JPH11319517A - Membrane separation apparatus, membrane separation method, and method for washing membrane separation apparatus - Google Patents

Membrane separation apparatus, membrane separation method, and method for washing membrane separation apparatus

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Publication number
JPH11319517A
JPH11319517A JP12620998A JP12620998A JPH11319517A JP H11319517 A JPH11319517 A JP H11319517A JP 12620998 A JP12620998 A JP 12620998A JP 12620998 A JP12620998 A JP 12620998A JP H11319517 A JPH11319517 A JP H11319517A
Authority
JP
Japan
Prior art keywords
membrane
water
membrane separation
treated
cleaning
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
JP12620998A
Other languages
Japanese (ja)
Inventor
Kazuyoshi Takahashi
和義 高橋
Masato Noguchi
真人 野口
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.)
Sumitomo Heavy Industries Ltd
Original Assignee
Sumitomo 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 Sumitomo Heavy Industries Ltd filed Critical Sumitomo Heavy Industries Ltd
Priority to JP12620998A priority Critical patent/JPH11319517A/en
Publication of JPH11319517A publication Critical patent/JPH11319517A/en
Pending legal-status Critical Current

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  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a membrane separation apparatus and a membrane separation method capable of carrying out continuous operation for a long duration by preventing fouling of membranes and to provide a method for washing the membrane separation apparatus by which membranes are efficiently washed in the case the membranes are fouled. SOLUTION: In a membrane separation method for filtering object water to be treated by a membrane element 2 immersed in a treatment tank 1 and solid-liq. separating the water, the object water is filtered while the membrane element 2 being washed by ultrasonic waves. In this case, based on high local energy of the cavitation-forming effect of ultrasonic waves and interface disturbing phenomenon and the likes, solid matter adhering to the membrane surface of the membrane element 2 and hardly to be shaken off and dirt in the insides of fine pores are efficiently separated, and solid matter is suppressed from adhering to the membrane surface.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、膜分離装置及び方
法並びにその洗浄方法に関し、より詳細には、処理槽内
に浸漬配置される膜エレメントにより、被処理水をろ過
して固液分離する膜分離装置及び方法並びにその洗浄方
法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus and a method for membrane separation, and a method for cleaning the same. The present invention relates to a membrane separation device and method and a cleaning method thereof.

【0002】[0002]

【従来の技術】廃水等の固液分離の手法として多くの方
法があるが、その中でも現在、注目されているのが、膜
を利用する分離法である。膜分離法は清澄な処理水が安
定して得られ、また汚泥の濃縮ができる等の多くの利点
がある。膜分離法でも特に注目されている方法として、
浸漬膜法がある。この方法は処理水槽に収容された被処
理水に膜エレメントを浸漬配置し、膜エレメントの膜が
被処理水中の水だけを透過させるようにしている。この
場合、該ろ過水は膜の被処理水側に圧力を加えたり、膜
のろ過水側から吸引力を加えたりすることによって透過
させられる。
2. Description of the Related Art There are many methods for solid-liquid separation of wastewater and the like, and among them, a separation method using a membrane is currently attracting attention. The membrane separation method has many advantages such that clear treated water can be stably obtained and sludge can be concentrated. As a method that has received special attention in membrane separation,
There is an immersion film method. In this method, the membrane element is immersed in the water to be treated accommodated in the treatment water tank, and the membrane of the membrane element allows only the water in the water to be treated to permeate. In this case, the filtered water is permeated by applying pressure to the treated water side of the membrane or applying suction from the filtered water side of the membrane.

【0003】ところで、運転動力費の低減や膜の強度の
点から一般に膜の被処理水側に加えられる圧力、又は膜
のろ過水側から加えられる吸引力は小さく、ろ過水が膜
を低速で透過するので、所定のろ過水量を得ようとする
と、膜の表面積を広くする必要がある。
In general, the pressure applied to the treated water side of the membrane or the suction force applied from the filtered water side of the membrane is small from the viewpoint of reduction in operating power cost and strength of the membrane. Because of the permeation, it is necessary to increase the surface area of the membrane in order to obtain a predetermined amount of filtered water.

【0004】そこで、膜エレメントとして平膜エレメン
トを使用した場合には、該平膜エレメントが処理槽内に
おいて短いピッチで積層され、膜の収容密度が高められ
るようになっている。また、同様に中空糸膜やチューブ
ラ(管状)膜ではそれらを束ねた膜エレメントが使用さ
れる。
Therefore, when a flat membrane element is used as a membrane element, the flat membrane elements are stacked at a short pitch in a processing tank, so that the accommodation density of the membrane is increased. Similarly, a hollow fiber membrane or a tubular (tubular) membrane uses a membrane element obtained by bundling them.

【0005】ところで、前記被処理水をろ過すると、被
処理水中の懸濁物質や高分子物質が膜面に残留し、次第
に膜面に付着又は濃縮して膜エレメントの透過性能を低
下させてしまう。
By the way, when the water to be treated is filtered, suspended substances and polymer substances in the water to be treated remain on the membrane surface, and gradually adhere to or concentrate on the membrane surface, thereby reducing the permeability of the membrane element. .

【0006】そこで、膜エレメントの下方から空気等の
気体が供給されて曝気ないしはバブリングが行われ、リ
フト作用や撹拌作用によって膜面にせん断力が加えられ
て固形物等の付着を少なくするようにしている。
Accordingly, a gas such as air is supplied from below the membrane element to perform aeration or bubbling, and a shearing force is applied to the membrane surface by a lifting action or a stirring action to reduce the adhesion of solids and the like. ing.

