JP5041688B2 - Filtration filter coating method - Google Patents

Filtration filter coating method Download PDF

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JP5041688B2
JP5041688B2 JP2005226510A JP2005226510A JP5041688B2 JP 5041688 B2 JP5041688 B2 JP 5041688B2 JP 2005226510 A JP2005226510 A JP 2005226510A JP 2005226510 A JP2005226510 A JP 2005226510A JP 5041688 B2 JP5041688 B2 JP 5041688B2
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filtration
filter
membrane surface
filtration filter
primary chamber
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JP2007038159A (en
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卓尚 原田
淳 中円尾
里志 笠原
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Organo Corp
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E30/00Energy generation of nuclear origin
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E30/00Energy generation of nuclear origin
    • Y02E30/30Nuclear fission reactors

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Description

本発明は、発電プラントにおいて用いられるろ過装置におけるろ過フィルタのコーティング方法に関し、特に、原子力発電所、火力発電所の復水処理に用いられるろ過装置におけるろ過フィルタのコーティング方法に関する。 The present invention relates to a method of coating a filtration filter in the filtration apparatus used in power plants, particularly nuclear power plants relates to a coating method of the filtration filter in the filtration apparatus used in condensate treatment for thermal power plants.

原子力発電所等における復水処理設備は、被処理水である復水に含まれる酸化鉄などの懸濁物質を除去するろ過装置と、塩素イオン等のイオン状の不純物を除去する脱塩器を備えて構成されている。このうち、ろ過装置としては、近年、多数の微細孔を備えた中空糸膜をろ過膜として備えたものが多く用いられている。プリコート材を用いたフィルタでは、洗浄排液中に使用済みろ過助剤が多量に含まれ、それが放射性廃棄物処理系の負担を大きくするが、中空糸膜を用いた場合にはそのような問題がない。しかしながら、中空糸膜は、懸濁物質を直接捕捉するため、比較的粘着性の大きな酸化鉄などが、膜表面から容易に剥離せず、洗浄の度に初期差圧が上昇するという問題があった。このことに鑑み、本出願人は、剥離性のよい酸化鉄微粒子の被膜を予め膜表面に形成しておき、懸濁物質を該被膜を介して捕捉することにより、洗浄によって、捕捉した懸濁物質を被膜と共に剥離し、これにより、洗浄後の初期差圧の上昇を抑制する技術を提案している(特許文献1参照)。
特公平6−24612号公報
Condensate treatment facilities in nuclear power plants and the like are equipped with a filtration device that removes suspended substances such as iron oxide contained in the condensate that is the treated water, and a demineralizer that removes ionic impurities such as chlorine ions. It is prepared for. Among these, as a filtration apparatus, what equipped the hollow fiber membrane provided with many micropores as a filtration membrane in recent years is used a lot. In the filter using the precoat material, a large amount of used filter aid is contained in the washing effluent, which increases the burden on the radioactive waste treatment system. However, when a hollow fiber membrane is used, such a filter is used. there is no problem. However, since the hollow fiber membrane directly captures suspended substances, iron oxide, etc., which is relatively sticky, does not easily peel off from the membrane surface, and the initial differential pressure increases with each washing. It was. In view of this, the present applicant formed a coating of iron oxide fine particles with good peelability on the surface of the membrane in advance, and captured the suspended substance by washing by capturing the suspended substance through the coating. The technique which peels a substance with a film and suppresses the raise of the initial differential pressure | voltage after washing | cleaning by this is proposed (refer patent document 1).
Japanese Patent Publication No. 6-24612

