JP2514933B2 - Method for cleaning hollow fiber modules - Google Patents
Method for cleaning hollow fiber modulesInfo
- Publication number
- JP2514933B2 JP2514933B2 JP61133760A JP13376086A JP2514933B2 JP 2514933 B2 JP2514933 B2 JP 2514933B2 JP 61133760 A JP61133760 A JP 61133760A JP 13376086 A JP13376086 A JP 13376086A JP 2514933 B2 JP2514933 B2 JP 2514933B2
- Authority
- JP
- Japan
- Prior art keywords
- hollow fiber
- cleaning
- iron oxide
- fiber module
- hydrogen peroxide
- 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 - Lifetime
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D65/00—Accessories or auxiliary operations, in general, for separation processes or apparatus using semi-permeable membranes
- B01D65/02—Membrane cleaning or sterilisation ; Membrane regeneration
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2321/00—Details relating to membrane cleaning, regeneration, sterilization or to the prevention of fouling
- B01D2321/16—Use of chemical agents
- B01D2321/168—Use of other chemical agents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2321/00—Details relating to membrane cleaning, regeneration, sterilization or to the prevention of fouling
- B01D2321/18—Use of gases
- B01D2321/185—Aeration
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2321/00—Details relating to membrane cleaning, regeneration, sterilization or to the prevention of fouling
- B01D2321/20—By influencing the flow
- B01D2321/2033—By influencing the flow dynamically
- B01D2321/2058—By influencing the flow dynamically by vibration of the membrane, e.g. with an actuator
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Description
【発明の詳細な説明】 〈産業上の利用分野〉 本発明は火力発電所、原子力発電所等の復水中に含ま
れる酸化鉄に起因するクラッドを除去するために設置さ
れる中空糸モジュールを用いる濾過塔において、当該濾
過処理の続行により中空糸モジュールが前記酸化鉄で汚
染された際の洗浄方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION <Industrial field of application> The present invention uses a hollow fiber module installed to remove a clad due to iron oxide contained in condensate of a thermal power plant, a nuclear power plant or the like. The present invention relates to a method for cleaning a hollow fiber module in a filtration tower when the hollow fiber module is contaminated with the iron oxide by continuing the filtration process.
〈従来の技術〉 火力発電所あるいは原子力発電所等の復水の処理方法
として、近年になって中空糸モジュールを用いた濾過塔
でまず復水中の酸化鉄に起因するクラッドを除去し、次
いで当該濾過水をカチオン交換樹脂とアニオン交換樹脂
の混床で処理して不純物イオンを除去する復水処理方法
が提案されている。<Prior art> As a method of treating condensate in a thermal power plant or a nuclear power plant, in recent years, a clad caused by iron oxide in condensate was first removed with a filtration tower using a hollow fiber module, and then A condensate treatment method has been proposed in which filtered water is treated with a mixed bed of a cation exchange resin and an anion exchange resin to remove impurity ions.
当該中空糸モジュールを用いた濾過塔をさらに詳しく
説明すると、微細孔を多数有する中空糸を多数本束ねて
中空糸モジュールを形成し、当該中空糸モジュールの多
数本を濾過塔内に装着したもので、当該各中空糸の外側
から内側へ、復水を通過させて各中空糸の外側で酸化鉄
を濾過し、内側から得る濾過水を集合して濾過塔から流
出させる外圧型濾過が主流を占めている。Explaining in more detail a filtration tower using the hollow fiber module, a hollow fiber module is formed by bundling a large number of hollow fibers having a large number of fine pores, and a large number of the hollow fiber modules are mounted in the filtration tower. External pressure type filtration, in which condensate is passed from the outside of each hollow fiber to filter iron oxide on the outside of each hollow fiber and the filtered water obtained from the inside is collected and discharged from the filtration tower, occupies the main stream. ing.
このような濾過の続行により濾過塔の差圧が上昇した
際に、濾過塔内に水を満たしたまま各中空糸モジュール
の下方から空気等の気体を流入し、各中空糸モジュール
内部に気泡を流入して各中空糸を当該気泡によって振動
させるいわゆるバブリング工程や、当該バブリング工程
を実施した後、必要に応じ濾過塔内の上方に存在する濾
過水を各中空糸の内側から外側に逆流させる逆洗を行っ
て中空糸から酸化鉄を剥離し、酸化鉄を多量に含む洗浄
排液を得る洗浄を行い、当該洗浄と前記濾過を順次繰り
返して処理を行うものである。When the differential pressure of the filtration tower rises due to the continuation of such filtration, a gas such as air is introduced from below each hollow fiber module while the inside of the filtration tower is filled with water, and air bubbles are generated inside each hollow fiber module. A so-called bubbling step in which each hollow fiber flows in and vibrates each hollow fiber by the bubbles, or after performing the bubbling step, the filtered water existing above in the filtration tower is allowed to flow backward from the inside of each hollow fiber to the outside, if necessary. Washing is performed to remove iron oxide from the hollow fiber, washing is performed to obtain a washing drainage liquid containing a large amount of iron oxide, and the washing and the filtration are sequentially repeated to perform the treatment.
