JPH05200383A - Auxiliary type filtrating and desalting device - Google Patents

Auxiliary type filtrating and desalting device

Info

Publication number
JPH05200383A
JPH05200383A JP1074492A JP1074492A JPH05200383A JP H05200383 A JPH05200383 A JP H05200383A JP 1074492 A JP1074492 A JP 1074492A JP 1074492 A JP1074492 A JP 1074492A JP H05200383 A JPH05200383 A JP H05200383A
Authority
JP
Japan
Prior art keywords
water
tower
filter
desalting
valve
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
JP1074492A
Other languages
Japanese (ja)
Inventor
Yoshihiro Shiozawa
義博 塩沢
Seiichi Numazaki
誠一 沼崎
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Hitachi Engineering Co Ltd
Hitachi Ltd
Original Assignee
Hitachi Engineering Co Ltd
Hitachi Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Hitachi Engineering Co Ltd, Hitachi Ltd filed Critical Hitachi Engineering Co Ltd
Priority to JP1074492A priority Critical patent/JPH05200383A/en
Publication of JPH05200383A publication Critical patent/JPH05200383A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To prevent organic impurities from being introduced from an equipment in which powdery ion exchange resin is used by providing a system for discharging the water held in a tower to a waste disposal equipment from a filtrating and desalting tower, supplying raw water not less than the amount of water held in the tower before passing water to perform replacement of water in the tower, draining the water held in the tower and thereafter passing water. CONSTITUTION:A system is provided to a waste disposal system from the outlet pipeline of a filtrating and desalting tower. After the filtrating and desalting tower 20 is back-washed and precoated, an outlet valve 22, an inlet valve 23 of precoat, an outlet valve 24 of precoat, a drain valve 25 of backwash and a vent valve 26 of backwash are closed. An inlet valve 21 is opened and the pressure of the system is exerted. While keeping a stand-by state for holding a precoat layer in a state wherein a holding pump 27 is operated, a valve 31 for replacing water held in the tower is opened to extrude and replace the water held in the tower by raw water. Thereby, organic impurities eluted from resin, fiber such as nylon cut off from a fiber element and the additive of precoat material are discharged to the outside of the system.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、ろ過エレメント表面に
ろ過助材をプリコートし、助材ろ過層に水を透過させ、
ろ過エレメント内部からろ過水を抜き、ろ過脱塩を行う
ろ過エレメントを多数設置した助材型ろ過脱塩装置にお
いて、特に、イオン交換樹脂から溶出する有機性不純
物,繊維エレメントからの繊維不純物及びプリコート材
の添加剤等を系外に排出し、処理水の純度を高める助材
型ろ過脱塩装置に関する。
BACKGROUND OF THE INVENTION The present invention is to pre-coat a filter aid on the surface of a filter element to allow water to pass through the filter layer of the aid,
In an auxiliary material type filter desalting device in which a large number of filter elements are installed to remove the filter water from the inside of the filter element to perform filter desalting, particularly, organic impurities eluted from the ion exchange resin, fiber impurities from the fiber element and precoat material. The present invention relates to an auxiliary material type filter desalting apparatus which enhances the purity of treated water by discharging the additives and the like of the above.

【0002】[0002]