酸化鉄微粒子の被膜を形成するに当たり、特許文献1では、当該酸化鉄微粒子を含む水を保持する水槽を付設し、原水流入管からろ過塔内に流入させている。特許文献1では明示されていないが、原水流入管を経てろ過塔内に流入させるためには、圧送用のポンプを配備しなければならず、そのことが構造の複雑化、コストの増加を招いていた。一方、ポンプを使用しない方法として、ろ過塔の上蓋を外して開放し、そこから酸化鉄を投入することも行われているが、発電所復水ろ過装置のように、常時運転しているろ過装置においては、上蓋を取り外すことができるタイミングが、定期点検時などに限られるという不便がある。また、上蓋を開放するための作業コストが増すと共に、原子力発電所では作業員の被爆機会も多くなる。 In forming a coating film of iron oxide fine particles, in Patent Document 1, a water tank for holding water containing the iron oxide fine particles is attached, and flows into the filtration tower from the raw water inflow pipe. Although not specified in Patent Document 1, in order to flow into the filtration tower through the raw water inflow pipe, a pump for pumping must be provided, which leads to a complicated structure and an increase in cost. It was. On the other hand, as a method that does not use a pump, the upper lid of the filtration tower is removed and opened, and iron oxide is also introduced from there. However, filtration that is always in operation like a power plant condensate filtration device. In the apparatus, there is an inconvenience that the timing at which the upper lid can be removed is limited to a periodic inspection. In addition, the work cost for opening the top cover increases, and the number of opportunities for workers to be exposed at the nuclear power plant increases.

本発明は上記に鑑みなされたものであり、ポンプを使用することなく、また、上蓋の開放作業を行うことなく、膜表面汚染防止剤を簡易な構成でろ過膜表面に付着させることができ、コストの低減を図ることができるろ過装置におけるろ過フィルタのコーティング方法を提供することを課題とする。 The present invention has been made in view of the above, and without using a pump, and without performing the opening operation of the upper lid, the membrane surface contamination preventive agent can be attached to the filtration membrane surface with a simple configuration, It aims at providing the coating method of the filtration filter in the filtration apparatus which can aim at reduction of cost.

上記課題を解決するため、請求項1記載の本発明では、ろ過塔の一次室内に配設される、被処理水中の懸濁物質を捕捉するためのろ過フィルタのろ過膜表面に、ろ過処理開始前に、予め膜表面汚染防止剤としての酸化鉄又は水酸化鉄を付着させるろ過フィルタのコーティング方法であって、前記膜表面汚染防止剤を、重力を利用して前記ろ過塔の一次室内に導入し、次いで、該一次室内に圧縮空気を導入してスクラビングし、前記ろ過フィルタのろ過膜表面に前記膜表面汚染防止剤を付着させることを特徴とするろ過フィルタのコーティング方法を提供する。
請求項2記載の本発明では、前記圧縮空気を、前記一次室に接続された洗浄用の圧縮空気導入管から導入してスクラビングすることを特徴とする請求項1記載のろ過フィルタのコーティング方法を提供する。
請求項3記載の本発明では、前記ろ過塔の一次室に接続された導入管の接続位置よりも高所に設置された汚染防止剤分散槽に保持された前記膜表面汚染防止剤を含む水を、前記導入管を介して重力を利用して前記ろ過塔の一次室内に導入することを特徴とする請求項1又は2記載のろ過フィルタのコーティング方法を提供する。
請求項4記載の本発明では、前記ろ過フィルタが中空糸膜フィルタであることを特徴とする請求項1又は2記載のろ過フィルタのコーティング方法を提供する。
請求項5記載の本発明では、前記ろ過フィルタが発電所の復水処理用に設置されたものであることを特徴とする請求項1〜4のいずれか1に記載のろ過フィルタのコーティング方法を提供する。
In order to solve the above-mentioned problems, in the present invention according to claim 1, the filtration treatment is started on the surface of the filtration membrane of the filtration filter disposed in the primary chamber of the filtration tower for capturing suspended substances in the water to be treated. Before, a method for coating a filtration filter in which iron oxide or iron hydroxide as a membrane surface contamination inhibitor is attached in advance, wherein the membrane surface contamination inhibitor is introduced into the primary chamber of the filtration tower using gravity And then, scrubbing by introducing compressed air into the primary chamber, and providing the membrane surface antifouling agent on the filtration membrane surface of the filtration filter.
According to a second aspect of the present invention, there is provided the filtration filter coating method according to the first aspect, wherein the compressed air is scrubbed by being introduced from a compressed air introduction pipe for cleaning connected to the primary chamber. provide.
In this invention of Claim 3, the water containing the said membrane | film | coat surface contamination | pollution prevention agent hold | maintained at the pollution inhibitor dispersion tank installed in the high place rather than the connection position of the introductory pipe connected to the primary chamber of the said filtration tower. The filtration filter coating method according to claim 1 or 2, wherein the filter is introduced into the primary chamber of the filtration tower using gravity through the introduction pipe.
In this invention of Claim 4, the said filtration filter is a hollow fiber membrane filter, The coating method of the filtration filter of Claim 1 or 2 characterized by the above-mentioned is provided.
In this invention of Claim 5, the said filtration filter is installed for the condensate treatment of a power plant, The coating method of the filtration filter of any one of Claims 1-4 characterized by the above-mentioned. provide.