【0007】また、気体の曝気に代えて、あるいは気体
の曝気と共に、膜を回転させる手法を用いる方法もある
(回転平膜等)。また、膜エレメントを機械的に振動さ
せて固形物等の付着を少なくするようにした方法もあ
る。
[0007] There is also a method of rotating the film instead of or together with the gas aeration (rotating flat film, etc.). There is also a method in which the membrane element is mechanically vibrated to reduce the adhesion of solids and the like.

【0008】[0008]

【発明が解決しようとする課題】しかしながら、懸濁物
質等を含む被処理水に膜を浸漬して、単に加圧下又は減
圧下でろ過する従来の膜分離方法では、沈殿分離等に比
べて、非常に清澄な処理水が得られるものの、ろ過を継
続すると、膜面や膜の細孔内に固形物等が付着あるいは
侵入し、ろ過性能が次第に低下する。
However, in a conventional membrane separation method in which a membrane is immersed in water to be treated containing a suspended substance or the like, and is simply filtered under pressure or under reduced pressure, the conventional membrane separation method has a disadvantage in comparison with precipitation separation. Although very clear treated water can be obtained, if filtration is continued, solids or the like adhere or enter the membrane surface or into the pores of the membrane, and the filtration performance gradually decreases.

【0009】また、設置した膜エレメントの下部より空
気等の気体をバブリングさせ、気泡の衝撃力や発生する
強い水の流れを利用して付着した固形物の剥離あるいは
付着防止を図る膜分離方法においては、膜の閉塞を抑制
することができるが一般にその効果は不十分で閉塞がか
なりの頻度で起こる。即ち、膜面に加えられるせん断力
が小さいので、膜面に付着した固形物が残留しやすく、
膜分離処理を継続すると固形物の付着が進み、ろ過抵抗
が大きくなってしまう。従って、膜の被処理水側に加え
られる圧力、又はろ過水側から加えられる吸引力を一定
にして定圧ろ過運転を行おうとすると、ろ過水量が少な
くなり、該ろ過水量を一定にして定量ろ過運転行おうと
すると、被処理水側とろ過水側との差圧が大きくなるの
で、膜分離処理を長時間にわたって継続することができ
なくなってしまう。
Further, in a membrane separation method for bubbling a gas such as air from below the installed membrane element to prevent the adhered solids from being separated or adhered by utilizing the impact force of bubbles or the strong flow of generated water. Can suppress membrane occlusion, but its effect is generally insufficient and occlusion occurs at a considerable frequency. That is, since the shearing force applied to the membrane surface is small, solid matter attached to the membrane surface is likely to remain,
If the membrane separation process is continued, solid substances will adhere and the filtration resistance will increase. Therefore, if the pressure applied to the water to be treated side of the membrane or the suction force applied from the filtered water side is kept constant to perform the constant pressure filtration operation, the amount of the filtered water decreases, and the fixed filtration water amount is kept constant to perform the quantitative filtration operation. Attempting to do so increases the pressure difference between the water to be treated and the filtered water, so that the membrane separation process cannot be continued for a long time.

【0010】また、膜を回転させる方法や膜エレメント
をセットした膜モジュールを機械的に揺らして振動を与
え、固形物の付着防止を図る方法については、単に機械
的に振動を与える程度では膜面への固形物の付着、細孔
の閉塞を防止することはできず、閉塞が起こる。
[0010] In addition, a method of rotating a membrane or a method of mechanically shaking a membrane module on which a membrane element is set to apply vibration to prevent the adhesion of solid matter is not enough to apply mechanical vibration. It is not possible to prevent solid matter from adhering to the pores and block the pores, and blockage occurs.

【0011】また、上記のいずれの膜分離方法も、膜が
汚れたり閉塞した時には処理を中断し、膜表面をブラシ
で洗浄したり、酸、アルカリ等の洗浄液に膜を浸漬して
膜面を洗浄する方法を併用しているのが一般的である。
しかしながら、この方法では、膜面の洗浄はある程度で
きるものの、細孔内の閉塞に対しては余り効果がなく、
洗浄効果が不十分で再使用後、比較的早い閉塞が起こる
という問題があった。
In any of the above-mentioned membrane separation methods, when the membrane becomes dirty or clogged, the treatment is interrupted, and the membrane surface is washed with a brush, or the membrane surface is immersed in a cleaning solution such as acid or alkali to clean the membrane surface. It is common to use a washing method in combination.
However, with this method, although the membrane surface can be washed to some extent, it has little effect on blocking in the pores,
There was a problem that the cleaning effect was insufficient and the blockage occurred relatively quickly after reuse.

【0012】そこで、本発明は、上記事情に鑑み、膜の
閉塞を防止して長期の連続運転を可能にする膜分離装置
及び方法並びに膜が閉塞した場合の膜の洗浄を効果的に
行うことを可能にする膜分離装置の洗浄方法を提供する
ことを目的とする。
In view of the above circumstances, the present invention has been made in view of the above circumstances, and has as its object to prevent a membrane from being clogged and to enable a long-term continuous operation, and to effectively perform membrane cleaning when the membrane is clogged. It is an object of the present invention to provide a method for cleaning a membrane separation device which enables the above.