【従来の技術】原子力発電所(BWR)の復水浄化系及
び炉水浄化系の水処理系統を図に示す。本図において原
子炉1で発生した蒸気(約290℃、約70kg/cm2
は蒸気管2を経てタービン3を回転駆動し発電を行い、
その後復水器4で凝縮され復水になる。復水器4からの
復水は管5によって導かれ復水ポンプ6により復水ろ過
脱塩装置7に送られる。復水ろ過脱塩装置7では、プラ
ント内で発生するクラッド(クラッドとは腐食生成物が
主体で通常、0.45μm のミリポアフィルタを通過し
ない微細な懸濁物の総称で主成分はFe23,Fe34
等である。)及び核種イオンを円筒形ろ過エレメントに
陽イオン及び陰イオンの粉末イオン交換樹脂を特定割合
で混合した樹脂を均等に数mm厚みに外径面にプリコート
した樹脂層でろ過脱塩して復水の浄化を行う。復水ろ過
脱塩装置7で浄化された水は、次に復水脱塩装置8に送
られ、復水脱塩塔内に陰及び陽イオンの粒状イオン交換
樹脂を積んだ樹脂層によって、復水ろ過脱塩装置7で除
去されなかった残留クラッド及び核種イオンが捕捉脱塩
される。復水脱塩装置8を経た浄化水は、復水昇圧ポン
プ9を経て低圧給水加熱器10で加熱されて給水ポンプ
11により高圧給水加熱器12へ送られ、再び、高圧で
加熱されて原子炉1へ戻る。
2. Description of the Related Art A water treatment system of a condensate purification system and a reactor water purification system of a nuclear power plant (BWR) is shown in the figure. In this figure, steam generated in the reactor 1 (about 290 ° C, about 70kg / cm 2 )
Drives the turbine 3 via the steam pipe 2 to generate electricity,
After that, it is condensed in the condenser 4 and becomes condensed water. Condensed water from the condenser 4 is guided by a pipe 5 and sent to a condensate filtration desalination apparatus 7 by a condensate pump 6. In condensate filter demineralizer device 7, the main component in the general term of the cladding (usually corrosion products and clad with mainly fine suspension that does not pass through the 0.45μm Millipore filter generated in the plant Fe 2 O 3 , Fe 3 O 4
Etc. ) And nuclide ions are mixed in a cylindrical filter element with powdered ion-exchange resin of cation and anion at a specific ratio, and the resin layer is pre-coated evenly on the outer diameter surface with a thickness of several mm to desalinate. To purify. The water purified by the condensate filtration desalination apparatus 7 is then sent to the condensate deionization apparatus 8 and reconstituted by a resin layer containing granular ion exchange resins of anions and cations in the condensate deionization tower. Residual cladding and nuclide ions that have not been removed by the water filtration desalination apparatus 7 are captured and desalted. The purified water that has passed through the condensate demineralizer 8 is heated by the low-pressure feed water heater 10 through the condensate booster pump 9 and is sent to the high-pressure feed water heater 12 by the feed water pump 11, and is heated again at high pressure and then the nuclear reactor. Return to 1.

【0003】このように原子炉1で発生した蒸気はター
ビン3を駆動した後、復水浄化して、原子炉1に戻すの
で復水浄化系を常時循環していることになる。一方、原
子炉1の炉水は炉水浄化系配管15を経てポンプ16に
より炉水浄化系ろ過脱塩装置17,炉水浄化系脱塩装置
18(非設置のプラントもある)へ送られて、浄化され
た後、再び、原子炉へ戻るように構成されている。炉水
浄化系ろ過脱塩装置17の構造は復水ろ過脱塩装置7と
同一で炉水を循環させてろ過脱塩し、浄化するようにな
っている。
Thus, the steam generated in the reactor 1 drives the turbine 3 and then purifies the condensate and returns it to the reactor 1. Therefore, the steam is constantly circulated in the condensate purification system. On the other hand, the reactor water of the nuclear reactor 1 is sent to the reactor water purification system filtration desalination apparatus 17 and the reactor water purification system desalination apparatus 18 (some plants are not installed) through a reactor water purification system pipe 15 by a pump 16. After being cleaned, it is configured to return to the reactor again. The structure of the reactor water purification system filter desalting device 17 is the same as that of the condensate water filter desalting device 7, and is designed to circulate the reactor water for filter desalting and purification.

【0004】ここで、復水ろ過脱塩装置7,炉水浄化系
ろ過脱塩装置17は、上述のように、粉末状の陽イオン
交換樹脂をある比率で混合し、ナイロン繊維又は多孔の
ステンレス製のエレメント上にろ過面積1m2 あたり約
1kgの樹脂をプリコートしたものを内蔵している。プリ
コートの際には、樹脂層の均一化を図るために、アクリ
ル酸系の薬品添加を行ったり、低濃度スラリによるプリ
コートを行う。プリコート操作後、ろ過脱塩器内に原水
を流入して処理を開始する。図3は、通常のろ過脱塩装
置概略系統を示す。ろ過脱塩装置は、複数のろ過脱塩塔
20からなり、各ろ過脱塩塔20をパラレルに使用して
処理を行っている。復水を処理するにつれて、プリコー
ト層に復水中のクラッドが捕獲され、それに伴ってろ過
圧力が急激に上昇する。通常ろ過圧力が約2kg/cm2
後になると、そのろ過脱塩塔20は処理を停止し、エレ
メントを逆洗する。そして、再びエレメントに新しい樹
脂をプリコートし、処理を再開する。しかし、粉末樹脂
の場合には、逆洗によってエレメントから除去された樹
脂は、その再生が困難なために、一回のみの使用で廃棄
されるのが一般的である。
Here, the condensate filtration desalination apparatus 7 and the reactor water purification system filtration desalination apparatus 17 are mixed with a powdery cation exchange resin at a certain ratio as described above, and are made of nylon fiber or porous stainless steel. Built-in pre-coated with about 1 kg of resin per 1 m 2 of filtration area on the manufactured element. At the time of precoating, in order to make the resin layer uniform, acrylic acid-based chemicals are added, or precoating with a low-concentration slurry is performed. After the precoating operation, raw water is introduced into the filter desalting device to start the treatment. FIG. 3 shows a schematic system of a normal filtration desalination apparatus. The filter desalting apparatus is composed of a plurality of filter desalting towers 20, and the filter desalting towers 20 are used in parallel for processing. As the condensate is treated, the clad in the condensate is captured in the precoat layer, and the filtration pressure rapidly increases accordingly. Normally, when the filtration pressure reaches about 2 kg / cm 2 , the filtration desalting tower 20 stops the treatment and backwashes the element. Then, the element is again precoated with a new resin, and the process is restarted. However, in the case of powdered resin, the resin removed from the element by backwashing is generally difficult to regenerate, and therefore it is generally discarded after only one use.