本発明は、膜表面汚染防止剤が分散された水を保持する汚染防止剤分散槽を、ろ過塔と導入管との接続位置よりも高所に設置するなどして、膜表面汚染防止剤を重力によりろ過塔内に導入することを特徴としている。従って、膜表面汚染防止剤をろ過膜に付着させる際には、導入管を開放状態にすれば、膜表面汚染防止剤が分散された水が重力によりろ過塔の一次室内に導入される。このため、ろ過塔の上蓋を開放する必要がないことはもちろんのこと、膜表面汚染防止剤が分散された水を導入するためのポンプを設ける必要もなく、膜表面汚染防止剤を導入するための装置構成が簡素化され、その分、コストの低減に資する。また、圧縮空気を導入してスクラビングすることにより、膜表面汚染防止剤が均一に撹拌され、膜表面汚染防止剤をろ過フィルタの膜面にほぼ均等に付着させることができる。 The present invention provides a membrane surface contamination preventive agent by, for example, installing a contamination inhibitor dispersion tank holding water in which the membrane surface contamination inhibitor is dispersed at a higher position than the connection position between the filtration tower and the introduction pipe. It is characterized by being introduced into the filtration tower by gravity. Therefore, when the membrane surface contamination preventive agent is attached to the filtration membrane, the water in which the membrane surface contamination preventive agent is dispersed is introduced into the primary chamber of the filtration tower by gravity if the introduction pipe is opened. Therefore, it is not necessary to open the top lid of the filtration tower, and it is not necessary to provide a pump for introducing water in which the membrane surface contamination inhibitor is dispersed, and to introduce the membrane surface contamination inhibitor. This simplifies the apparatus configuration and contributes to the cost reduction. In addition, by introducing compressed air and scrubbing, the membrane surface contamination preventive agent is uniformly agitated, and the membrane surface contamination preventive agent can be adhered almost evenly to the membrane surface of the filtration filter.

以下、図面に示した実施形態に基づき本発明をさらに詳細に説明する。図1は、本実施形態にかかるろ過装置10が使用される発電所の処理系統の一例を示す図であり、図2は、該ろ過装置10の構造を示す図である。   Hereinafter, the present invention will be described in more detail based on embodiments shown in the drawings. FIG. 1 is a diagram illustrating an example of a processing system of a power plant in which the filtration device 10 according to the present embodiment is used, and FIG. 2 is a diagram illustrating a structure of the filtration device 10.

図1に示したように、原子炉等の蒸気発生器100で発生した蒸気は、蒸気タービン110を回転させた後、復水器120で冷却されて凝縮し、復水となる。復水は、復水ポンプ130により、復水処理設備140に送られる。復水処理設備140により処理された水は再び蒸気発生器100に送られる。このうち、復水処理設備140は、復水配管、蒸気配管等から発生する酸化鉄等の懸濁物質を除去する本実施形態のろ過装置10と、イオン状の不純物を除去する脱塩器150を備えて構成されている。   As shown in FIG. 1, the steam generated by the steam generator 100 such as a nuclear reactor rotates the steam turbine 110, is then cooled by the condenser 120, is condensed, and becomes condensate. Condensate is sent to the condensate treatment facility 140 by the condensate pump 130. The water treated by the condensate treatment facility 140 is sent to the steam generator 100 again. Among these, the condensate treatment facility 140 includes a filtration device 10 according to the present embodiment that removes suspended substances such as iron oxide generated from a condensate pipe, a steam pipe, and the like, and a demineralizer 150 that removes ionic impurities. It is configured with.

復水処理設備140において、復水中の懸濁物質を除去するために用いられる本実施形態のろ過装置10は、図2に示したように、ろ過塔20、導入管40及び汚染防止剤分散槽50とを備えて構成される。   In the condensate treatment facility 140, the filtration apparatus 10 of the present embodiment used for removing suspended substances in the condensate, as shown in FIG. 2, is a filtration tower 20, an introduction pipe 40, and a pollution inhibitor dispersion tank. 50.