以上説明したごとく中空糸モジュールを用いる濾過塔
は、復水を各中空糸で直接濾過するので、従来から行わ
れている微粉末状イオン交換樹脂等の濾過助剤を用いる
プレコート式濾過塔と比較して、洗浄排液中に含まれる
固形物量が極めて少量であり、特に沸騰水型原子力発電
所の復水のごとく、放射性物質を含む酸化鉄の除去に適
している。As described above, since the filter tower using the hollow fiber module directly filters the condensate with each hollow fiber, it is compared with the pre-coated filter tower using the filter aid such as the conventional fine powder ion exchange resin. In addition, the amount of solids contained in the cleaning effluent is extremely small, and it is particularly suitable for removing iron oxide containing radioactive substances like condensate of a boiling water nuclear power plant.
すなわちプレコート式濾過塔の場合は、その洗浄の際
に濾過により除去した酸化鉄とともに、当該酸化鉄より
圧倒的多量の使用済プレコート剤をも含む洗浄排液が排
出されるが、中空糸モジュールを用いる濾過塔における
洗浄排液には、このような使用済プレコート剤が一切含
まれることがないので、放射性廃棄物処理の対象となる
固形物が著しく低減できるという利点を有している。That is, in the case of a precoating type filtration tower, the cleaning wastewater containing an overwhelmingly large amount of the used precoating agent than the iron oxide is discharged together with the iron oxide removed by filtration during the cleaning. Since the cleaning drainage in the filtration tower to be used does not contain such a used precoating agent at all, it has an advantage that the solid matter to be treated for radioactive waste can be significantly reduced.
〈発明が解決しようとする問題点〉 上述したような中空糸モジュールを用いる濾過塔で比
較的長期間復水の処理を行うと、前記バブリング工程や
逆洗を実施しても、差圧がもとの状態に戻らなくなるこ
とがある。<Problems to be Solved by the Invention> When the condensate is treated for a relatively long time in the filtration tower using the hollow fiber module as described above, even if the bubbling step or the backwashing is performed, the pressure difference is increased It may not return to the state.
この原因は膜面に強固に付着した少量の酸化鉄が前記
バブリング工程や逆洗を実施しても除去されず、中空糸
の膜面に残留し、これがしだいに蓄積するためである。The reason for this is that a small amount of iron oxide strongly adhered to the membrane surface is not removed even after the bubbling step or backwash, but remains on the membrane surface of the hollow fiber, and gradually accumulates.
したがってかかる状態、すなわち酸化鉄で汚染された
中空糸モジュールを適当な洗浄薬液で洗浄して当該酸化
鉄を除去しないかぎり、当該中空糸モジュールを再び用
いることができない。Therefore, the hollow fiber module cannot be used again unless the iron oxide is contaminated by such a state, that is, the hollow fiber module contaminated with iron oxide is washed with an appropriate cleaning chemical solution.
このような酸化鉄で汚染された中空糸モジュールを、
ハイドロサルファイトのような還元剤溶液あるいは蓚酸
溶液、クエン酸溶液のような還元性を有する酸やキレー
ト性を有する酸等の薬液で洗浄すれば、膜面に強固に付
着した酸化鉄と言えどもこれを溶解して除去することが
できる。A hollow fiber module contaminated with iron oxide
If it is washed with a reducing agent solution such as hydrosulfite, an oxalic acid solution, or a chemical solution such as a reducing acid or a chelating acid such as a citric acid solution, iron oxide firmly adhered to the film surface It can be dissolved and removed.
しかしながら沸騰水型原子力発電所の復水のごとく放
射性物質を含む酸化鉄の除去を対象とした中空糸モジュ
ールを用いる濾過塔においては、前述の薬液による洗浄
排液は放射性廃棄物処理の対象となり、当該洗浄排液中
に含まれる還元剤や酸を中和して生ずる塩等が放射性廃
棄物処理の際の固形物を増加させるという点で好ましく
ない。However, in a filtration tower that uses a hollow fiber module intended for the removal of iron oxide containing radioactive substances like condensate of boiling water nuclear power plants, the cleaning wastewater with the aforementioned chemical solution is the target of radioactive waste treatment, The reducing agent contained in the cleaning drainage, the salt produced by neutralizing the acid, and the like are not preferable in that they increase the solid matter in the radioactive waste treatment.
したがって中空糸の膜面に強固に付着している酸化鉄
を効果的に除去するとともに、しかも、その洗浄排液中
に当該除去した酸化鉄以外の固形物を増加させないよう
な洗浄方法の確立が要望されている。Therefore, it is possible to establish a cleaning method that effectively removes iron oxide strongly adhered to the membrane surface of the hollow fiber and does not increase solids other than the removed iron oxide in the cleaning drainage liquid. Is requested.