【0013】[0013]

【課題を解決するための手段】上記目的を達成するた
め、本発明の膜分離方法は、処理槽内に浸漬配置される
膜エレメントにより被処理水をろ過して固液分離する膜
分離方法において、膜エレメントを超音波洗浄しながら
被処理水をろ過することを特徴とする。
In order to achieve the above object, a membrane separation method of the present invention is directed to a membrane separation method in which water to be treated is filtered by a membrane element immersed and disposed in a treatment tank to perform solid-liquid separation. In addition, the water to be treated is filtered while ultrasonically cleaning the membrane element.

【0014】本発明によれば、超音波によるキャビテー
ション作用のもつ局部的に大きなエネルギーにより、膜
エレメントの膜面に付着した落ちにくい固形物や細孔内
の汚れが効果的に剥離されると共に、膜面に固形物が付
着するのを抑制することができる。
According to the present invention, a solid substance which adheres to the membrane surface of the membrane element and dirt in the pores are effectively peeled off by locally large energy having a cavitation action by ultrasonic waves, Adhesion of solid matter to the film surface can be suppressed.

【0015】また、本発明の膜分離装置の洗浄方法は、
処理槽内に浸漬配置される膜エレメントにより被処理水
をろ過して固液分離する膜分離装置の洗浄方法におい
て、膜エレメントの膜が閉塞した段階で、膜エレメント
を超音波洗浄することを特徴とする。
Further, the method for cleaning a membrane separation device of the present invention comprises:
In a method for cleaning a membrane separation device in which water to be treated is filtered and solid-liquid separated by a membrane element immersed and disposed in a treatment tank, the membrane element is ultrasonically cleaned when the membrane of the membrane element is closed. And

【0016】この発明によれば、超音波によるキャビテ
ーション作用のもつ局部的に大きなエネルギーにより、
膜エレメントの膜面に付着した落ちにくい固形物や細孔
内の汚れが効果的に剥離される。
According to the present invention, the locally large energy of the cavitation action by the ultrasonic wave can be used.
The solids that are hard to fall off and the dirt in the pores adhered to the membrane surface of the membrane element are effectively peeled off.

【0017】また、本発明の膜分離装置は、処理槽内に
浸漬配置される膜エレメントにより被処理水をろ過して
固液分離する膜分離装置において、膜エレメントを超音
波洗浄するための超音波発生装置を備えることを特徴と
する。
Further, the membrane separation apparatus of the present invention is a membrane separation apparatus for filtering water to be treated by a membrane element immersed and disposed in a treatment tank to perform solid-liquid separation. It is characterized by having a sound wave generator.

【0018】この発明によれば、超音波発生装置により
超音波が被処理水に付与され、超音波によるキャビテー
ション作用のもつ局部的に大きなエネルギーにより、膜
エレメントの膜面に付着した落ちにくい固形物や細孔内
の汚れが効果的に剥離されると共に、膜面に固形物が付
着するのを抑制することができる。また、本発明は、膜
エレメントの膜が閉塞した段階で膜エレメントを超音波
洗浄する場合でも、超音波によるキャビテーション作用
のもつ局部的に大きなエネルギーにより、膜面に付着し
た落ちにくい固形物や細孔内の汚れが効果的に剥離され
る。
According to the present invention, the ultrasonic wave is applied to the water to be treated by the ultrasonic wave generator, and the solid matter adhered to the membrane surface of the membrane element due to the locally large energy having the cavitation action by the ultrasonic wave. And the dirt in the pores can be effectively peeled off, and the attachment of solid matter to the membrane surface can be suppressed. In addition, the present invention provides a method for cleaning a membrane element with ultrasonic waves when the membrane of the membrane element is closed due to locally large energy having cavitation action by ultrasonic waves. The dirt in the holes is effectively peeled off.

【0019】[0019]

【発明の実施の形態】以下、本発明の実施形態について
図1及び図2を参照して詳細に説明する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described below in detail with reference to FIGS.

【0020】図1は、本発明の膜分離装置の第1実施形
態を示す断面図である。図1に示すように、膜分離装置
10は処理槽1を備えており、この処理槽1内には被処
理水流入ラインL1を通して被処理水が流入される。被
処理水には、所定間隔を置いて積層される膜エレメント
2としての平膜エレメントが複数浸漬されている。膜エ
レメント2としては、平膜エレメントの代わりに中空糸
膜やチューブラ膜の浸漬膜に置き換えることができる。
また、これらの浸漬膜の種類としてはRO膜、NF膜、
UF膜、MF膜等のいずれも使用することができる。
FIG. 1 is a sectional view showing a first embodiment of the membrane separation apparatus of the present invention. As shown in FIG. 1, the membrane separation apparatus 10 includes a treatment tank 1, into which treatment water flows through a treatment water inflow line L1. In the water to be treated, a plurality of flat membrane elements as the membrane elements 2 stacked at predetermined intervals are immersed. The membrane element 2 can be replaced with an immersion membrane such as a hollow fiber membrane or a tubular membrane instead of the flat membrane element.
The types of these immersion films are RO film, NF film,
Any of a UF film, an MF film and the like can be used.

【0021】各膜エレメント2には集水管L2が接続さ
れ、該各集水管L2に膜エレメント2の膜を透過した水
がろ過水として集められるようになっている。各集水管
L2はラインL3に接続されている。そして該ラインL
3に接続された図示しない吸引ポンプによって膜エレメ
ント2内に負圧が発生させられ、ろ過水が吸引される。
A water collecting pipe L2 is connected to each membrane element 2, and water permeating the membrane of the membrane element 2 is collected in each water collecting pipe L2 as filtered water. Each collecting pipe L2 is connected to a line L3. And the line L
A negative pressure is generated in the membrane element 2 by a suction pump (not shown) connected to 3, and the filtered water is sucked.