【0005】ここで、ろ過脱塩塔20及び復水脱塩塔3
5に装荷される樹脂からは、図4に示すように有機性不
純物(全有機炭素TOC)が溶出する傾向がある。この
有機性不純物は、C−SO3 H等であり、これらが原子
炉に流入すると熱分解してSO4 2-等になり炉水導電率
を変動させる要因となる。
[0005] Here, the filter desalting tower 20 and the condensate demineralizing tower 3
Organic impurities (total organic carbon TOC) tend to be eluted from the resin loaded in No. 5 as shown in FIG. The organic impurity is C-SO 3 H and the like, becomes a factor to which they vary the result reactor water conductivity in the flowing into the reactor pyrolyzed SO 4 2-like.

【0006】この樹脂からの有機性不純物の原子炉流入
防止対策として従来は、樹脂量が多く、有機性不純物発
生量の多い復水脱塩塔35について実施されている。図
5は、復水脱塩塔35を保管した場合の塔内のTOC濃
度の一例を示したものであるが、脱塩塔を保管した場
合、塔内に保有の樹脂からTOCが溶出し、塔内TOC
濃度が上昇、約30日後には、2000mg/m3 程度と
なる。脱塩塔1塔がこの濃度となった状態で通水し、原
子炉にTOCが流入した場合、炉水の硫酸根(S
4 2- )は、約3〜5mg/lになると予想される。この
ため脱塩塔35では、通水前に塔内に保有されている水
を系外に排出した後通水するようにしている。図6は、
脱塩塔廻りの構成を示すものである。塔内保有水のドレ
ンは、廃棄物処理設備への弁36を開き、圧縮空気の弁
37を開くことにより塔内保有水をドレンする。この
時、全量ドレンすると樹脂層に空気が混入するため、樹
脂層表面までドレンし、廃棄物処理設備への弁36及び
圧縮空気の弁37を閉じた後、補給水設備からの弁38
を開いて脱塩塔35を満水とする。このドレン,満水の
操作を数回(通常3〜5回)繰返し行うことにより塔内
保有水と共に樹脂より溶出した不純物を系外に排出す
る。
As a countermeasure for preventing the inflow of organic impurities from the resin into the reactor, the condensate demineralization tower 35, which has a large amount of resin and a large amount of organic impurities, is conventionally used. FIG. 5 shows an example of TOC concentration in the tower when the condensate demineralization tower 35 is stored, but when the demineralization tower is stored, TOC is eluted from the resin held in the tower, TOC in the tower
The concentration increases, and after about 30 days, it becomes about 2000 mg / m 3 . When water is passed through one desalting tower at this concentration and TOC flows into the reactor, the sulfate radicals (S
O 4 2− ) is expected to be about 3-5 mg / l. For this reason, in the desalting tower 35, the water held in the tower is discharged to the outside of the system before passing water. Figure 6
It shows the structure around the desalting tower. The drain of the retained water in the tower drains the retained water in the tower by opening the valve 36 to the waste treatment facility and opening the valve 37 of the compressed air. At this time, if the entire amount is drained, air will be mixed into the resin layer, so the resin layer surface will be drained, and after closing the valve 36 to the waste treatment facility and the valve 37 for compressed air, the valve 38 from the makeup water facility is closed.
Is opened to fill the desalting tower 35 with water. By repeating this operation of drainage and full water several times (usually 3 to 5 times), impurities eluted from the resin are discharged out of the system together with the water retained in the tower.