本発明は中空糸モジュールを用いる濾過塔におけるか
かる問題点に鑑みてなされたものであり、その目的とす
るところは前記バブリング工程や逆洗を行っても容易に
剥離できないような、中空糸の膜面に強固に付着してい
る酸化鉄を効果的に除去できるとともに、しかもその洗
浄排液中に酸化鉄以外の固形物を増加させることがない
中空糸モジュールの洗浄方法を提供するところにある。The present invention has been made in view of such problems in a filtration tower using a hollow fiber module, and an object thereof is a hollow fiber membrane that cannot be easily peeled off even after the bubbling step or backwashing. It is an object of the present invention to provide a method for cleaning a hollow fiber module, which is capable of effectively removing iron oxide strongly adhered to the surface and does not increase solid matters other than iron oxide in the cleaning drainage liquid.
〈問題点を解決するための手段〉 本発明者等は酸化鉄で汚染された中空糸モジュールの
洗浄について種々の実験を行ったところ、当該汚染され
た中空糸モジュールを過酸化水素溶液あるいはオゾン溶
液に接触させた後、前記バブリング工程を実施したとこ
ろ中空糸の膜面に強固に付着した酸化鉄が容易に除去で
きることを知見した。<Means for Solving Problems> The inventors of the present invention conducted various experiments for cleaning the hollow fiber module contaminated with iron oxide, and found that the contaminated hollow fiber module was treated with a hydrogen peroxide solution or an ozone solution. It was found that the iron oxide strongly adhered to the membrane surface of the hollow fiber can be easily removed by carrying out the bubbling step after contacting with the iron oxide.
また当該洗浄により排出される洗浄排水中の残留過酸
化水素やオゾンは加熱処理あるいは紫外線照射によって
容易に分解することができ、塩類を全く増加させないこ
とをも知見した。It was also found that the residual hydrogen peroxide and ozone in the cleaning waste water discharged by the cleaning can be easily decomposed by heat treatment or ultraviolet irradiation and do not increase salts at all.
本発明はかかる知見に基づくもので、微細孔を多数有
する中空糸を多数本束ねて中空糸モジュールを形成し、
当該中空糸モジュールの多数本を濾過塔内に横設した仕
切板の下部に垂設した構成よりなる濾過塔で、酸化鉄を
含む復水を各中空糸の外側から内側に通流する濾過処理
をすることにより、酸化鉄で汚染された中空糸モジュー
ルを洗浄するにあたり、各中空糸モジュールを過酸化水
素溶液またはオゾン溶液に接触させ、しかる後に各中空
糸モジュールの下方から空気等の気体を流入することに
より発生する気泡によって各中空糸モジュール内の各中
空糸を気泡によって振動させて各中空糸の膜面から酸化
鉄を剥離除去することを特徴とするものであり、また当
該洗浄によって発生する洗浄排液を加熱あるいは紫外線
照射して当該排液中の過酸化水素またはオゾンを分解除
去するものである。The present invention is based on such knowledge, to form a hollow fiber module by bundling a large number of hollow fibers having a large number of fine pores,
A filtration tower comprising a configuration in which a large number of the hollow fiber modules are vertically installed at the lower part of a partition plate horizontally installed in the filtration tower, and a condensate containing iron oxide is passed through the hollow fibers from the outside to the inside. By cleaning the hollow fiber modules contaminated with iron oxide, the hollow fiber modules are brought into contact with a hydrogen peroxide solution or an ozone solution, and then a gas such as air flows in from below the hollow fiber modules. It is characterized by vibrating each hollow fiber in each hollow fiber module by the air bubbles generated by doing so to remove iron oxide from the membrane surface of each hollow fiber by peeling and removing it. The cleaning effluent is heated or irradiated with ultraviolet rays to decompose and remove hydrogen peroxide or ozone in the effluent.
〈作用〉 以下に本発明を詳細に説明する。<Operation> The present invention will be described in detail below.
本発明は従来から行われている還元剤や還元性を有す
る酸やキレート性を有する酸を用いて、中空糸の膜面に
強固に付着している酸化鉄を溶解させて除去するもので
なく、中空糸モジュールに過酸化水素溶液やオゾン溶液
を接触させることにより、当該酸化鉄を気泡振動によっ
て容易に剥離できる形態に変形するところにあり、この
点が従来の洗浄方法と全く相違するところである。The present invention does not remove the iron oxide firmly adhering to the membrane surface of the hollow fiber by dissolving it by using a reducing agent, a reducing acid or a chelating acid that has been conventionally used. By contacting the hollow fiber module with a hydrogen peroxide solution or an ozone solution, the iron oxide is transformed into a form that can be easily peeled off by bubble vibration, which is completely different from the conventional cleaning method. .