【0022】また、膜分離装置10には超音波発生装置
11が設けられ、超音波発生装置11により処理槽1内
の被処理水に超音波が付与される。超音波発生装置11
は超音波の周波数をもった高周波電流を供給する発振器
と、この高周波電気エネルギーを機械的エネルギーであ
る超音波振動に変える振動子とからなり、発振器は発振
回路及び能動素子(トランジスター、サイリスタ等)を
目的に合わせて使い分けることにより、数十ワットの小
出力のものから数十キロワット程度の大出力のものが得
られる。また、振動子としてはジルコチタン酸鉛やチタ
ン酸バリウム等のセラミックの電歪現象を応用したも
の、あるいはニッケル、フェライト、アルフェロ等の磁
歪現象を応用したものが使われる。セラミック系のもの
は100〜400キロサイクル/secの比較的高い周
波数を使用する場合に多く使われるが、高価であるた
め、大出力のものにはニッケル、フェライト、アルフェ
ロ等の磁歪現象を応用した振動子が使われ、通常、20
〜50キロサイクル/sec程度の周波数に用いられ
る。
Further, an ultrasonic generator 11 is provided in the membrane separation apparatus 10, and the ultrasonic generator 11 applies ultrasonic waves to the water to be treated in the treatment tank 1. Ultrasonic generator 11
Consists of an oscillator that supplies a high-frequency current having the frequency of an ultrasonic wave and a vibrator that converts this high-frequency electric energy into ultrasonic vibration, which is mechanical energy. The oscillator is an oscillation circuit and active elements (transistors, thyristors, etc.) Depending on the purpose, a power output of several tens of watts and a power output of several tens of kilowatts can be obtained. Further, as the vibrator, a vibrator that uses an electrostriction phenomenon of a ceramic such as lead zirconate titanate or barium titanate, or a vibrator that applies a magnetostriction phenomenon such as nickel, ferrite, or alphero is used. The ceramic type is often used when a relatively high frequency of 100 to 400 kilocycles / sec is used, but is expensive, so the magnetostrictive phenomenon of nickel, ferrite, alphero, etc. is applied to the high output type. Oscillator is used, usually 20
It is used for a frequency of about 50 kilocycles / sec.

【0023】超音波による洗浄はキャビテーションを利
用する。キャビテーションを発生するのに必要な力は周
波数が多くなればなるほど大きな力を必要とするので、
膜の洗浄には低出力でもキャビテーション効果の良い2
0〜50キロサイクル/sec程度の比較的周波数の低
いものを使用することが適している。
The ultrasonic cleaning uses cavitation. The force required to generate cavitation requires more power at higher frequencies,
Good cavitation effect even at low output for film cleaning 2
It is suitable to use one having a relatively low frequency of about 0 to 50 kilocycles / sec.

【0024】例えばフェライト振動子を用いて被処理水
中に超音波を発生させるには、この振動子をそのまま被
処理水中に漬けて使用するか、又は図1に示すように、
ステンレス等の金属鋼薄板で作った処理槽1の底面にフ
ェライト振動子3を接着して使用してもよい。大型の処
理槽1では多数の振動子を共通の巻線で励振することも
できる。上記のように振動子を直接使用する方法のほ
か、振幅拡大やエネルギー集中のためにホーンを介して
被処理水に超音波振動を伝える方法を利用することもで
きる。
For example, in order to generate ultrasonic waves in the water to be treated by using a ferrite vibrator, the vibrator is immersed in the water to be treated as it is, or as shown in FIG.
The ferrite vibrator 3 may be used by bonding it to the bottom of the processing tank 1 made of a thin metal plate such as stainless steel. In the large processing tank 1, a large number of vibrators can be excited by a common winding. In addition to the method of directly using the vibrator as described above, a method of transmitting ultrasonic vibrations to the water to be treated via a horn for amplitude expansion and energy concentration can also be used.

【0025】尚、図1において、コイル4及びバイアス
磁石5は発振回路の一部を構成するものであり、コイル
4に流される高周波電流により発生する磁界、およびバ
イアス磁石5からの磁界がフェライト振動子3に加えら
れ、これによりフェライト振動子3に生じる超音波振動
が処理槽1内の被処理水に付与される。
In FIG. 1, the coil 4 and the bias magnet 5 constitute a part of an oscillation circuit, and a magnetic field generated by a high-frequency current flowing through the coil 4 and a magnetic field from the bias magnet 5 cause ferrite oscillation. The ultrasonic vibration generated in the ferrite vibrator 3 is applied to the water to be treated in the processing tank 1.

【0026】次に、前述した構成を有する膜分離装置1
0の作用について説明する。
Next, the membrane separation apparatus 1 having the above-described configuration will be described.
The operation of 0 will be described.

