JPH0720592B2 - Activated sludge treatment equipment - Google Patents

Activated sludge treatment equipment

Info

Publication number
JPH0720592B2
JPH0720592B2 JP63238297A JP23829788A JPH0720592B2 JP H0720592 B2 JPH0720592 B2 JP H0720592B2 JP 63238297 A JP63238297 A JP 63238297A JP 23829788 A JP23829788 A JP 23829788A JP H0720592 B2 JPH0720592 B2 JP H0720592B2
Authority
JP
Japan
Prior art keywords
membrane
filtration
water
filtration membrane
treated water
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
Application number
JP63238297A
Other languages
Japanese (ja)
Other versions
JPH0286893A (en
Inventor
宏司 石田
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.)
Kubota Corp
Original Assignee
Kubota Corp
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 Kubota Corp filed Critical Kubota Corp
Priority to JP63238297A priority Critical patent/JPH0720592B2/en
Publication of JPH0286893A publication Critical patent/JPH0286893A/en
Publication of JPH0720592B2 publication Critical patent/JPH0720592B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Description

【発明の詳細な説明】 産業上の利用分野 本発明は、単一の槽内で有機性廃水の消化処理とろ過膜
による固液分離とを行なう活性汚泥処理装置に関するも
のである。
Description: TECHNICAL FIELD The present invention relates to an activated sludge treatment device that performs digestion treatment of organic wastewater and solid-liquid separation by a filtration membrane in a single tank.

一般に、この種の活性汚泥処理装置においては、使用し
ている間にろ過膜が汚泥により目詰りを起こすので、従
来より、この目詰りを防止するための提案が種々なされ
ている。例えば、第10図に示す装置は、曝気槽1内の原
水2の浄化処理水3中に中空糸膜4がつり下げて浸さ
れ、中空糸膜4の直下に散気管5が配置されたものであ
る。原水2の浄化処理に必要な曝気用空気6はブロワー
7から散気管5を経て浄化処理水3中に吹き出される。
浄化処理水3は、吸引ポンプ8により中空糸膜4の中空
孔内が吸引されることにより固液分離され、中空糸膜4
を透過した清浄なろ過処理水9はろ過処理水槽10に送ら
れる。他方、曝気槽1内に蓄積した余剰汚泥11は適時外
部に引き抜かれる。この中空糸膜4は、連続吸引される
と目詰りが目詰り呼び、短期間で回復不能になるので、
間欠吸引を行なって周期的に圧力を開放することにより
急激な目詰りを防止し、長期間安定した運転を可能にし
ている。また、特開昭61-274799号公報に示されている
装置は、処理槽内にろ過手段を備えたものである。この
ろ過手段は、中央部に穴を設けた複数個のろ過板を中空
回転軸に前記穴を貫設して一定間隔が並列し、中空回転
軸の駆動機構によって一体に回転し、各ろ過板の間にガ
スを吐出する曝気手段が設けられたものであり、ろ過板
は、ろ過処理水通路を有する膜支持体の両面に半透膜を
おおったものである。処理槽内に送られた原水は、曝気
手段からのガスにより曝気され消化処理される。消化処
理水は、回転しているろ過板の半透膜によりろ過され、
清浄なろ過処理水は膜支持体のろ過処理水通路および中
空回転軸の中空部を経て外部に取り出される。他方、ろ
過により膜表面に付着した汚泥は、曝気用ガス自体およ
びガスの浄化処理水のかくはん作用により膜表面から離
脱する。膜表面は、ろ過手段が1回転するごとに曝気手
段のガス吐出管の位置を通過するので、きわめて短い周
期で洗浄されることになり、常に清浄に維持され、長期
間安定した使用が可能である。処理槽内に蓄積された余
剰汚泥は、適時外部に排出される。
Generally, in this type of activated sludge treatment device, the filtration membrane is clogged with the sludge during use, so various proposals have been made to prevent the clogging. For example, in the apparatus shown in FIG. 10, the hollow fiber membrane 4 is suspended and immersed in the purified water 3 of the raw water 2 in the aeration tank 1, and the air diffusing pipe 5 is arranged immediately below the hollow fiber membrane 4. Is. The aeration air 6 required for the purification treatment of the raw water 2 is blown from the blower 7 into the purified treatment water 3 through the air diffuser 5.
The purified water 3 is solid-liquid separated by the suction pump 8 sucking the inside of the hollow holes of the hollow fiber membrane 4, and the hollow fiber membrane 4
The clean filtered water 9 that has passed through is sent to the filtered water tank 10. On the other hand, the excess sludge 11 accumulated in the aeration tank 1 is pulled out to the outside in a timely manner. If the hollow fiber membrane 4 is continuously sucked, the clogging is called clogging, and the hollow fiber membrane 4 cannot be recovered in a short period of time.
By performing intermittent suction and periodically releasing the pressure, sudden clogging is prevented and stable operation is possible for a long time. Further, the device disclosed in Japanese Patent Laid-Open No. 61-274799 has a filtering means in the processing tank. This filtering means comprises a plurality of filtration plates having a hole at the center thereof, the holes being penetrated through a hollow rotary shaft and arranged in parallel at regular intervals, and the hollow rotary shaft is driven by a drive mechanism of the hollow rotary shaft so as to be integrally rotated. The aeration means for discharging gas is provided in the membrane, and the filtration plate is a membrane support having filtration-treated water passages covered with semipermeable membranes on both sides. The raw water sent into the treatment tank is aerated by the gas from the aeration means and digested. The digested water is filtered by the semipermeable membrane of the rotating filter plate,
The clean filtered water is taken out through the filtered water passage of the membrane support and the hollow portion of the hollow rotating shaft. On the other hand, the sludge attached to the membrane surface by filtration is separated from the membrane surface by the stirring action of the aeration gas itself and the purified water of the gas. Since the membrane surface passes through the position of the gas discharge pipe of the aeration means every time the filtration means makes one revolution, it is cleaned in an extremely short cycle, and it is always kept clean and can be used stably for a long period of time. is there. Excess sludge accumulated in the treatment tank is discharged to the outside in a timely manner.

