濃縮水循環管11へ直接流れ込む。
In this case, the conductivity of the permeated water flowing in the permeated water distribution pipe 15 is measured by the conductivity indicator alarm meter CI A-2 for permeated water, and when the measured value becomes the indicator type conductivity, the alarm meter C.I.A.
-2 signal can be used to switch valve v7.℃・0Also,
When the temperature or pressure of the water supplied to the reverse osmosis treatment equipment reaches the indicated value, the electrical signal from the temperature indication alarm meter TIA or the pressure indication alarm meter PIA causes the valve V3 to close and the valve V6 to open, causing the reverse osmosis treatment equipment supply water to flow in the reverse direction. It flows directly into the concentrated water circulation pipe 11 through the percolation treatment equipment supply water flow pipe 14 .

このように、洗浄排水タンク1の下流側に設けた所定容
量の循環タンク6に供給された洗浄排水を高圧ポンプ9
を介して逆浸透処理装置10に供給して上記排水を濃縮
水と透過水とに分離し、つし・で上記濃縮水を冷却器1
2を通したのち循環タンク6へ返送する工程を繰返して
濃縮を行℃・、濃縮倍率が数十倍迄は洗浄排水タンク1
から排水を供給して循環タンク6の水位を水位指示調節
警報計LICAによって検知しながら一定に保持して引
続き濃縮を行なうので、大量な洗浄水を効率良く処理す
ることが出来、また、循環タンク6内の ・濃縮水は洗
浄排水タンク1から循環タンク6の水位が一定になるま
でに供給される洗浄排水によって希稀され続けるので、
逆浸透処理装置10からの透過水の水質も急激に悪化せ
ず、良質の透過水を大量に得ることが出来る。
In this way, the cleaning wastewater supplied to the circulation tank 6 with a predetermined capacity provided downstream of the cleaning drainage tank 1 is transferred to the high-pressure pump 9.
The waste water is supplied to the reverse osmosis treatment device 10 via a water filter to separate the waste water into concentrated water and permeated water, and the concentrated water is sent to a cooler 1 through a water filter.
After passing through 2, the process of returning to circulation tank 6 is repeated for concentration.
Since the water level in the circulation tank 6 is detected by the LICA water level indicator and adjustment alarm meter and continues to be concentrated, a large amount of washing water can be efficiently processed. Concentrated water in 6 continues to be diluted by the washing wastewater supplied from the washing wastewater tank 1 until the water level in the circulation tank 6 becomes constant.
The quality of the permeated water from the reverse osmosis treatment device 10 does not deteriorate rapidly, and a large amount of high-quality permeated water can be obtained.

さらに、濃縮倍率が数十倍になった後は、流量積算指示
警報計FMCIAの電気信号によって弁v1 を閉状態
にするかあるし・は循環タンクポンプ4を停止するかま
たは電導度指示警報計CIA−1の電気信号によって弁
V1 を閉にするかによって洗浄排水タンク1と循環タ
ンク6との連通を断ち引続℃・て洗浄排水を最終濃縮倍
率で数十倍〜数百倍になるまで濃縮をするので濃縮水の
濃縮は急速に高められ、したがって、最終濃縮倍率が数
十倍〜数百倍になる最終濃縮水をきわめて早急にしかも
容易に得ることが出来る。
Furthermore, after the concentration ratio has increased several tens of times, valve v1 must be closed or the circulation tank pump 4 must be stopped by the electric signal from the flow rate integration indicator FMCIA, or the conductivity indicator alarm By closing the valve V1 in response to an electric signal from the CIA-1, the communication between the cleaning wastewater tank 1 and the circulation tank 6 is cut off, and the cleaning wastewater is then concentrated at a final concentration ratio of tens to hundreds of times at ℃. As a result, the concentration of concentrated water is rapidly increased, and therefore, final concentrated water with a final concentration factor of several tens to hundreds of times can be obtained very quickly and easily.

さらにまた、流量積算指示警報計FMCIAに循環タン
ク供給管3内を流れる積算流量を指示することによって
濃縮倍率をあらかじめセットしておくことが出来る。
Furthermore, the concentration magnification can be set in advance by indicating the cumulative flow rate flowing through the circulation tank supply pipe 3 to the flow rate cumulative indicator and alarm meter FMCIA.