膜面に強固に付着している酸化鉄を過酸化水素溶液や
オゾン溶液に接触させると、いかなる理由により容易に
膜面から剥離できるような形態に変形するのか今のとこ
ろ明らかではないが、後述する実施例で示すごとく膜面
に強固に付着した酸化鉄は過酸化水素溶液やオゾン溶液
を接触すると剥離しやすくなるのは事実であり、本発明
の効果は確実に達成できる。It is not clear yet why iron oxide strongly adhered to the film surface is transformed into a form that can be easily peeled from the film surface when brought into contact with a hydrogen peroxide solution or an ozone solution. It is a fact that iron oxide strongly adhered to the film surface easily peels off when contacted with a hydrogen peroxide solution or an ozone solution, as shown in Examples, and the effect of the present invention can be reliably achieved.
本発明に用いる過酸化水素溶液またはオゾン溶液の濃
度は少なくとも1%以上とする必要があり、これ以下の
濃度では酸化鉄の剥離効果が小さく好ましくない。また
5%以上の高濃度としても剥離効果はそれ程上昇せず、
いたずらに処理コストを上昇させるだけなので、過酸化
水素溶液またはオゾン溶液の濃度は1〜5%(重量%)
の範囲とすることが望ましい。The concentration of the hydrogen peroxide solution or ozone solution used in the present invention needs to be at least 1% or more, and if the concentration is less than this, the iron oxide peeling effect is small, which is not preferable. Moreover, even if the concentration is higher than 5%, the peeling effect does not increase so much,
The concentration of the hydrogen peroxide solution or the ozone solution is 1 to 5% (wt%) because it only unnecessarily increases the processing cost.
It is desirable to set the range to.
また過酸化水素溶液またはオゾン溶液の中空糸モジュ
ールに対する接触時間は、少なくとも10時間以上とする
ことが必要であり、これより短い接触時間では酸化鉄の
剥離効果が小さく好ましくない。また接触時間が30時間
以内で酸化鉄の剥離効果が平衡に達するので、接触時間
としては10〜30時間の範囲とすることが望ましい。Further, the contact time of the hydrogen peroxide solution or the ozone solution with the hollow fiber module needs to be at least 10 hours or more, and a contact time shorter than this is not preferable because the iron oxide peeling effect is small. Further, since the peeling effect of iron oxide reaches equilibrium within a contact time of 30 hours, the contact time is preferably in the range of 10 to 30 hours.
本発明は酸化鉄で汚染された中空糸モジュールを、濾
過塔内あるいは濾過塔外で過酸化水素溶液あるいはオゾ
ン溶液に接触させ、しかる後に中空糸モジュールの各中
空糸を気泡によって振動させることにより、各中空糸の
膜面から酸化鉄を剥離するものであるが、以下に本発明
の実施態様を説明する。The present invention, by contacting a hollow fiber module contaminated with iron oxide with a hydrogen peroxide solution or an ozone solution inside or outside the filtration tower, and then vibrating each hollow fiber of the hollow fiber module by bubbles, The iron oxide is peeled off from the membrane surface of each hollow fiber, and an embodiment of the present invention will be described below.
図面は外圧型中空糸モジュールを用いる濾過塔および
洗浄槽のフローを示す説明図であり、濾過塔1は当該濾
過塔1内に横設した仕切板2に多数の中空糸モジュール
3を垂設したものである。当該中空糸モジュール3は本
願出願人が先に開示した特願昭59−273579に示したごと
く、多数の中空糸を、各中空糸の上端部を開口するとと
もに、その下端部を閉塞して束ねたものであり、また各
中空糸モジュール3の下端にスカート部4を有し、ディ
ストリビュータ5から発生する気泡を当該スカート部4
で受け、そして当該気泡を各中空糸の外表面に通過させ
るための貫通口を当該モジュール3の下端部に有するも
のである。当該濾過塔1において復水を濾過する場合
は、濾過塔1の下部に付設した流入管6から復水を流入
し、復水を各中空糸モジュール3の前記貫通口、あるい
は側部から各中空糸モジュール3内に導入して、各中空
糸の外側で酸化鉄を濾過し、各中空糸内側の濾過水を前
記仕切板2の上方で集合し、濾過水を流出管7から流出
する。このような濾過の続行により圧力損失が増加した
場合、以下のバブリング工程を行う。The drawing is an explanatory view showing the flow of a filtration tower and a washing tank using an external pressure type hollow fiber module. In the filtration tower 1, a large number of hollow fiber modules 3 are hung vertically on a partition plate 2 provided inside the filtration tower 1. It is a thing. As shown in Japanese Patent Application No. 59-273579 previously disclosed by the applicant of the present invention, the hollow fiber module 3 bundles a large number of hollow fibers by opening the upper ends of the hollow fibers and closing the lower ends thereof. In addition, each hollow fiber module 3 has a skirt portion 4 at the lower end thereof so that air bubbles generated from the distributor 5 can be prevented.