発明が解決しようとする課題 しかし、原水中に多量の繊維状きよう雑物が含まれてい
る場合には、上記従来の前者の装置においては、繊維状
きよう雑物が中空糸膜4に絡み付き、最終的には1本の
汚泥の棒のようになって、中空糸膜4が完全に目詰りし
てしまうという問題があった。また、後者の装置におい
ては、繊維状きよう雑物が中空回転軸に巻き付き、最終
的にはろ過板の間を閉そくしてしまうという問題があっ
た。さらに、後者の装置においては、ろ過板の間で気液
混相流が偏流を起こす構造となっているので、膜面流速
が不均一となり、膜透過性能の低い部分が生じるおそれ
がある。そこで、これを防止するため、ろ過手段を回転
させている。そのため、構造が複雑となるだけでなく、
高価になるという問題もあった。
However, when a large amount of fibrous foreign matters are contained in the raw water, in the former conventional device, the fibrous foreign matters are contained in the hollow fiber membrane 4. There was a problem that the hollow fiber membrane 4 became entangled and finally became like a rod of sludge, and the hollow fiber membrane 4 was completely clogged. Further, in the latter device, there is a problem that the fibrous foreign matters are wound around the hollow rotary shaft and finally block the space between the filter plates. Further, in the latter device, since the gas-liquid mixed phase flow is unevenly flowed between the filtration plates, the membrane surface flow velocity becomes nonuniform, and there is a possibility that a portion having low membrane permeation performance may occur. Therefore, in order to prevent this, the filtering means is rotated. Therefore, not only is the structure complicated,
There was also the problem of becoming expensive.

本発明は、従来の装置を改良して、このような問題点を
解決することを目的とする。
It is an object of the present invention to improve the conventional device and solve such problems.