【0007】ここで、従来は、樹脂量の多い復水脱塩塔
35のみ有機性不純物の除去操作が考慮されていたが、
その他の粉末樹脂等を保有する復水ろ過脱塩装置7,炉
水浄化系ろ過脱塩装置17では、この操作が考慮されて
いないばかりでなく有機性不純物の系外への排出系統も
考慮されていなかった。また、エレメント材質としてナ
イロン繊維,ポリプロピレン繊維等を使用していること
による繊維の流出に伴う原子炉内での熱分解による影
響,プリコート型ろ過脱塩塔の粉末イオン交換樹脂の適
正フロック形成用に使用されるにアクリル酸系の共重合
体である添加剤も水質変動の要因となることからこれら
に流出対策も必要であった。
Here, conventionally, only the condensate demineralizing tower 35 having a large amount of resin has been considered to remove the organic impurities.
In the condensate filtration desalination apparatus 7 and the reactor water purification system filtration desalination apparatus 17 that have other powdered resins, not only this operation is not taken into consideration, but also the discharge system of organic impurities out of the system is taken into consideration. I didn't. In addition, due to the fact that nylon fibers, polypropylene fibers, etc. are used as the element material, the effect of thermal decomposition in the nuclear reactor due to the outflow of fibers, and for the proper floc formation of the powder ion exchange resin in the precoat type filter desalting tower. Additives, which are acrylic acid type copolymers used, also cause water quality fluctuations, and therefore, measures against spillage were also necessary for these.

【0008】なお、この種の装置として関連するものに
は、例えば特開平3−31799号公報が上げられる。
A related device of this type is disclosed in, for example, Japanese Patent Laid-Open No. 3-31799.

【0009】[0009]

【発明が解決しようとする課題】最近の原子力発電所で
は、原子炉内の高純度水質維持の要求があり、水質変動
を与える要因を排除するようにしている。この従来技術
は、樹脂から溶出する有機性不純物(TOC等)を考慮
し、樹脂量の多い復水脱塩装置のみを対象としていた
が、原子炉へ供給される系統には、粉末イオン交換樹脂
及び繊維エレメント等の有機性不純物等が流出する可能
性のある設備である復水ろ過脱塩装置,炉水浄化系ろ過
脱塩装置については、この設備からの有機性不純物等が
原子炉で熱分解した場合の硫酸根,アンモニア,アクリ
ル酸による水質変動について、その量が少ないこともあ
り考慮されていなかった。
In recent nuclear power plants, there is a demand for maintaining high-purity water quality in nuclear reactors, and the factors that cause fluctuations in water quality are eliminated. This prior art was intended only for the condensate demineralizer with a large amount of resin in consideration of organic impurities (TOC, etc.) eluted from the resin, but the system supplied to the reactor has a powder ion exchange resin. Also, regarding condensate filtration desalination equipment and reactor water purification system filtration desalination equipment, which are equipments where organic impurities such as fiber elements may flow out, the organic impurities etc. from this equipment heats up in the reactor. The water quality change due to sulfate, ammonia, and acrylic acid when decomposed was not taken into consideration due to the small amount.

【0010】本発明の目的は、近年の原子炉水の高純度
水質要求を満足すべく原子炉水質の変動要因を排除する
ため復水ろ過脱塩装置,炉水材浄化系ろ過脱塩装置のよ
うに粉末イオン交換樹脂を使用する設備からの有機性不
純物等の系統内への流入を防止するための系統設備構成
と運用方法である。
An object of the present invention is to provide a condensate filtration desalination system and a reactor water material purification system filtration desalination system in order to eliminate the factors of fluctuations in the reactor water quality in order to satisfy recent requirements for high-purity water quality of reactor water. Thus, it is a system equipment configuration and operation method for preventing the inflow of organic impurities and the like from the equipment using the powder ion exchange resin into the system.

【0011】[0011]

【課題を解決するための手段】本発明は、粉末イオン交
換樹脂をプリコートするプリコート型ろ過脱塩装置にお
いて、原子力発電所の一次冷却水(復水,原子炉水)処
理する際の通水前にろ過脱塩塔内の有機性不純物(TO
C)を含む保有水を系統外に排出した後、通水すること
を特徴とする助材型ろ過脱塩装置である。
The present invention relates to a precoat type filter desalting apparatus for precoating a powder ion exchange resin, before the passage of water when processing primary cooling water (condensate water, reactor water) of a nuclear power plant. In addition, organic impurities (TO
It is an auxiliary material type filter desalination apparatus, characterized in that the stored water containing C) is discharged to the outside of the system and then passed through.