At the lower end of the module 3 for receiving the air bubbles and passing the bubbles to the outer surface of each hollow fiber. When the condensate is filtered in the filtration tower 1, the condensate is introduced from the inflow pipe 6 attached to the lower part of the filtration tower 1, and the condensate is discharged from the through holes or the side portions of each hollow fiber module 3 into each hollow. It is introduced into the thread module 3, the iron oxide is filtered outside each hollow fiber, the filtered water inside each hollow fiber is collected above the partition plate 2, and the filtered water flows out from the outflow pipe 7. When the pressure loss increases due to the continuation of such filtration, the following bubbling step is performed.
すなわち通水を中断し、濾過塔1の仕切板2の下部に
流入復水を、また仕切板2の上方に濾過水を満たしたま
ま、空気流入管8Aから空気を流入する。当該空気はディ
ストリビュータ5から気泡状となって上昇し、当該上昇
した気泡は前述した各中空糸モジュール3のスカート部
4を介して下端に設けた貫通口から各中空糸モジュール
3の内部に流入し、各中空糸を振動させ、各中空糸の外
側の膜面に付着している酸化鉄を剥離させる。なお当該
気泡は各中空糸モジュール3の上側部から放出させ、つ
いで濾過塔1の上側部に付設した空気抜き管17から流出
させる。That is, the water flow is interrupted, and condensate flows into the lower part of the partition plate 2 of the filtration tower 1 and air flows into the upper part of the partition plate 2 from the air inflow pipe 8A while being filled with the filtered water. The air rises in the form of bubbles from the distributor 5, and the raised bubbles flow into the inside of each hollow fiber module 3 through the through holes provided at the lower ends through the skirt portion 4 of each hollow fiber module 3 described above. , Each hollow fiber is vibrated, and the iron oxide adhering to the outer membrane surface of each hollow fiber is peeled off. The bubbles are discharged from the upper part of each hollow fiber module 3 and then discharged from the air vent pipe 17 attached to the upper part of the filtration tower 1.
このような各中空糸の気泡による振動を充分に行った
後、多量の酸化鉄を含む洗浄排液をブロー管9より流出
し、洗浄排液槽10で一旦受け、また沸騰水型原子力発電
所の復水処理の場合は、当該槽10内の洗浄排液を放射性
廃棄物処理系へと移送する。After sufficiently vibrating each hollow fiber by the bubbles, the cleaning waste liquid containing a large amount of iron oxide flows out from the blow pipe 9 and is once received in the cleaning waste liquid tank 10, and the boiling water nuclear power plant In the case of the condensate treatment, the cleaning effluent in the tank 10 is transferred to the radioactive waste treatment system.
このようなバブリング工程を行った後、あるいはバブ
リング工程の後に必要に応じ逆洗を行った後、再び前述
した濾過を続行するが、当該濾過とバブリング工程等を
繰り返すことにより、各中空糸の膜面に酸化鉄が強固に
付着し、前述の洗浄では圧力損失がそれ程回復せず、濾
過処理に障害を与えるような状態となった際に以下の本
発明による洗浄を行う。After performing such a bubbling step, or after backwashing if necessary after the bubbling step, the above-described filtration is continued again, but by repeating the filtration and the bubbling step, the membrane of each hollow fiber can be obtained. When iron oxide is strongly adhered to the surface and the pressure loss is not recovered so much in the above-mentioned cleaning and the filtration process is impaired, the following cleaning according to the present invention is performed.
すなわち濾過塔1の上部鏡板11を取り外し、各中空糸
モジュール3を垂設したまま、仕切板2を濾過塔外部へ
持ち上げ、洗浄槽12内に装着する。That is, the upper end plate 11 of the filtration tower 1 is removed, and the partition plates 2 are lifted to the outside of the filtration tower and mounted in the cleaning tank 12 while the hollow fiber modules 3 are vertically installed.
次いで薬液槽13であらかじめ調整した1〜5%(重量
%)の過酸化水素溶液をポンプ14を駆動させて洗浄槽12
の下方部から流入させ、各中空糸を通過させた過酸化水
素溶液を仕切板2の上方で集水し、オーバーフローする
過酸化水素溶液を薬液槽13に循環させる。Next, the cleaning tank 12 is driven by driving the pump 14 with a 1 to 5% (wt%) hydrogen peroxide solution which has been adjusted in advance in the chemical solution tank 13.
The hydrogen peroxide solution that has flowed in from the lower part of the above and passed through each hollow fiber is collected above the partition plate 2, and the overflowing hydrogen peroxide solution is circulated in the chemical solution tank 13.
なお本発明においては中空糸モジュール3に過酸化水
素溶液を接触させればよいので、場合によっては洗浄槽
12内に過酸化水素溶液を満たしたのち、ポンプ14の駆動
を中断してもよい。また15は過酸化水素溶液を加熱する
ために設けた熱交換器であり、後述する過酸化水素の分
解時以外は当該熱交換器15に蒸気16等の熱媒体を流入さ
せない。In the present invention, it is sufficient to bring the hydrogen peroxide solution into contact with the hollow fiber module 3.