【0027】膜分離装置10においては、膜分離を行う
処理槽1内の被処理水は、超音波を付与されながら膜エ
レメント2によってろ過される。このとき、超音波発生
装置11から被処理水に超音波を放射すると、被処理水
は一周期のある期間は負圧力(張力)を受けることにな
り、被処理水は引きちぎられて真空になり、その中に液
体や溶解した気体が入って気泡となる。この気泡が次の
期間正の圧力を受けて圧縮される。このように音波によ
って気泡は激しく膨張収縮運動を繰り返し、膨張した気
泡はほとんど真空に近い状態になり、圧縮された気泡は
高温高圧となって爆発的に破壊する(キャビテーション
現象)。この瞬間に大きな力が働き、数千気圧の衝撃波
を発生する。又、この大きな力による撹拌作用が起こ
る。更に密度差のある異相界面(液体と膜表面)では超
音波は著しい反射を起こし、この反射音圧のために界面
で機械撹拌が行われる。すなわち、超音波を被処理水に
付与すると、キャビテーション作用のもつ局部的に大き
なエネルギーと界面撹乱現象などにより、膜面に付着し
た落ちにくい固形物や細孔内の汚れが効果的に剥離され
ると共に、膜面に固形物が付着するのを抑制することが
できるので、膜エレメント2の膜の閉塞が十分防止さ
れ、長期の安定運転が可能になる。
In the membrane separation apparatus 10, the water to be treated in the treatment tank 1 for performing membrane separation is filtered by the membrane element 2 while applying ultrasonic waves. At this time, when ultrasonic waves are radiated from the ultrasonic generator 11 to the water to be treated, the water to be treated is subjected to a negative pressure (tension) for a certain period of one cycle, and the water to be treated is torn to a vacuum. Then, liquid or dissolved gas enters into it, forming bubbles. This bubble is compressed by receiving a positive pressure for the next period. As described above, the sound waves cause the bubbles to repeatedly expand and contract intensely, so that the expanded bubbles are almost in a state close to a vacuum, and the compressed bubbles become high-temperature and high-pressure and are explosively destroyed (cavitation phenomenon). At this moment, a large force acts, generating a shock wave of several thousand atmospheres. In addition, a stirring action by this large force occurs. Further, at the hetero-phase interface (liquid and film surface) where there is a difference in density, ultrasonic waves are remarkably reflected, and mechanical agitation is performed at the interface due to the reflected sound pressure. In other words, when ultrasonic waves are applied to the water to be treated, due to locally large energy having a cavitation effect and interface disturbance phenomena, solid substances adhered to the membrane surface and dirt in pores are effectively removed. At the same time, it is possible to prevent solid matter from adhering to the membrane surface, so that blockage of the membrane of the membrane element 2 is sufficiently prevented, and long-term stable operation becomes possible.

【0028】尚、超音波の付与は連続に行う以外に、あ
る時間間隔をもって間欠的に付与してもよい。
The application of ultrasonic waves may be performed intermittently at certain time intervals, instead of being performed continuously.

【0029】次に、本発明の膜分離装置の第2実施形態
について説明する。なお、第1実施形態と同一又は相当
する構成要素については同一の符号を付す。
Next, a second embodiment of the membrane separation apparatus of the present invention will be described. The same or corresponding components as those of the first embodiment are denoted by the same reference numerals.

【0030】図2は、本発明の膜分離装置の第2実施形
態を示す断面図である。図2に示すように、膜分離装置
20の処理槽1には、超音波発生装置11に加え、前記
各膜エレメント2の下方に散気管6が配設され、該散気
管6はラインL4に接続されている。そして該ラインL
4に配設された図示しないブロアによって気体が散気管
6を通して被処理水中に供給され、曝気が行われ、気泡
になって上昇するようになっている。気体としては、空
気、酸素その他のガスを使用することができる。
FIG. 2 is a sectional view showing a second embodiment of the membrane separation apparatus of the present invention. As shown in FIG. 2, in the treatment tank 1 of the membrane separation device 20, in addition to the ultrasonic generator 11, an air diffuser 6 is disposed below each of the membrane elements 2, and the air diffuser 6 is connected to a line L 4. It is connected. And the line L
The gas is supplied into the water to be treated through the air diffuser 6 by a blower (not shown) disposed at 4, and is aerated so as to form bubbles and rise. As the gas, air, oxygen and other gases can be used.

【0031】このような膜分離装置20においては、超
音波発生装置11により被処理水に超音波が付与され、
ガスバブリングが行われると、超音波による洗浄効果に
加えて、ガスバブリングによる気泡のリフト作用による
せん断力、及び同時に形成される水流によるせん断力が
膜エレメント2の表面に加えられ、膜に付着する固形物
が除去されると共に、膜面に固形物が付着するのを抑制
することができる。このため、きわめて効果的に膜面の
固形物の付着や膜の細孔内の閉塞を防止することがで
き、長期間の安定運転を可能にすることができる。
In such a membrane separation device 20, ultrasonic waves are applied to the water to be treated by the ultrasonic generator 11,
When the gas bubbling is performed, in addition to the cleaning effect by the ultrasonic wave, the shearing force due to the lifting action of the bubbles by the gas bubbling and the shearing force due to the simultaneously formed water flow are applied to the surface of the membrane element 2 and adhere to the membrane. The solids are removed, and the solids can be prevented from adhering to the film surface. Therefore, it is possible to extremely effectively prevent solid matter from adhering to the membrane surface and blockage in pores of the membrane, thereby enabling long-term stable operation.