また、濃縮水が所定の最終濃縮倍率になったときは、水
位指示調節警報計LICAによって弁V5は切換えられ
、したがって最終濃縮水を洗浄排水のピストンフロー作
用によって直接ドラム諸室へ送り込むことが出来最終濃
縮水のドラム詰の工程がきわめて容易となる。
Furthermore, when the concentrated water reaches a predetermined final concentration magnification, the valve V5 is switched by the water level indication adjustment alarm meter LICA, so that the final concentrated water can be directly sent to the drum chambers by the piston flow action of the washing waste water. The process of packing the final concentrated water into drums becomes extremely easy.

しかも、循環タンクポンプ4の起動停止、弁■1 の開
閉および弁V5の切換は各警報計FMCIA、LICA
、CIA−1の電気信号によって自動的に操作されるの
で洗浄排水のピストンフロー作用による最終濃縮水の系
外への排出もきわめて容易なものである。
Moreover, the start/stop of the circulation tank pump 4, the opening/closing of the valve 1, and the switching of the valve V5 are controlled by each alarm meter FMCIA and LICA.
Since the system is automatically operated by electric signals from the CIA-1, it is extremely easy to discharge the final concentrated water out of the system by the piston flow action of the washing waste water.

さらに、供給当初におし・て不純物含有率が高℃・洗浄
排水を数百倍の最終濃縮倍率になるように濃縮処理を行
った場合には最終濃縮水中の不純物含有率が非常に高く
なり、水位指示調節警報計LICAでは指示調節出来な
し・などの支障がある場合でも、電気度指示警報計CI
A−1による濃度管理をすることによって、上記の支障
を防ぐことが出来る。
Furthermore, if the impurity content is high at the time of supply and cleaning wastewater is concentrated to a final concentration ratio of several hundred times, the impurity content in the final concentrated water will be extremely high. Even if there is a problem such as the water level indicator and adjustment alarm meter LICA not being able to adjust the indication, the electricity level indicator and alarm meter CI
By controlling the concentration according to A-1, the above problems can be prevented.

さらにまた、逆浸透処理装置供給水の温度または圧力を
湿度指示警報計TIAまたは圧力指示警報計PIAで計
測し、指示値になると同警報計TIA、PIAの電気信
号により弁V3を閉、弁v6を開状態にして、異常温度
または異常圧力の逆浸透処理装置供給水を分流管14に
分流することによって逆浸透処理装置10の膜面が異常
温度または異常圧力にさらされるのが防げるので、膜の
保守上きわめて有効である。
Furthermore, the temperature or pressure of the water supplied to the reverse osmosis treatment equipment is measured by the humidity indicator and alarm meter TIA or the pressure indicator and alarm meter PIA, and when the indicated value is reached, the valve V3 is closed by the electric signal from the alarm meters TIA and PIA, and the valve V6 is closed. By opening the reverse osmosis treatment apparatus supply water at an abnormal temperature or pressure to the branch pipe 14, the membrane surface of the reverse osmosis treatment apparatus 10 can be prevented from being exposed to abnormal temperature or pressure. It is extremely effective for maintenance.

また、逆浸透膜は一般に膜面にふれる逆浸透処理装置供
給水の不純物含有率が上昇するにともな℃・透過水量が
減少する性質を有するため逆浸透処理装置10の処理容
量が変動すると℃・う欠点や長期使用にともなし・膜の
圧密化および膜面の汚れによって透過水量が減少すると
℃・う欠点を有して(・だが、透過水量が逆浸透処理装
置10の出口濃縮水の圧力に比例する性質を利用して、
濃縮水の圧力を圧力指示調節計PICで計測するか、あ
るし・は透過水の流量を流量指示調節計FICで計測し
て弁v4 によって濃縮水の圧力を自動的に調節するこ
とによって上記の欠点を解消し透過水の水量を一定に保
つとともに、逆浸透処理装置10内での運転圧力を低く
し、膜の長寿命を確保できるようにして℃・る。
In addition, reverse osmosis membranes generally have the property that as the impurity content of the water supplied to the reverse osmosis treatment device that comes into contact with the membrane surface increases, the temperature and amount of permeated water decrease.・Due to long-term use, the amount of permeated water decreases due to compaction of the membrane and dirt on the membrane surface. Utilizing the property of being proportional to pressure,
The above method can be carried out by measuring the pressure of the concentrated water with the pressure indicator controller PIC, or alternatively by measuring the flow rate of the permeated water with the flow indicator controller FIC and automatically adjusting the pressure of the concentrated water with the valve v4. By eliminating the drawbacks and keeping the amount of permeated water constant, the operating pressure within the reverse osmosis treatment device 10 is lowered to ensure a long life of the membrane.