The drive of the pump 14 may be interrupted after the hydrogen peroxide solution is filled in the inside 12. Further, 15 is a heat exchanger provided for heating the hydrogen peroxide solution, and a heat medium such as steam 16 does not flow into the heat exchanger 15 except when the hydrogen peroxide is decomposed as described later.
以上のような循環あるいは浸漬を10〜30時間行って、
各中空糸を充分に過酸化水素溶液に接触させた後、熱交
換器15に熱媒体として蒸気16を流入するとともに、ポン
プ14を駆動し、過酸化水素溶液を80℃前後に加熱しなが
ら循環する。Circulate or soak for 10 to 30 hours as above,
After sufficiently bringing each hollow fiber into contact with the hydrogen peroxide solution, the steam 16 flows into the heat exchanger 15 as a heat medium, and the pump 14 is driven to circulate while heating the hydrogen peroxide solution to about 80 ° C. To do.
当該加熱循環により、過酸化水素はしだいに分解さ
れ、当該過酸化水素の分解が終了した時点で、加熱循環
を中止し、洗浄槽12から各中空糸モジュール3を垂設し
たまま仕切板2を持ち上げ、濾過塔1内に装着し、次い
で上部鏡板11を取り付ける。しかる後に仕切板2の下方
に純水、濾過水あるいは原水である復水を満たし、空気
流入管8Aから空気を流入する。当該空気の流入により、
前述したと同様に、ディストリビュータ5から気泡が上
昇し、当該気泡は各中空糸モジュール3の内部へ流入
し、各中空糸を振動させ、前述の過酸化水素溶液の接触
により膜面から剥離しやすくなった酸化鉄を剥離する。The hydrogen peroxide is gradually decomposed by the heating circulation, and when the decomposition of the hydrogen peroxide is completed, the heating circulation is stopped and the partition plate 2 is installed while the hollow fiber modules 3 are suspended from the cleaning tank 12. It is lifted and mounted in the filtration tower 1, and then the upper end plate 11 is attached. Thereafter, the partition plate 2 is filled with pure water, filtered water, or condensate, which is raw water, below the partition plate 2, and air is introduced from the air inflow pipe 8A. Due to the inflow of the air,
In the same manner as described above, bubbles rise from the distributor 5, the bubbles flow into the inside of each hollow fiber module 3, vibrate each hollow fiber, and are easily separated from the membrane surface by the contact with the hydrogen peroxide solution. Remove the iron oxide that has become.
次いで必要に応じ空気流入管8Bあるいは他の配管から
濾過塔1の仕切板2の上部に濾過水あるいは純水を圧入
し、当該水を各中空糸の内側から外側へ逆流させ、酸化
鉄を含む洗浄排液をブロー管9より流出し、洗浄排液槽
10に受ける。Next, if necessary, filtered water or pure water is press-fitted into the upper part of the partition plate 2 of the filtration tower 1 from the air inflow pipe 8B or another pipe, and the water is caused to flow backward from the inside to the outside of each hollow fiber to contain iron oxide. The cleaning drainage liquid flows out from the blow pipe 9, and the cleaning drainage tank
Get to 10.
なお沸騰水型原子力発電所の復水処理の場合は薬品槽
13内の過酸化水素が分解された洗浄排液および洗浄排液
槽10内の酸化鉄を含む洗浄排液を放射性廃棄物処理系へ
と移送する。A chemical tank for condensate treatment at boiling water nuclear power plants
A cleaning waste solution in which hydrogen peroxide in 13 is decomposed and a cleaning waste solution containing iron oxide in the cleaning waste solution tank 10 are transferred to a radioactive waste treatment system.
図面に示した実施態様においては、通常の洗浄では剥
離できない膜面に強固に付着した酸化鉄を除去する際
に、各中空糸モジュール3を濾過塔1から取り出し、別
に設けた洗浄槽12を用いたが、当該洗浄槽12の設置を省
略し、各中空糸モジュール3を濾過塔1内に装着したま
ま過酸化水素溶液を濾過塔1内に供給して、各中空糸モ
ジュール3に過酸化水素溶液を接触させても差し支えな
い。In the embodiment shown in the drawings, each hollow fiber module 3 is taken out from the filtration tower 1 and a separately provided cleaning tank 12 is used to remove iron oxide strongly adhered to the membrane surface that cannot be removed by normal cleaning. However, the installation of the washing tank 12 is omitted, and the hydrogen peroxide solution is supplied into the filtration tower 1 while the hollow fiber modules 3 are mounted in the filtration tower 1 to supply the hydrogen peroxide to the hollow fiber modules 3. It does not matter if the solution is contacted.