【0032】また、上記第1及び第2の実施形態の洗浄
方法は、膜分離を行っている時だけに限らず、一旦、膜
に所定程度以上に固形物が付着したり細孔内が閉塞した
りしたときに、膜分離処理を停止した状態で洗浄する場
合にも効果的であることは言うまでもない。すなわち、
本発明の超音波を使用する方法では膜面での強力なキャ
ビテーション効果により効果的な膜の洗浄が行える。こ
の場合、処理槽1内の被処理水又は膜エレメント2の膜
の内側の処理水を酸(塩酸、硫酸、クエン酸等)、アル
カリ(カセイソーダ等)、酸化剤(次亜塩素酸ソーダ
等)、還元剤、キレート化剤若しくは界面活性剤を含有
する洗浄液に交換し、これら洗浄液に超音波を付与する
と、超音波による衝撃波と洗浄液との洗浄力との相乗作
用により、膜面の付着物に限らず、細孔内の閉塞物に対
しても有効に剥離効果があり、一層効果的な膜面の洗浄
が可能となる。
Further, the cleaning methods of the first and second embodiments are not limited to the time when the membrane is separated, but once the solids adhere to the membrane to a predetermined degree or more and the pores are closed. Needless to say, this is also effective in the case where cleaning is performed in a state where the membrane separation process has been stopped. That is,
In the method using ultrasonic waves of the present invention, effective cleaning of the film can be performed by the strong cavitation effect on the film surface. In this case, the water to be treated in the treatment tank 1 or the treated water inside the membrane of the membrane element 2 is converted into acid (hydrochloric acid, sulfuric acid, citric acid, etc.), alkali (caustic soda, etc.), oxidizing agent (sodium hypochlorite, etc.). If the cleaning solution is replaced with a cleaning solution containing a reducing agent, a chelating agent or a surfactant, and ultrasonic waves are applied to these cleaning solutions, a synergistic effect of the shock wave generated by the ultrasonic waves and the cleaning power of the cleaning solution may be applied to deposits on the film surface. Not only that, there is also an effective peeling effect on the clogging in the pores, and more effective cleaning of the membrane surface becomes possible.

【0033】本発明の膜分離装置および膜分離方法は、
被処理水中の懸濁物質の除去や濃縮あるいは溶解した塩
分や有害物質の除去に利用することができる。例えば河
川水、湖沼水、各種の廃水、活性汚泥やメタン発酵等の
生物汚泥の分離、濃縮や凝集沈殿汚泥の分離、濃縮、更
には溶解性の塩分や有機塩素化合物等の分離、除去等の
広い分野に利用することができる。
The membrane separation device and the membrane separation method of the present invention
It can be used for removing and concentrating suspended substances in the water to be treated or for removing dissolved salts and harmful substances. For example, river water, lake water, various wastewaters, separation of biological sludge such as activated sludge and methane fermentation, separation and concentration of coagulated sedimentation sludge, separation and removal of soluble salts and organic chlorine compounds, etc. Can be used in a wide range of fields.

【0034】[0034]

【実施例】(実施例1)図1の形態における膜分離方法
を生物処理装置(活性汚泥処理)に適用した例を下記に
説明する。膜面積が0.05m2(12.5cm×20
cm×2(両面))の膜エレメントを各膜間距離13m
mとして5枚積層した膜モジュール1ヶを、600Wの
超音波洗浄装置を処理槽(40cm(w)×25cm
(l)×45cm(h)=45000cm3)とする水
槽に浸漬し、懸濁物質7000mg/lの被処理水を供
給し、超音波を付与しながら吸引ろ過速度を毎分0.1
7l(1.0m3/m2/d)に設定して膜分離を行っ
た。その結果、図3に示す様に、試験開始後2週間程度
までは、膜差圧の増加は僅かであった。尚、図3におい
て、横軸は膜ろ過の運転時間、縦軸は25℃における膜
差圧である。
(Embodiment 1) An example in which the membrane separation method in the embodiment of FIG. 1 is applied to a biological treatment apparatus (activated sludge treatment) will be described below. The film area is 0.05 m 2 (12.5 cm × 20
cm × 2 (both sides)) with a membrane distance of 13 m
m, and one membrane module obtained by stacking five membrane modules was placed in a processing bath (40 cm (w) × 25 cm) using a 600 W ultrasonic cleaning device.
(L) × 45 cm (h) = 45000 cm 3 ), 7000 mg / l of water to be treated was supplied as a suspended substance, and the suction filtration rate was set to 0.1 per minute while applying ultrasonic waves.
The membrane was separated at a setting of 7 l (1.0 m 3 / m 2 / d). As a result, as shown in FIG. 3, the increase in the transmembrane pressure was slight until about two weeks after the start of the test. In FIG. 3, the horizontal axis represents the operation time of membrane filtration, and the vertical axis represents the membrane differential pressure at 25 ° C.

【0035】(比較例1)超音波を付与しない以外は、
実施例1と同じ条件でろ過を行った。図3に示すよう
に、2日程度で膜差圧が急激に増加し、膜閉塞が進行し
た。
Comparative Example 1 Except that no ultrasonic wave was applied,
Filtration was performed under the same conditions as in Example 1. As shown in FIG. 3, the transmembrane pressure increased rapidly in about two days, and the membrane occlusion advanced.

【0036】(実施例2)図2の形態における膜分離方
法を上記実施例1に用いた被処理水と同じものに適用し
た例を下記に示す。
(Example 2) An example in which the membrane separation method in the embodiment of FIG. 2 is applied to the same water to be treated used in Example 1 above is shown below.