【0012】このろ過脱塩塔内の有機性不純物(TO
C)を含む保有水を系統外に排出する手段として廃棄物
処理設備への系統を設け、粉末イオン交換樹脂のプリコ
ート樹脂層を剥離させないために原水(復水,原子炉水
等)または、補給水設備からの補給水(この場合は、新
たに補給水設備からの供給系統を設置する。)を連続供
給するとともに連続ドレンし、塔内の水を置換すること
により有機性不純物を含む保有水を系統外に排出する。
この場合の原水または補給水の供給量は、塔内保有水量
以上とする。
Organic impurities (TO
A system to the waste treatment facility is provided as a means for discharging the retained water containing C) to the outside of the system, and raw water (condensate water, reactor water, etc.) or replenishment is provided to prevent the precoat resin layer of the powder ion exchange resin from peeling Retained water containing organic impurities by continuously supplying makeup water from the water facility (in this case, newly installing a supply system from the makeup water facility) and continuously draining it to replace the water in the tower. Is discharged to the outside of the grid.
In this case, the amount of raw water or make-up water supplied should be at least the amount of water held in the tower.

【0013】[0013]

【作用】ろ過脱塩塔は、原水を通水することによりエレ
メントにプリコートされた粉末イオン交換樹脂が、クラ
ッド成分,イオン成分を吸着する。このろ過脱塩塔がプ
プラント定期検査時、予備塔運用時等樹脂をプリコート
した状態で満水保管されると樹脂から有機性不純物が溶
出し、塔内に保有される。また、逆洗・プリコートされ
新規にプリコートされた新品粉末イオン交換樹脂からも
有機性不純物が溶出するとともに、適切なフロック形成
用としてアクリル酸系(CH2CHCOOH )の添加剤が加えら
れており、樹脂に吸着されないで残ったアクリル酸が塔
内に保有される。エレメントについてもナイロン繊維を
使用している場合があり、このナイロン繊維の一部切れ
る等して塔内に浮遊する。これらが通水により系統内に
流出すると原子炉内に持ち込まれ、熱分解等により硫酸
根,アンモニア,スルホン酸となり原子炉水の水質変動
要因となる。
In the filter desalting tower, the powder ion-exchange resin precoated on the element by passing the raw water adsorbs the clad component and the ionic component. When this filter desalting tower is stored in a state where the resin is pre-coated, such as during a plant regular inspection and during a preliminary tower operation, organic impurities are eluted from the resin and are retained in the tower. In addition, organic impurities are eluted from the newly powdered ion-exchange resin that has been backwashed and pre-coated and newly pre-coated, and an acrylic acid (CH 2 CHCOOH) additive has been added for proper floc formation. The acrylic acid remaining without being adsorbed by the resin is retained in the tower. Nylon fibers may also be used for the elements, and some of the nylon fibers are cut off and float in the tower. When these flow out into the system due to water flow, they are brought into the reactor, where they are converted to sulfate, ammonia, and sulfonic acid due to thermal decomposition, etc., and become a factor that affects the water quality of the reactor water.

【0014】このため、ろ過脱塩塔通水前に塔内保有水
を系外の廃棄物処理設備等に排出する系統を設け原水
(復水,原子炉水)または補給水(この場合は、新たに
補給水設備からの供給系統を設置する)で塔内の水を置
換する運用を行うことにより樹脂,エレメント,添加剤
等からの有機性不純物を原子炉一次冷却水(復水,原子
炉水)系統外に排出できるので、原子炉水の水質変動要
因を排除できる。
For this reason, a system for discharging the water contained in the tower to a waste treatment facility outside the system is provided before passing through the filter desalting tower, and raw water (condensate, reactor water) or makeup water (in this case, A new supply system from the makeup water facility is installed to replace the water in the tower to remove organic impurities from the resin, elements, additives, etc. to the reactor primary cooling water (condensate, reactor). Water), which can be discharged outside the system, can eliminate the factors that affect the water quality of reactor water.

【0015】[0015]

【実施例】以下に本発明の実施例を具体的に説明する。EXAMPLES Examples of the present invention will be specifically described below.

【0016】前述の技術的内容は変わることは無い。つ
まり、原子炉一次冷却水を処理する装置として復水ろ過
脱塩装置7,復水脱塩装置8,炉水材浄化系ろ過脱塩装
置17,炉水浄化系脱塩装置18があり、これらにより
復水,原子炉水の浄化を行っている。
The above technical contents do not change. That is, there are a condensate filtration desalination device 7, a condensate deionization device 8, a reactor water purification system filtration desalination device 17, and a reactor water purification system desalination device 18 as devices for treating the reactor primary cooling water. The condensate and the reactor water are purified by.

【0017】ここで、これらの装置に装荷される樹脂
は、下記の構造をしており、水中では、このうちのスル
ホン基(−SO3H )が溶出する。
Here, the resin loaded in these devices has the following structure, and the sulfo group (--SO 3 H) among them is eluted in water.