一方、最終濃縮水を得る工程におし・ては、逆浸透処理
装置10の出口濃縮水の圧力を一定に圧力指示調節弁P
ICおよび弁v4で制御することによって、透過水の流
量を増大させる[ ので濃縮効率をさらに高めることが
出来る。
On the other hand, in the step of obtaining the final concentrated water, the pressure of the concentrated water at the outlet of the reverse osmosis treatment device 10 is kept constant by the pressure control valve P.
By controlling the IC and valve v4, the flow rate of permeated water can be increased, thereby further increasing the concentration efficiency.

さらに、透過水は濃縮倍率が数十倍迄は比較的水質は良
好なので回収水供給管20から再利用水または放流水と
して処理されるが、所定の濃縮倍率になって流量積算指
示警報計FMCIAなどに、 よって洗浄排水タンク1
と循環タンク6との連通が断たれると逆浸透処理装置1
0からの透過水の水質は急速に悪化するがその際流量積
算指示警報計FMCIAの電気信号によって弁v7が切
換えられ悪質の透過水は透過水返送管19から洗浄排;
水タンク1へ返送されるので、透過水はその水質の良
悪によって適格に区分けされる。
Furthermore, the quality of permeated water is relatively good until the concentration ratio is several tens of times, so it is treated as reuse water or discharge water from the recovered water supply pipe 20, but when the concentration ratio reaches a predetermined concentration ratio, the flow rate integration indicator etc. Therefore, cleaning drainage tank 1
When the communication between the circulation tank 6 and the reverse osmosis treatment device 1 is cut off,
The quality of the permeated water from 0 rapidly deteriorates, but at this time the valve v7 is switched by an electric signal from the flow rate integration indicator FMCIA, and the bad permeated water is cleaned and discharged from the permeated water return pipe 19;
Since the permeated water is returned to the water tank 1, it is appropriately classified according to its quality.

したがって、再利用または放流可能な透過水を有効に得
ることが出来るとともに、悪質な透過水は洗浄排水タン
ク1に戻されたあと再び上記の濃縮処理工程を経、て良
質な透過水の一部となり水の循環利用に極めて有効であ
る。
Therefore, it is possible to effectively obtain permeated water that can be reused or discharged, and the bad permeated water is returned to the cleaning wastewater tank 1 and then goes through the above concentration treatment process again, and a portion of the good quality permeated water is collected. This makes it extremely effective for water circulation.

なお、弁v7の切換は透過水の電導度を電導度指示警報
計CIA−2で計測し、その計測値によって切換えるこ
とも出来るようになって℃・るので、逆浸透処理装置1
0の膜の破壊に・ よって透過水の電導度が急激に上昇
した場合でもその悪質の透過水を弁V7の切換で洗浄排
水タンク1へ戻すことによって良質の透過水との混合を
未然に防ぐことが出来る。
The valve v7 can also be switched by measuring the conductivity of the permeated water with a conductivity indicator/alarm meter CIA-2 and switching based on the measured value.
Even if the electrical conductivity of the permeated water suddenly increases due to the destruction of the 0 membrane, the bad permeated water is returned to the cleaning drainage tank 1 by switching the valve V7, thereby preventing it from mixing with the good quality permeated water. I can do it.

さらにまた、逆浸透処理装置10の膜面の汚れを除去す
るためのホーム洗浄運転の必要時期につり・では、高圧
ポンプ9の出口側圧力で自動的に確認することができる
Furthermore, when a home cleaning operation is required to remove dirt from the membrane surface of the reverse osmosis treatment device 10, the pressure at the outlet side of the high-pressure pump 9 can be automatically checked.