ろ過塔20は、その内部に固定配設されたフィルタ固定板21を介して、被処理水が流入する一次室22と、ろ過処理された処理水が通過する二次室23とを備えている。フィルタ固定板21には、中空糸膜を用いたろ過フィルタである中空糸膜フィルタ24が多数本支持されている。具体的には、各中空糸膜フィルタ24の上端がフィルタ固定板21に固定されることにより支持されている。一次室22の下部には被処理水の流入管25が接続されており、該流入管25には再生用水流入管31が接続されている。また、二次室23の上部には中空糸膜フィルタ24を通過することによりろ過された処理水を、次工程の脱塩器150に送る流出管26が接続されている。   The filtration tower 20 includes a primary chamber 22 into which treated water flows and a secondary chamber 23 through which filtered treated water passes through a filter fixing plate 21 fixedly disposed therein. . A large number of hollow fiber membrane filters 24, which are filtration filters using hollow fiber membranes, are supported on the filter fixing plate 21. Specifically, the upper end of each hollow fiber membrane filter 24 is supported by being fixed to the filter fixing plate 21. A treated water inflow pipe 25 is connected to the lower part of the primary chamber 22, and a regeneration water inflow pipe 31 is connected to the inflow pipe 25. In addition, an outlet pipe 26 is connected to the upper part of the secondary chamber 23 to send the treated water filtered by passing through the hollow fiber membrane filter 24 to the demineralizer 150 in the next step.

ろ過塔20に形成された上記一次室22の側部には、導入口42を介して導入管40の一端が接続されている。また、この導入管40の他端は、汚染防止剤分散槽50に接続されている。これにより、導入管40を介して、汚染防止剤分散槽50内に貯留された膜表面汚染防止剤が分散された水が一次室22内に導入可能となっている。この際、本実施形態においては、汚染防止剤分散槽50を、一次室22と導入管40との接続位置よりも高所となるように配置しており、導入管40に設けた弁41を開放することにより、汚染防止剤分散槽50に貯留された上記水が、重力により一次室22内に導入される。   One end of an introduction pipe 40 is connected to a side portion of the primary chamber 22 formed in the filtration tower 20 through an introduction port 42. The other end of the introduction pipe 40 is connected to the antifouling agent dispersion tank 50. Thereby, the water in which the film surface contamination preventive agent stored in the contamination preventing agent dispersion tank 50 is dispersed can be introduced into the primary chamber 22 through the introduction pipe 40. At this time, in this embodiment, the anti-fouling agent dispersion tank 50 is disposed so as to be higher than the connection position between the primary chamber 22 and the introduction pipe 40, and the valve 41 provided on the introduction pipe 40 is provided. By opening, the water stored in the pollution inhibitor dispersion tank 50 is introduced into the primary chamber 22 by gravity.

汚染防止剤分散槽50において水に分散させる膜表面汚染防止剤としては、酸化鉄又は水酸化鉄が用いられる。酸化鉄としては、例えば、α−Fe203、α−FeOOH、Fe304等を用いることができる。酸化鉄及び水酸化鉄は、発電所の系統内で発生するもの(例えば、アモルファス、α−FeOOH、γ−FeOOH、Fe203、Fe304等)を利用することができる。発電所の系統内で発生する酸化鉄又は水酸化鉄を利用することにより、廃棄物量をより低減することができる。 As the film surface contamination inhibitor dispersed in water in the contamination inhibitor dispersion tank 50, iron oxide or iron hydroxide is used. As iron oxide , for example, α-Fe203, α-FeOOH, Fe304, or the like can be used. As the iron oxide and iron hydroxide, those generated in the power plant system (for example, amorphous, α-FeOOH, γ-FeOOH, Fe203, Fe304, etc.) can be used. By utilizing iron oxide or iron hydroxide generated in the power plant system, the amount of waste can be further reduced.