【0018】[0018]

【化1】 [Chemical 1]

【0019】このスルホン基が原子炉内に流入すると熱
分解して硫酸根(SO4 2- )が生成される。同様にエレ
メントに使用されているナイロン繊維は、ジアミン(N
2(CH2)mNH2)と炭素数nの二塩基酸(HOOC(C
2)n-2COOH)の重縮合物で、これが原子炉で分解
されるとアンモニア(NH4OH ),硝酸根(NO3 -
等が生成されることが考えられる。また、プリコート材
の添加剤として使用されるアクリル酸(CH2CHCO
OH )系の薬品も原子炉へ流入すると導電率を変動さ
せる。
When this sulfone group flows into the nuclear reactor, it is thermally decomposed to generate sulfate radicals (SO 4 2− ). Similarly, the nylon fiber used for the element is diamine (N
H 2 (CH 2 ) mNH 2 ) and a dibasic acid having a carbon number of n (HOOC (C
H 2) polycondensates of n-2 COOH), when it is decomposed in the reactor ammonia (NH 4 OH), nitrate (NO 3 -)
It is possible that In addition, acrylic acid (CH 2 CHCO) used as an additive for the precoat material
OH) type chemicals also change the conductivity when they flow into the reactor.

【0020】以上のようなことからろ過脱塩装置でも通
水前に塔内保有水のドレン,水置換が必要である。
From the above, even in the filter desalting apparatus, it is necessary to drain the water held in the tower and replace it with water before passing water.

【0021】図1は、塔内保有水を系外に排出する系統
を設けたろ過脱塩装置の系統図を示す。原水の処理方
法,プリコート方法等は、従来技術と替わることはな
い。
FIG. 1 shows a system diagram of a filtration desalination apparatus provided with a system for discharging the water retained in the tower to the outside of the system. The method of treating raw water, the method of pre-coating, etc. are not replaced with the conventional technology.

【0022】ここで、従来と相違する点は、ろ過脱塩塔
出口配管より廃棄物処理系への系統を設置したことにあ
る。ろ過脱塩塔20を逆洗・プリコート後は、出口弁2
2,プリコート入口弁23,プリコート出口弁24,逆
洗ドレン弁25,逆洗ベント弁26を閉じ、入口弁21
を開いて系統の圧力を加えたまま保持ポンプ27を運転
した状態でプリコート層を保持する。この状態から通水
する場合は、通常出口弁22を開くが、本発明では、こ
の通水前に塔内の水置換を行なうことにある。つまり、
入口弁21を開いたまま塔内保有水置換弁31を開き、
塔内保有水を原水により押出し置換する。この時、原水
は、通水状態と同様にエレメントの外側から内側に流れ
るようにしてプリコート層が剥離しないようにし、塔内
保有水量以上(約1.3 倍以上)の原水を供給するよう
にする。
Here, the point different from the conventional one is that a system is installed from the outlet pipe of the filter desalting tower to the waste treatment system. After backwashing and precoating the filter desalting tower 20, the outlet valve 2
2, the precoat inlet valve 23, the precoat outlet valve 24, the backwash drain valve 25, and the backwash vent valve 26 are closed, and the inlet valve 21
Is opened to hold the precoat layer while the holding pump 27 is operated with the system pressure applied. When water is passed from this state, the outlet valve 22 is normally opened, but in the present invention, the water in the tower is replaced before this water is passed. That is,
With the inlet valve 21 open, open the water replacement valve 31 in the tower,
The water held in the tower is extruded and replaced by raw water. At this time, the raw water is made to flow from the outside to the inside of the element to prevent the precoat layer from peeling off, as in the case of flowing water, and to supply the raw water in an amount equal to or more than the water content in the tower (about 1.3 times or more). To do.

【0023】本発明は、ろ過脱塩塔20より廃棄物処理
設備に排出する系統を設け、通水前に塔内保有水量以上
の原水を供給して塔内の水を置換し、塔保有水をドレン
した後、通水することにより樹脂より溶出する有機性不
純物,繊維エレメントから切れる等したナイロン繊維,
プリコート材の添加剤等が系統外に排出されるため、こ
れらがろ過脱塩塔20の通水と共に原子炉一次冷却水に
混入して原子炉1に流入することがなくなり、この結果
として原子炉水水質変動を抑制することができる。
According to the present invention, a system for discharging from the filter desalting tower 20 to the waste treatment facility is provided, and raw water in an amount equal to or more than the amount of water held in the tower is supplied to replace the water in the tower with water before passing water. After draining the water, organic impurities eluted from the resin by passing water, nylon fiber cut from the fiber element,
Since the additives and the like of the precoat material are discharged to the outside of the system, they are not mixed into the reactor primary cooling water together with the water flow of the filter desalting tower 20 and flow into the reactor 1, and as a result, Water quality fluctuation can be suppressed.