【0037】膜面積が0.05m2(12.5cm×2
0cm×2(両面))の膜エレメントを各膜間距離13
mmとして5枚積層した膜モジュール1ヶを、600W
の超音波洗浄装置を処理槽(40cm(w)×25cm
(l)×45cm(h)=45000cm3)とする水
槽に浸漬し、懸濁物質7000mg/lの被処理水を供
給し、超音波を付与すると共に膜エレメントの下部から
空気を毎分4lで供給して、バブリング洗浄を併用しな
がら、吸引ろ過速度を毎分0.17l(1.0m3/m2
/d)に設定して膜分離を行った。その結果、図3に示
す様に、試験開始1ヶ月後でも、膜差圧の増加は僅かで
あった。すなわち、超音波付与のみの場合の実施例1の
結果に比べて、バブリング洗浄を併用すると、更に改善
されることが分かった。
The membrane area 0.05m 2 (12.5cm × 2
0 cm x 2 (both sides)) with a membrane distance of 13
1 mm membrane module with a capacity of 600 W
Of the ultrasonic cleaning device in the treatment tank (40 cm (w) x 25 cm)
(L) × 45 cm (h) = 45000 cm 3 ), and 7000 mg / l of water to be treated was supplied as a suspended substance, ultrasonic waves were applied, and air was supplied from the lower part of the membrane element at 4 l / min. The suction filtration rate was set to 0.17 l / min (1.0 m 3 / m 2
/ D) to perform membrane separation. As a result, as shown in FIG. 3, the increase in the transmembrane pressure was slight even one month after the start of the test. That is, it was found that the combined use of bubbling cleaning was further improved as compared with the result of Example 1 in which only ultrasonic wave was applied.

【0038】(実施例3)図1の形態における膜分離方
法で、膜面積が0.05m2(12.5cm×20cm
×2(両面))の膜エレメントを各膜間距離13mmと
して5枚積層した膜モジュール1ヶを、600Wの超音
波洗浄装置を処理槽(40cm(w)×25cm(l)
×45cm(h)=45000cm3)とする水槽に浸
漬した。懸濁物質30mg/l程度の河川水を被処理水
として供給し、超音波を付与しながら吸引ろ過速度を毎
分0.26l(1.5m3/m2/d)に設定して膜分離
を行った。その結果、図4に示す様に、試験開始後20
日程度までは、膜差圧の増加はわずかであった。図4に
おいて、横軸は膜ろ過の運転時間、縦軸は25℃におけ
る膜差圧である。
(Example 3) The membrane area is 0.05 m 2 (12.5 cm × 20 cm) by the membrane separation method in the form shown in FIG.
One membrane module in which five membrane elements of × 2 (both sides) are stacked at a distance of 13 mm between each membrane is treated with a 600 W ultrasonic cleaning device in a treatment tank (40 cm (w) × 25 cm (l)).
× 45 cm (h) = 45000 cm 3 ). Suspended matter About 30 mg / l of river water is supplied as the water to be treated, and while applying ultrasonic waves, the suction filtration rate is set to 0.26 l / min (1.5 m 3 / m 2 / d) to perform membrane separation. Was done. As a result, as shown in FIG.
Until the day, the increase in transmembrane pressure was slight. In FIG. 4, the horizontal axis represents the operation time of membrane filtration, and the vertical axis represents the membrane differential pressure at 25 ° C.

【0039】(比較例2)超音波を付与しない以外は、
実施例3と同じ条件で膜分離を行った。その結果、図4
に示すように試験開始後2日程度で膜差圧が急激に増加
し、膜閉塞が進行した。
(Comparative Example 2) Except that no ultrasonic wave was applied,
Membrane separation was performed under the same conditions as in Example 3. As a result, FIG.
As shown in the figure, the membrane pressure difference rapidly increased about 2 days after the start of the test, and the membrane occlusion progressed.

【0040】[0040]

【発明の効果】以上述べたように、本発明の膜分離装置
及び方法によれば、超音波によるキャビテーション作用
のもつ局部的に大きなエネルギーと界面撹乱現象などに
より、膜面に付着した落ちにくい固形物や細孔内の汚れ
が効果的に剥離されると共に膜面に固形物が付着するの
を抑制することができ、膜分離中の膜の閉塞が十分防止
され、長期間の連続運転が可能となる。
As described above, according to the membrane separation apparatus and method of the present invention, the solid which adheres to the membrane surface due to the locally large energy of the cavitation action by ultrasonic waves and the interface disturbance phenomenon, etc. The substance and dirt in the pores are effectively peeled off, and the solid matter is prevented from adhering to the membrane surface. This prevents the membrane from being clogged during membrane separation and enables long-term continuous operation. Becomes

【0041】また、本発明の膜分離装置の洗浄方法によ
れば、超音波によるキャビテーション作用のもつ局部的
に大きなエネルギーにより、膜面に付着した落ちにくい
固形物や細孔内の汚れが効果的に剥離される。
Further, according to the method for cleaning a membrane separation device of the present invention, solid substances adhered to the membrane surface and dirt in pores are effectively removed by locally large energy having cavitation action by ultrasonic waves. Peeled off.

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

【図1】本発明の膜分離装置の一実施形態を示す断面図
である。
FIG. 1 is a sectional view showing an embodiment of a membrane separation device of the present invention.

【図2】本発明の膜分離装置の他の実施形態を示す断面
図である。
FIG. 2 is a sectional view showing another embodiment of the membrane separation device of the present invention.

【図3】実施例1、2及び比較例1に関するろ過差圧の
経時変化を示すグラフである。
FIG. 3 is a graph showing the change over time of the filtration pressure difference for Examples 1, 2 and Comparative Example 1.