また過酸化水素溶液に変えて1〜5%(重量%)のオ
ゾン溶液を用いても同様の効果を奏し、また洗浄排液中
の過酸化水素あるいはオゾンを分解する場合、加熱の他
に波長260nm前後の紫外線の照射によっても同様に達成
できる。The same effect can be obtained by using a 1-5% (wt%) ozone solution instead of the hydrogen peroxide solution, and when decomposing hydrogen peroxide or ozone in the cleaning effluent, in addition to heating, the wavelength The same can be achieved by irradiation with ultraviolet rays around 260 nm.
〈効果〉 以上詳述したごとく、本発明によれば単なる気泡の振
動あるいは気体、水等の逆流では容易に剥離できないよ
うな、中空糸の膜面に強固に付着した酸化鉄を、容易に
剥離させることができる。<Effect> As described in detail above, according to the present invention, the iron oxide firmly adhered to the membrane surface of the hollow fiber, which cannot be easily separated by the mere vibration of bubbles or the reverse flow of gas, water, etc., can be easily separated. Can be made.
また本発明の洗浄方法は還元剤や酸等の固形物を増加
させるような薬剤を一切用いることがなく、かつ洗浄に
よって排出される洗浄排液中の過酸化水素またはオゾン
を加熱あるいは紫外線照射によって分解することができ
るので、当該分解処理においても固形物を増加させるこ
とがない。Further, the cleaning method of the present invention does not use any chemicals such as reducing agents and acids that increase solids, and hydrogen peroxide or ozone in the cleaning effluent discharged by cleaning is heated or irradiated with ultraviolet rays. Since it can be decomposed, solid matter is not increased even in the decomposition treatment.
したがって本発明の洗浄方法は、沸騰水型原子力発電
所のように、当該洗浄排液をさらに放射性廃棄物処理を
せねばならないような場合においては極めて効果的であ
る。Therefore, the cleaning method of the present invention is extremely effective in the case where the cleaning waste liquid must be further treated as radioactive waste, as in a boiling water nuclear power plant.
以下に本発明の効果をより明確とするために実施例を
説明する。Examples will be described below in order to clarify the effects of the present invention.
実施例 内径0.8mm、外径1.2mm、長さ1000mmの中空糸2000本を
束ねた直径80mmの中空糸モジュール(濾過総面積7.6
m2)1本を実験用濾過塔に装着し、発電所の復水に水酸
化鉄、α−三二酸化鉄(α−Fe2O3)、γ−含水酸化鉄
(γ−FeOOH)の三種類の酸化鉄を添加して、懸濁固形
物として1mg/lとした合成水を、各中空糸の外側から内
側へ通す外圧型として1.75m3/Hで濾過した。Example: A hollow fiber module with an inner diameter of 0.8 mm, an outer diameter of 1.2 mm, and 2000 hollow fibers of 1000 mm in length and having a diameter of 80 mm (total filtration area 7.6
One m 2 ) was attached to the experimental filtration tower, and three of iron hydroxide, α-ferric oxide (α-Fe 2 O 3 ) and γ-iron oxide hydroxide (γ-FeOOH) were added to the condensate of the power plant. Synthetic water having 1 mg / l as a suspended solid added with various kinds of iron oxides was filtered at 1.75 m 3 / H as an external pressure type which passed from the outside to the inside of each hollow fiber.
当該濾過後に気泡による振動と濾過水の逆流による洗
浄を行って、再び濾過を行うというサイクルを繰り返し
たところ50サイクル経過時の通水初期の差圧は1.25kg/c
m2at1.75m3/Hとなった。After the filtration, the cycle of repeating vibration by bubbles and backflow of filtered water, and then filtering again was repeated, and the differential pressure at the beginning of water passage after 50 cycles was 1.25 kg / c.
It became m 2 at 1.75m 3 / H.
そこで、51サイクル目において、5重量%の過酸化水
素溶液を当該汚染モジュールに20時間浸漬し、その後気
泡による振動と濾過水の逆流による洗浄を行ったとこ
ろ、通水初期の差圧は0.65kg/cm2at1.75m3/Hとなり、差
圧は回復した。Therefore, in the 51st cycle, a 5% by weight hydrogen peroxide solution was immersed in the contaminated module for 20 hours, and after that, washing was performed by vibration due to bubbles and backflow of filtered water. / cm 2 at 1.75m 3 / H, the differential pressure recovered.
なお以上の結果を新品モジュールの通水初期の差圧と
ともに第1表に示した。The above results are shown in Table 1 together with the differential pressure of the new module at the initial stage of water passage.
なお前述の過酸化水素溶液による洗浄の際に排出する
洗浄排液に波長260nmの紫外線を5時間循環照射したと
ころ、洗浄排液中の過酸化水素はほぼ完全に分解するこ
とができた。 When the cleaning waste liquid discharged during the cleaning with the above-mentioned hydrogen peroxide solution was circulated and irradiated with ultraviolet rays having a wavelength of 260 nm for 5 hours, the hydrogen peroxide in the cleaning waste liquid could be almost completely decomposed.