膜表面汚染防止剤を中空糸膜フィルタ24の表面にコーティングする作業は、ろ過装置10の新設時、中空糸膜フィルタ24の交換時、ろ過塔20内の水を全量抜いて行うろ過装置10の点検時、あるいは、差圧上昇による中空糸膜フィルタ24の洗浄時等において、ろ過装置10を再稼働させる際に行なう。具体的には、まず、再生用水流入管31の弁31aを開放し、ろ過塔20の一次室22内に半分程度の水を張る。あるいは、ろ過塔20内に予め水が残っている状態では、弁27aを開放し、ドレン管27から排水し、一次室22内の水位が半分程度になるようにする。次に、再生用水流入管31の弁31aあるいはドレン管27の弁27aを閉じ、導入管40の弁41を開放し、膜表面汚染防止剤が分散された水を導入する。この際、本実施形態によれば、汚染防止剤分散槽50が、導入管40とろ過塔20の一次室22との接続位置よりも高所に配設されているため、弁41を開放するだけで、重力により膜表面汚染防止剤が分散された水が一次室22内に導入される。膜表面汚染防止剤が分散された水を所定量導入したならば、弁41を閉じ、ろ過塔20の下部に接続された圧縮空気導入管28の弁28aを開放し、圧縮空気を導入してスクラビングする。これにより、膜表面汚染防止剤が均一に撹拌され、その直後の満水操作で膜表面汚染防止剤が中空糸膜フィルタ24の膜面にほぼ均等に付着し、該膜面上に膜表面汚染防止剤の被膜が形成される。   The operation of coating the surface of the hollow fiber membrane filter 24 with the membrane surface contamination preventive agent is performed when the filtration device 10 is newly installed, when the hollow fiber membrane filter 24 is replaced, and all the water in the filtration tower 20 is drained. This is performed when the filtration device 10 is restarted at the time of inspection or at the time of cleaning the hollow fiber membrane filter 24 due to an increase in differential pressure. Specifically, first, the valve 31 a of the regeneration water inflow pipe 31 is opened, and about half of the water is filled in the primary chamber 22 of the filtration tower 20. Alternatively, in a state where water remains in the filtration tower 20 in advance, the valve 27a is opened and drained from the drain pipe 27 so that the water level in the primary chamber 22 becomes about half. Next, the valve 31a of the regeneration water inflow pipe 31 or the valve 27a of the drain pipe 27 is closed, the valve 41 of the introduction pipe 40 is opened, and water in which the membrane surface contamination inhibitor is dispersed is introduced. At this time, according to the present embodiment, the pollution inhibitor dispersion tank 50 is disposed at a higher position than the connection position between the introduction pipe 40 and the primary chamber 22 of the filtration tower 20, so the valve 41 is opened. Only water in which the film surface contamination preventive agent is dispersed by gravity is introduced into the primary chamber 22. When a predetermined amount of water in which the membrane surface contamination inhibitor is dispersed is introduced, the valve 41 is closed, the valve 28a of the compressed air introduction pipe 28 connected to the lower part of the filtration tower 20 is opened, and compressed air is introduced. Scrub. As a result, the membrane surface contamination preventive agent is uniformly agitated, and the membrane surface contamination preventive agent adheres almost evenly to the membrane surface of the hollow fiber membrane filter 24 immediately after the water filling operation, preventing the membrane surface contamination on the membrane surface. A coating of agent is formed.

このような準備をしたならば、流入管25の弁25a及び流出管26の弁26aを開放状態にし、ろ過装置10の運転を開始する。流入管25から流入する被処理水は、中空糸膜フィルタ24の外側から内側へ通過するが、この際、被処理水中に含まれる酸化鉄粒子等の懸濁物質は、上記した膜表面汚染防止剤の被膜によって捕捉される。中空糸膜フィルタ24の内側に至ってろ過処理された処理水は、二次室23に流入し、さらに流出管26を経て、次工程の脱塩器150へ送られる。ろ過処理を継続することにより、差圧が上昇してきたならば、弁25a,26aを閉じ、洗浄用の圧縮空気導入管28の弁28aとベント管30の弁30aを開放して、圧縮空気を導入して洗浄する。圧縮空気により中空糸膜フィルタ24が振動し、膜表面汚染防止剤が剥離される。膜表面汚染防止剤の被膜により捕捉された懸濁物質は、膜表面汚染防止剤が剥離される際に一緒に除去されることになるため、中空糸膜フィルタ24の膜表面に残存する懸濁物質は極めて少なく、洗浄の度に初期差圧が上昇するということがない。 If such a preparation is made, the valve 25a of the inflow pipe 25 and the valve 26a of the outflow pipe 26 are opened, and the operation of the filtration device 10 is started. The treated water flowing from the inflow pipe 25 passes from the outside to the inside of the hollow fiber membrane filter 24. At this time, suspended substances such as iron oxide particles contained in the treated water prevent the above-described membrane surface contamination. Captured by coating of agent. The treated water that has been filtered through the inside of the hollow fiber membrane filter 24 flows into the secondary chamber 23, and further passes through the outflow pipe 26 and is sent to the demineralizer 150 in the next step. If the differential pressure has increased by continuing the filtration process, the valves 25a and 26a are closed, the valve 28a of the compressed air introduction pipe 28 for cleaning and the valve 30a of the vent pipe 30 are opened, and compressed air is supplied. Introduce and clean. The hollow fiber membrane filter 24 is vibrated by the compressed air, and the membrane surface contamination preventive agent is peeled off. Suspended substances captured by the coating film of the membrane surface contamination preventive agent are removed together when the membrane surface contamination preventing agent is peeled off, so that the suspension remaining on the membrane surface of the hollow fiber membrane filter 24 is removed. There is very little material and the initial differential pressure does not increase with each wash.