【図4】実施例3、比較例2に関するろ過差圧の経時変
化を示すグラフである。
FIG. 4 is a graph showing the change over time in the filtration differential pressure for Example 3 and Comparative Example 2.

【符号の説明】[Explanation of symbols]

1…処理槽、2…膜エレメント、3…フェライト振動子
(超音波発生装置)、4…コイル(超音波発生装置)、
5…バイアス磁石(超音波発生装置)、10,20…膜
分離装置。
DESCRIPTION OF SYMBOLS 1 ... Processing tank, 2 ... Membrane element, 3 ... Ferrite vibrator (ultrasonic generator), 4 ... Coil (ultrasonic generator),
5: bias magnet (ultrasonic generator), 10, 20: membrane separation device.

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 処理槽内に浸漬配置される膜エレメント
により被処理水をろ過して固液分離する膜分離方法にお
いて、 前記膜エレメントを超音波洗浄しながら前記被処理水を
ろ過することを特徴とする膜分離方法。
1. A membrane separation method for filtering water to be treated by a membrane element immersed and disposed in a treatment tank to perform solid-liquid separation, wherein the filtration of the water to be treated is performed while ultrasonically cleaning the membrane element. Characterized membrane separation method.
【請求項2】 前記膜エレメントを超音波洗浄しながら
前記膜エレメントの下方で気体をバブリングすることを
特徴とする請求項1に記載の膜分離方法。
2. The method according to claim 1, wherein a gas is bubbled below the membrane element while ultrasonically cleaning the membrane element.
【請求項3】 処理槽内に浸漬配置される膜エレメント
により被処理水をろ過して固液分離する膜分離装置の洗
浄方法において、 前記膜エレメントの膜が閉塞した段階で、前記膜エレメ
ントを超音波洗浄することを特徴とする膜分離装置の洗
浄方法。
3. A method for cleaning a membrane separation device, wherein water to be treated is filtered and solid-liquid separated by a membrane element immersed and disposed in a treatment tank, wherein the membrane element is closed when the membrane of the membrane element is closed. A method for cleaning a membrane separation device, comprising performing ultrasonic cleaning.
【請求項4】 前記膜エレメントを超音波洗浄しながら
前記膜エレメントの下方で気体をバブリングすることを
特徴とする請求項3に記載の膜分離装置の洗浄方法。
4. The method for cleaning a membrane separation device according to claim 3, wherein a gas is bubbled below the membrane element while ultrasonically cleaning the membrane element.
【請求項5】 前記膜エレメントの膜が閉塞した後であ
って前記膜エレメントを超音波洗浄する前に、前記膜の
外側の前記被処理水及び前記膜の内側の処理水又はその
いずれか一方を洗浄液に代えることを特徴とする請求項
3又は4に記載の膜分離装置の洗浄方法。
5. The water to be treated outside the membrane and / or the water treated inside the membrane after the membrane of the membrane element is closed and before the membrane element is subjected to ultrasonic cleaning. 5. The method for cleaning a membrane separation device according to claim 3, wherein is replaced with a cleaning liquid.
【請求項6】 処理槽内に浸漬配置される膜エレメント
により被処理水をろ過して固液分離する膜分離装置にお
いて、 前記膜エレメントを超音波洗浄するための超音波発生装
置を備えることを特徴とする膜分離装置。
6. A membrane separation device for filtering water to be treated by a membrane element immersed and disposed in a treatment tank and separating the solid and liquid, comprising an ultrasonic generator for ultrasonically cleaning the membrane element. Characteristic membrane separation device.
JP12620998A 1998-05-08 1998-05-08 Membrane separation apparatus, membrane separation method, and method for washing membrane separation apparatus Pending JPH11319517A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12620998A JPH11319517A (en) 1998-05-08 1998-05-08 Membrane separation apparatus, membrane separation method, and method for washing membrane separation apparatus

Publications (1)

Publication Number Publication Date
JPH11319517A true JPH11319517A (en) 1999-11-24

Family

ID=14929430

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Link
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JP2018504263A (en) * 2015-09-01 2018-02-15 ジエンシー ジェイディエル エンバイロメンタル プロテクション カンパニー リミテッド Method and system for removing phosphorus by gasification
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WO2006038426A1 (en) 2004-10-01 2006-04-13 Nitto Denko Corporation Semipermeable composite membrane and process for producing the same
WO2006038409A1 (en) 2004-10-01 2006-04-13 Nitto Denko Corporation Process for producing semipermeable composite membrane
JP2007167789A (en) * 2005-12-22 2007-07-05 Shinshu Univ Mud taking-out method and its taking-out apparatus
US8518310B2 (en) 2006-10-10 2013-08-27 Nitto Denko Corporation Process for producing a dried composite semipermeable membrane
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JP2010520050A (en) * 2007-03-05 2010-06-10 クロネス アクティェンゲゼルシャフト Beer filter
WO2010073442A1 (en) 2008-12-25 2010-07-01 志摩環境事業協業組合 Immersion-type membrane separation apparatus
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JP2014205110A (en) * 2013-04-12 2014-10-30 国立大学法人三重大学 Waste water treatment apparatus provided with solid-liquid separation unit
JP2018504263A (en) * 2015-09-01 2018-02-15 ジエンシー ジェイディエル エンバイロメンタル プロテクション カンパニー リミテッド Method and system for removing phosphorus by gasification
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