【0024】図7は、本発明の応用例であり、ろ過脱塩
塔保有水を排出するに当たりその排出系統を逆洗受タン
クに排出するようにしたものである。つまり、塔内保有
水置換弁31の出口を逆洗ドレン配管に接続し、塔内保
有水を逆洗受タンクに一時受入た後、廃棄物処理設備に
排出する。
FIG. 7 is an application example of the present invention, in which the discharge system for discharging water held in the filter desalting tower is discharged to a backwash receiving tank. That is, the outlet of the tower internal water replacement valve 31 is connected to the backwash drain pipe, and the tower internal water is temporarily received in the backwash receiving tank and then discharged to the waste treatment facility.

【0025】図8,図9は、図1,図7で説明のろ過脱
塩塔内保有水を置換するための水を補給水としたもので
ある。つまり、入口弁21とろ過脱塩塔20の間に補給
水設備からの補給水供給系統を設け、塔内保有水の水置
換時入口弁21を閉じた後、補給水供給弁32を開き、
塔内に補給水を供給,塔内保有水置換弁31より廃棄物
処理設備へ塔内保有水を排出するものである。
FIGS. 8 and 9 show that make-up water is used to replace the water held in the filter desalting tower described in FIGS. 1 and 7. That is, a make-up water supply system from a make-up water facility is provided between the inlet valve 21 and the filter desalting tower 20, the inlet valve 21 is closed when the water held in the tower is replaced with water, and then the make-up water supply valve 32 is opened.
Make-up water is supplied to the inside of the tower, and the held water in the tower is discharged from the held water replacement valve 31 to the waste treatment facility.

【0026】[0026]

【発明の効果】本発明によれば、復水ろ過脱塩装置,炉
水浄化系ろ過脱塩装置等のろ過脱塩塔より塔内保有水を
廃棄物処理設備に排出する系統を設け、通水前に塔内保
有水量以上の原水または補給水を供給して塔内の水置換
を行ない、塔内保有水をドレンした後通水することによ
り樹脂より溶出する有機性不純物,繊維エレメントから
切れる等したナイロン等の繊維,プリコート材の添加剤
等が系統外に排出されるため、これらがろ過脱塩塔の通
水と共に原子炉一次冷却水に混入して原子炉に流入する
ことがなくなり、この結果として原子炉水水質変動を抑
制することができる。
According to the present invention, a system for discharging the retained water in the tower to the waste treatment facility from the filter desalting tower such as the condensate filtration desalination apparatus and the reactor water purification system filtration desalination apparatus is provided. The raw water or makeup water that exceeds the amount of water in the tower is supplied before water to replace the water in the tower, drain the water in the tower, and then pass water to cut off organic impurities and fiber elements eluted from the resin. Since such fibers such as nylon, additives of precoat material, etc. are discharged to the outside of the system, they will not be mixed with the primary cooling water of the reactor together with the water passing through the filter desalting tower and flow into the reactor. As a result, fluctuations in water quality of reactor water can be suppressed.

【図面の簡単な説明】[Brief description of drawings]

【図1】ろ過脱塩塔保有水の廃棄物処理設備へのドレン
系統を設けたろ過脱塩装置の系統図。
FIG. 1 is a system diagram of a filtration desalination apparatus provided with a drain system to a waste treatment facility for water held in a filtration desalination tower.

【図2】沸騰水型原子力発電所の系統図。FIG. 2 is a system diagram of a boiling water nuclear power plant.

【図3】ろ過脱塩装置の系統図。FIG. 3 is a system diagram of a filter desalting apparatus.

【図4】樹脂の全有機炭素(TOC)の溶出速度と浸漬
日数の関係の説明図。
FIG. 4 is an explanatory diagram of a relationship between the elution rate of total organic carbon (TOC) of a resin and the number of immersion days.

【図5】脱塩塔の保管日数と全有機炭素(TOC)量の
関係の説明図。
FIG. 5 is an explanatory diagram of the relationship between the number of days of storage in the desalting tower and the amount of total organic carbon (TOC).

【図6】脱塩塔廻りの系統図。FIG. 6 is a system diagram around a desalting tower.

【図7】ろ過脱塩塔保有水を逆洗受タンクにドレンする
系統を設けたろ過脱塩装置の系統図。
FIG. 7 is a system diagram of a filtration desalination apparatus provided with a system for draining the water retained in the filtration desalination tower to a backwash receiving tank.