洗浄後、再稼働させるに当たっては、上記したように、弁41を開放し、汚染防止剤分散槽50から膜表面汚染防止剤が分散された水を導入し、再び、中空糸膜フィルタ24の膜面に膜表面汚染防止剤の被膜を形成して実施する。   In order to restart the operation after washing, as described above, the valve 41 is opened, water in which the membrane surface contamination inhibitor is dispersed is introduced from the contamination inhibitor dispersion tank 50, and the membrane of the hollow fiber membrane filter 24 is again introduced. A film of a film surface contamination inhibitor is formed on the surface.

本実施形態によれば、弁41を開放するだけで、膜表面汚染防止剤が分散された水が一次室22内に導入されるため、専用のポンプを用いる必要がなく、その分、低いコストで中空糸膜フィルタ24の表面に膜表面汚染防止剤の被膜を形成可能なろ過装置10を提供することができる。   According to this embodiment, since the water in which the membrane surface contamination preventive agent is dispersed is introduced into the primary chamber 22 simply by opening the valve 41, it is not necessary to use a dedicated pump, and the cost is reduced accordingly. Thus, it is possible to provide the filtration device 10 capable of forming a membrane surface antifouling agent film on the surface of the hollow fiber membrane filter 24.

なお、上記実施形態では、膜表面汚染防止剤を導入するための導入管40を、導入口42を介し、ろ過塔20の一次室22に直接接続しているが、例えば、一次室22に予め接続されているベント管30に分岐口30bを設け、該分岐口30bに導入管40を接続するようにしてもよい。また、上記実施形態では、導入管40の他端に汚染防止剤分散槽50を接続しているが、このような専用の水槽(汚染防止剤分散槽50)を設けるのではなく、例えば、漏斗状器具を導入管40の他端に一時的に接続し、別途に調製した膜表面汚染防止剤が分散された水を、該漏斗状器具を介して導入することも可能である。もちろん、この場合も、漏斗状器具は、導入管40とろ過塔20との接続位置よりも高所に配置し、重力を利用して導入する。   In the above-described embodiment, the introduction pipe 40 for introducing the film surface contamination preventing agent is directly connected to the primary chamber 22 of the filtration tower 20 via the introduction port 42. A branch port 30b may be provided in the connected vent pipe 30, and the introduction pipe 40 may be connected to the branch port 30b. Moreover, in the said embodiment, although the pollution inhibitor dispersion tank 50 is connected to the other end of the introduction pipe 40, such a dedicated water tank (pollution prevention agent dispersion tank 50) is not provided, for example, a funnel, for example. It is also possible to temporarily connect a water-like device to the other end of the introduction tube 40 and introduce the water in which the separately prepared membrane surface contamination inhibitor is dispersed through the funnel-like device. Of course, also in this case, the funnel-shaped instrument is arranged at a higher position than the connection position between the introduction tube 40 and the filtration tower 20 and is introduced by using gravity.