図面は本発明の実施態様を示す濾過塔および洗浄槽のフ
ローを示す説明図である。 1…濾過塔、2…仕切板 3…中空糸モジュール、4…スカート部 5…ディストリビュータ、6…流入管 7…流出管、8…空気流入管 9…ブロー管、10…洗浄排液槽 11…上部鏡板、12…洗浄槽 13…薬液槽、14…ポンプ 15…熱交換器、16…蒸気 17…空気抜き管Drawing is an explanatory view showing a flow of a filtration tower and a washing tank showing an embodiment of the present invention. 1 ... Filtration tower, 2 ... Partition plate 3 ... Hollow fiber module, 4 ... Skirt part 5 ... Distributor, 6 ... Inflow pipe 7 ... Outflow pipe, 8 ... Air inflow pipe 9 ... Blow pipe, 10 ... Wash drainage tank 11 ... Upper end plate, 12 ... Cleaning tank 13 ... Chemical solution tank, 14 ... Pump 15 ... Heat exchanger, 16 ... Steam 17 ... Air vent tube
───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 昭60−175504(JP,A) 特開 昭51−105988(JP,A) 特開 昭51−13391(JP,A) ─────────────────────────────────────────────────── ─── Continuation of the front page (56) Reference JP-A-60-175504 (JP, A) JP-A-51-105988 (JP, A) JP-A-51-13391 (JP, A)
Claims (2)
中空糸モジュールを形成し、当該中空糸モジュールの多
数本を濾過塔内に横設した仕切板の下部に垂設した構成
よりなる濾過塔で、酸化鉄を含む復水を各中空糸の外側
から内側に通流する濾過処理をすることにより、酸化鉄
で汚染された中空糸モジュールを洗浄するにあたり、各
中空糸モジュールを過酸化水素溶液またはオゾン溶液に
接触させ、しかる後に各中空糸モジュールの下方から空
気等の気体を流入することにより発生する気泡によって
各中空糸モジュール内の各中空糸を気泡によって振動さ
せて各中空糸の膜面から酸化鉄を剥離除去することを特
徴とする中空糸モジュールの洗浄方法1. A hollow fiber module is formed by bundling a large number of hollow fibers having a large number of fine holes, and a large number of the hollow fiber modules are hung vertically at the bottom of a partition plate installed horizontally in a filtration tower. In cleaning the hollow fiber modules contaminated with iron oxide, the condensate containing iron oxide is filtered from the outside to the inside of each hollow fiber in the filtration tower, so that each hollow fiber module is peroxidized. The hollow fibers in each hollow fiber module are vibrated by the bubbles by being brought into contact with a hydrogen solution or an ozone solution, and then the gas generated by inflowing a gas such as air from below each hollow fiber module Method for cleaning hollow fiber module, characterized by removing iron oxide from the membrane surface
加熱あるいは紫外線照射して、当該排液中の過酸化水素
またはオゾンを分解する特許請求の範囲第1項記載の中
空糸モジュールの洗浄方法2. The cleaning of the hollow fiber module according to claim 1, wherein the cleaning waste liquid containing hydrogen peroxide or ozone is heated or irradiated with ultraviolet rays to decompose the hydrogen peroxide or ozone in the waste liquid. Method
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP61133760A JP2514933B2 (en) | 1986-06-11 | 1986-06-11 | Method for cleaning hollow fiber modules |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP61133760A JP2514933B2 (en) | 1986-06-11 | 1986-06-11 | Method for cleaning hollow fiber modules |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS62294406A JPS62294406A (en) | 1987-12-21 |
JP2514933B2 true JP2514933B2 (en) | 1996-07-10 |
Family
ID=15112306
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP61133760A Expired - Lifetime JP2514933B2 (en) | 1986-06-11 | 1986-06-11 | Method for cleaning hollow fiber modules |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2514933B2 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20100108601A1 (en) * | 2007-03-30 | 2010-05-06 | Masahiro Saito | Method for Treating Ballast Water with a Membrane |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP1789165B1 (en) * | 2004-08-04 | 2014-03-12 | Siemens Water Technologies LLC | Process for cleaning membranes |
JP2008221178A (en) * | 2007-03-15 | 2008-09-25 | Kuraray Co Ltd | Cleaning method of hollow fiber membrane module |
Family Cites Families (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS60175504A (en) * | 1984-02-22 | 1985-09-09 | Kurita Water Ind Ltd | Method for washing membrane separation apparatus |
-
1986
- 1986-06-11 JP JP61133760A patent/JP2514933B2/en not_active Expired - Lifetime
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20100108601A1 (en) * | 2007-03-30 | 2010-05-06 | Masahiro Saito | Method for Treating Ballast Water with a Membrane |
Also Published As
Publication number | Publication date |
---|---|
JPS62294406A (en) | 1987-12-21 |
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