【図8】ろ過脱塩塔保有水置換のために補給水設備から
の供給系統を設けると共に廃棄物処理設備へのドレン系
統を設けたろ過脱塩装置の系統図。
FIG. 8 is a system diagram of a filtration desalination apparatus in which a supply system from a makeup water facility is provided to replace the water held in the filtration desalination tower and a drain system is provided to a waste treatment facility.

【図9】ろ過脱塩塔保有水置換のために補給水設備から
の供給系統を設けると共に逆洗受タンクにドレンする系
統を設けたろ過脱塩装置の系統図。
FIG. 9 is a system diagram of a filtration desalination apparatus in which a system for supplying water from a makeup water facility is provided for replacing the water held in the filtration desalination tower and a system for draining to a backwash tank.

【符号の説明】[Explanation of symbols]

20…ろ過脱塩塔、21…入口弁、22…出口弁、23
…プリコート入口弁、24…プリコート出口弁、25…
逆洗ドレン弁、26…逆洗ベント弁、27…保持ポン
プ、29…プリコートタンク、30…逆洗受タンク。
20 ... Filtration desalting tower, 21 ... Inlet valve, 22 ... Outlet valve, 23
… Precoat inlet valve, 24… Precoat outlet valve, 25…
Backwash drain valve, 26 ... Backwash vent valve, 27 ... Holding pump, 29 ... Precoat tank, 30 ... Backwash receiving tank.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】表面にろ過助材をプリコートし、助材ろ過
層に原水を透過させ、ろ過エレメント内部からろ過水を
抜きろ過脱塩を行うろ過エレメントを多数設置し、ろ過
助材として粉末イオン交換樹脂を使用する助材型ろ過脱
塩装置において、通水を行う前に塔内保有水を原水を用
いて系外に排出した後、通水をすることを特徴とする助
材型ろ過脱塩装置。
1. A filter aid is pre-coated on the surface, raw water is allowed to permeate through the aid filter layer, and a large number of filter elements for removing filtered water from the inside of the filter element to perform desalination are installed, and powder ions are used as the filter aid. In an auxiliary material type filter desalination apparatus using an exchange resin, the auxiliary material type filter desalination apparatus is characterized in that the water held in the tower is discharged to the outside of the system using raw water before water is passed. Salt equipment.
【請求項2】請求項1において、ろ過脱塩塔内保有水を
系外に排出するためにろ過脱塩塔出口側から廃棄物処理
設備に排出する系統を設けた助材型ろ過脱塩装置。
2. The auxiliary material type filter desalination apparatus according to claim 1, wherein a system is provided for discharging the retained water in the filter desalination tower to the outside of the system to the waste treatment facility from the outlet side of the filter desalination tower. .
【請求項3】請求項1において、ろ過脱塩塔内保有水を
系外に排出するためにろ過脱塩塔出口側から逆洗受タン
クへの系統を設け、塔内保有水を逆洗受タンクを経由し
て廃棄物処理設備に排出する助材型ろ過脱塩装置。
3. The system according to claim 1, wherein a system from the outlet side of the filter desalting tower to the backwash receiving tank is provided to discharge the water retained in the filter desalting tower to the outside of the system, and the water retained in the tower is backwashed. An auxiliary material type filter desalination device that discharges waste to a waste treatment facility via a tank.
【請求項4】請求項1,2または3において、ろ過脱塩
塔内保有水を系外に排出するためろ過脱塩塔入口側に補
給水を供給する系統を設け、補給水を用いて塔内保有水
を系外へ排出する助材型ろ過脱塩装置。
4. The tower according to claim 1, 2 or 3, wherein a system for supplying make-up water is provided on the inlet side of the filter desalting tower in order to discharge the retained water in the filter desalting tower to the outside of the system. An auxiliary material type filter desalination device that discharges the water held inside the system.
JP1074492A 1992-01-24 1992-01-24 Auxiliary type filtrating and desalting device Pending JPH05200383A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1074492A JPH05200383A (en) 1992-01-24 1992-01-24 Auxiliary type filtrating and desalting device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1074492A JPH05200383A (en) 1992-01-24 1992-01-24 Auxiliary type filtrating and desalting device

Publications (1)

Publication Number Publication Date
JPH05200383A true JPH05200383A (en) 1993-08-10

Family

ID=11758821

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1074492A Pending JPH05200383A (en) 1992-01-24 1992-01-24 Auxiliary type filtrating and desalting device

Country Status (1)

Country Link
JP (1) JPH05200383A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001327813A (en) * 2000-05-22 2001-11-27 Japan Organo Co Ltd Regeneration equipment of filtering desalting device

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001327813A (en) * 2000-05-22 2001-11-27 Japan Organo Co Ltd Regeneration equipment of filtering desalting device

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