すなわち、一般に膜面の汚れに伴なって透過水量は減少
して来るのであるがこの実施例では透過水量を一定に保
つために高圧ポンプ9の出口側圧力を制御しており、高
圧ポンプ9の出口側圧力を通常よりも高めても規定の透
過水量が得られなし・場合にはボール洗浄が必要である
ことを自動的に確認することができる。
In other words, the amount of permeated water generally decreases as the membrane surface becomes fouled, but in this embodiment, the pressure on the outlet side of the high-pressure pump 9 is controlled in order to keep the amount of permeated water constant. If the specified amount of permeated water is not obtained even if the outlet side pressure is raised higher than usual, it can be automatically confirmed that ball cleaning is necessary.

また、逆浸透処理装置10の近接位置に透過水タンク1
6を設置し逆浸透処理装置10と透過水タンク16の水
位とのヘッド差によって透過水を透過水タンク16内に
流し落すとともに、水位スイッチLSにより透過水タン
ク16の水位が逆浸透処理装置10よりも高くならなし
・ように透過水ポンプ18を起動停止させ自動的に透過
水の排出を可能にしており、逆浸透処理装置10の透過
水側膜面には圧力がかからなし・ように配慮されており
、したがって逆浸透処理装置10にかげられる圧力を圧
力損なしに有効に利用することが出来る。
In addition, a permeated water tank 1 is located near the reverse osmosis treatment device 10.
6 is installed, and the permeated water flows down into the permeated water tank 16 based on the head difference between the water levels of the reverse osmosis treatment device 10 and the permeated water tank 16, and the water level of the permeated water tank 16 is adjusted by the water level switch LS to the reverse osmosis treatment device 10. The permeated water pump 18 is started and stopped to automatically discharge the permeated water so that no pressure is applied to the membrane surface on the permeated water side of the reverse osmosis treatment device 10. Therefore, the pressure applied to the reverse osmosis treatment device 10 can be effectively used without pressure loss.

さらに、本実施例では第2図に図示するような電気系路
が配線されて℃・るため各運転モードは自動的に制御さ
れしたがって無人運転が可能である。
Furthermore, in this embodiment, since the electrical system lines as shown in FIG. 2 are wired at a temperature of 0.degree. C., each operation mode is automatically controlled and unmanned operation is therefore possible.

第3図は、原子カプラントから排出される放射性物質を
含む洗浄排水を用(・第1図で示す完全バッチ濃縮方式
で逆浸透処理を繰返して得られた、濃縮比(被処理排水
量/濃縮水量)と放射性物質の除去率(濃縮水下の放射
性物質の濃度/透過水中の放射性物質の濃度)との関係
を示すものであり、縦軸は放射性物質の除去率、横軸は
濃縮比を表わすものであり、第3図中の・印は58CO
、ム印は、60Co、■印は54 Mnの放射性物質を
含む洗浄排水を逆浸透処理した場合の結果を示す。
Figure 3 shows the concentration ratio (amount of wastewater to be treated/amount of concentrated water) obtained by repeating reverse osmosis treatment using the complete batch concentration method shown in Figure 1. ) and the radioactive material removal rate (radioactive material concentration in concentrated water/radioactive material concentration in permeated water), where the vertical axis represents the radioactive material removal rate and the horizontal axis represents the concentration ratio. The * mark in Figure 3 is 58CO.
, Mu marks indicate the results of reverse osmosis treatment of cleaning wastewater containing radioactive substances such as 60Co and 54Mn radioactive substances.

第3図に示されるように濃縮比が上昇するに伴ない放射
性物質の除去率は上昇しており、したがって、上記のよ
うな放射性物質を含有する排水を逆浸透処理する場合に
は、逆浸透供給水の濃度が高くなっても透過水の水質は
大幅に悪くならないことが分る。
As shown in Figure 3, the removal rate of radioactive substances increases as the concentration ratio increases. Therefore, when treating wastewater containing radioactive substances as described above, reverse osmosis It can be seen that even if the concentration of the feed water increases, the quality of the permeated water does not deteriorate significantly.

したがって、本発明に係る方法を放射性物質を含有する
洗浄排水などに用いた場合にはさらに有効な処理方法と
して適用される。
Therefore, when the method according to the present invention is used for cleaning wastewater containing radioactive substances, it is applied as a more effective treatment method.