また、上記説明では、膜表面汚染防止剤により中空糸膜フィルタ24の膜表面のコーティング作業を行った後、導入管40を接続したままで通常運転に切り替えているが、コーティング作業終了後は、導入管40を取り外し、導入口42を閉じてから、あるいは、ベント管30の分岐口30bに接続した場合には該分岐口30bを閉じてから、通常運転に切り替えることが好ましい。   Further, in the above description, after performing the coating operation of the membrane surface of the hollow fiber membrane filter 24 with the membrane surface contamination inhibitor, the operation is switched to the normal operation while the introduction pipe 40 is connected. It is preferable to switch to the normal operation after removing the introduction pipe 40 and closing the introduction opening 42, or when the branch pipe 30b is closed when connected to the branch opening 30b of the vent pipe 30.

図1は、本発明の一の実施形態にかかるろ過装置を用いた発電所の水処理系統の一例を示す図である。Drawing 1 is a figure showing an example of the water treatment system of the power plant using the filtration device concerning one embodiment of the present invention. 図2は、上記実施形態にかかるろ過装置の概略構造を示す図である。FIG. 2 is a diagram illustrating a schematic structure of the filtration device according to the embodiment.

符号の説明Explanation of symbols

10 ろ過装置
20 ろ過塔
22 一次室
23 二次室
24 中空糸膜フィルタ
25 流入管
26 流出管
40 導入管
50 汚染防止剤分散槽
DESCRIPTION OF SYMBOLS 10 Filtration apparatus 20 Filtration tower 22 Primary chamber 23 Secondary chamber 24 Hollow fiber membrane filter 25 Inflow pipe 26 Outflow pipe 40 Introduction pipe 50 Antifouling agent dispersion tank

Claims (5)

ろ過塔の一次室内に配設される、被処理水中の懸濁物質を捕捉するためのろ過フィルタのろ過膜表面に、ろ過処理開始前に、予め膜表面汚染防止剤としての酸化鉄又は水酸化鉄を付着させるろ過フィルタのコーティング方法であって、
前記膜表面汚染防止剤を、重力を利用して前記ろ過塔の一次室内に導入し、次いで、該一次室内に圧縮空気を導入してスクラビングし、前記ろ過フィルタのろ過膜表面に前記膜表面汚染防止剤を付着させることを特徴とするろ過フィルタのコーティング方法。
Prior to the start of the filtration treatment, iron oxide or hydroxide as a membrane surface contamination inhibitor is previously placed on the filtration membrane surface of the filtration filter for capturing suspended substances in the water to be treated, which is disposed in the primary chamber of the filtration tower. A method of coating a filtration filter for attaching iron,
The membrane surface contamination inhibitor is introduced into the primary chamber of the filtration tower using gravity, and then scrubbed by introducing compressed air into the primary chamber, and the membrane surface contamination on the filtration membrane surface of the filtration filter. A method for coating a filtration filter, comprising attaching an inhibitor.
前記圧縮空気を、前記一次室に接続された洗浄用の圧縮空気導入管から導入してスクラビングすることを特徴とする請求項1記載のろ過フィルタのコーティング方法。 The method for coating a filtration filter according to claim 1, wherein the compressed air is scrubbed by being introduced from a compressed air introduction pipe for cleaning connected to the primary chamber. 前記ろ過塔の一次室に接続された導入管の接続位置よりも高所に設置された汚染防止剤分散槽に保持された前記膜表面汚染防止剤を含む水を、前記導入管を介して重力を利用して前記ろ過塔の一次室内に導入することを特徴とする請求項1又は2記載のろ過フィルタのコーティング方法。   Gravity of water containing the membrane surface antifouling agent held in the antifouling agent dispersion tank installed at a location higher than the connection position of the introduction pipe connected to the primary chamber of the filtration tower through the introduction pipe. The filtration filter coating method according to claim 1, wherein the filtration filter is introduced into a primary chamber of the filtration tower by using a filter. 前記ろ過フィルタが中空糸膜フィルタであることを特徴とする請求項1又は2記載のろ過フィルタのコーティング方法。   The method for coating a filtration filter according to claim 1 or 2, wherein the filtration filter is a hollow fiber membrane filter. 前記ろ過フィルタが発電所の復水処理用に設置されたものであることを特徴とする請求項1〜4のいずれか1に記載のろ過フィルタのコーティング方法。   The said filtration filter is installed for the condensate treatment of a power plant, The coating method of the filtration filter of any one of Claims 1-4 characterized by the above-mentioned.
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