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

第1図は従来の完全バッチ濃縮方式に適用される排水の
逆浸透処理のフローチャート、第2図は本発明方法の一
実施例のフローチャート、第3図は放射性物質を含む洗
浄排水の濃縮比と放射性物質の除去率との関係を示すも
のである。 1・・・・・・洗浄排水タンク、6・・・・・・循環タ
ンク、9・・・・・・高圧ポンプ、10・・・・・・逆
浸透処理装置、12−・・・・・冷却器。
Figure 1 is a flowchart of reverse osmosis treatment of wastewater applied to the conventional complete batch concentration method, Figure 2 is a flowchart of an embodiment of the method of the present invention, and Figure 3 is the concentration ratio of cleaning wastewater containing radioactive materials. This shows the relationship with the removal rate of radioactive substances. 1...Washing drainage tank, 6...Circulation tank, 9...High pressure pump, 10...Reverse osmosis treatment device, 12-... Cooler.

Claims (1)

【特許請求の範囲】[Claims] 1 洗浄排水タンクの下流側に設けた所定容量の循環タ
ンクに供給された被処理排水を高圧ポンプを介して逆浸
透処理装置に供給して上記排水を濃縮水と透過水とに分
離し、つし・で上記濃縮水を冷却器を通したのち上記循
環タンクへ返送する工程を繰返して濃縮を行℃・、濃縮
倍率が数十倍迄は上記排水タンクから上記排水を供給し
て上記循環タンクの水位を一定に保持して引続き濃縮を
行な(・、つし・で上記排水タンクと上記循環タンクと
の連通を断ち引続き濃縮を行なうことを特徴とする排水
の処理方法。
1. The wastewater to be treated is supplied to a circulation tank with a predetermined capacity provided downstream of the washing wastewater tank, and is supplied to a reverse osmosis treatment device via a high-pressure pump to separate the wastewater into concentrated water and permeated water. Concentration is carried out by repeating the process of passing the concentrated water through the cooler and then returning it to the circulation tank at °C. Until the concentration ratio is several tens of times, the wastewater is supplied from the wastewater tank to the circulation tank. A method for treating wastewater, characterized in that the water level of the wastewater tank is maintained at a constant level to continue concentration, and the communication between the wastewater tank and the circulation tank is cut off at .
JP11559578A 1978-09-20 1978-09-20 How to treat wastewater Expired JPS5925633B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11559578A JPS5925633B2 (en) 1978-09-20 1978-09-20 How to treat wastewater

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11559578A JPS5925633B2 (en) 1978-09-20 1978-09-20 How to treat wastewater

Publications (2)

Publication Number Publication Date
JPS5584586A JPS5584586A (en) 1980-06-25
JPS5925633B2 true JPS5925633B2 (en) 1984-06-19

Family

ID=14666492

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11559578A Expired JPS5925633B2 (en) 1978-09-20 1978-09-20 How to treat wastewater

Country Status (1)

Country Link
JP (1) JPS5925633B2 (en)

Families Citing this family (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS59155596U (en) * 1983-04-05 1984-10-18 三菱重工業株式会社 Waste liquid treatment equipment
JPS59228988A (en) * 1983-06-10 1984-12-22 Jgc Corp Method for obtaining pure water from high-conductivity water by reverse osmosis method
JPS60113598U (en) * 1984-01-10 1985-08-01 三菱重工業株式会社 Radioactive laundry wastewater treatment equipment
JPS62206498A (en) * 1986-03-05 1987-09-10 東芝プラント建設株式会社 Processor for sea water containing radioactive substance
JPH0664187B2 (en) * 1986-08-22 1994-08-22 科学技術庁原子力局長 Treatment method of radioactive waste liquid
US5096574A (en) * 1990-01-16 1992-03-17 Teledyne Industries, Inc. Reverse osmosis system
JP5048239B2 (en) * 2005-11-22 2012-10-17 株式会社マーフィード Water purifier
JP2014020962A (en) * 2012-07-19 2014-02-03 Hitachi-Ge Nuclear Energy Ltd Radioactive wastewater treatment method and treatment device for the same
JP6141610B2 (en) * 2012-09-07 2017-06-07 旭化成株式会社 Method for operating water treatment apparatus and method for producing potable water
CN106448787B (en) * 2014-01-09 2018-10-02 清华大学 A kind of method and apparatus of Spent Radioactive water process
JP7122761B2 (en) * 2017-11-06 2022-08-22 Wota株式会社 water purification system

Also Published As

Publication number Publication date
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