課題を解決するための手段 上記目的を達成するために、本発明の活性汚泥処理装置
は、曝気槽内の原水の浄化処理水中に、浄化処理水の固
液分離を行なうろ過膜装置がその頂部を水没せしめて浸
され、ろ過膜装置の直下に曝気用気体を供給する散気管
が配置されたものであって、ろ過膜装置は、複数個の膜
モジュールが上下両面開放された方形の箱枠内の上部に
垂直に一定間隔をおいて並列に設けられてなり、各膜モ
ジュールは、一定の厚みと剛性を有する膜支持体の表面
がろ過膜によりおおわれ、内部にろ過処理水流路が形成
されてなり、各ろ過処理水流路の出口側がろ過処理水吸
引管に接続されていて、散気管は、前記方形の箱枠内の
下部に設けられた構成としたものである。
Means for Solving the Problems In order to achieve the above object, the activated sludge treatment device of the present invention has a filtration membrane device for performing solid-liquid separation of purified treated water in purified treated water of raw water in an aeration tank. The filter is a submerged tube that has a diffusing pipe that supplies the gas for aeration just below the filtration membrane device.The filtration membrane device is a rectangular box frame with a plurality of membrane modules open on both upper and lower sides. Each of the membrane modules is installed in parallel vertically on the upper part of the inside, and each membrane module has a surface of a membrane support having a certain thickness and rigidity covered with a filtration membrane, and a filtration-treated water channel is formed inside. The outlet side of each filtered water channel is connected to the filtered water suction pipe, and the air diffuser is provided in the lower part of the rectangular box frame.

作用 上記本発明の構成においては、曝気槽内に送られた原水
は、散気管から膜モジュールの間に吹き出される曝気用
気体により曝気され、浄化処理される。浄化処理水は、
膜モジュールの膜支持体のろ過処理水流路内がろ過処理
水吸引管の方に吸引されることによりろ過膜で固液分離
され、ろ過膜を透過した清浄なろ過処理水はろ過処理水
流路からろ過処理水吸引管を経て外部に取り出される。
他方、ろ過により膜面に付着した汚泥は、膜モジュール
の間を上昇する曝気用気体の気泡のエヤリフト作用によ
り生じた上昇流により膜面から離脱させられて上昇し、
ろ過膜装置の頂部から出て浄化処理水中にもどり、活性
汚泥として循環使用される。なお、膜モジュールが垂直
線に対して傾斜するように設けられている場合には、下
向きの膜面に気泡が衝突して膜面をかく乱するので、汚
泥はより一層膜面から離脱し易くなり、ろ過膜の透過抵
抗が減少する。
Action In the configuration of the present invention described above, the raw water sent into the aeration tank is aerated by the aeration gas blown from the diffuser pipe to the space between the membrane modules, and purified. Purified water is
The inside of the filtration-treated water channel of the membrane support of the membrane module is suctioned toward the filtration-treated water suction pipe to perform solid-liquid separation with the filtration membrane, and the clean filtration-treated water that has passed through the filtration membrane flows from the filtration-treated water channel. It is taken out through the suction pipe of filtered water.
On the other hand, the sludge attached to the membrane surface by filtration is separated from the membrane surface by the upward flow generated by the airlift action of the bubbles of the aeration gas rising between the membrane modules and rises,
It comes out from the top of the filtration membrane device, returns to the purified water, and is recycled as activated sludge. When the membrane module is installed so as to be inclined with respect to the vertical line, air bubbles collide with the downward membrane surface and disturb the membrane surface, so that sludge is more easily separated from the membrane surface. , The permeation resistance of the filtration membrane decreases.

本発明の作用は上記の通りであるが、膜モジュールの間
隔を適当に設定しておけば、原水中に多量の繊維状きよ
う雑物が含まれていても、そのきよう雑物が膜モジュー
ルに絡み付くおそれがなく、汚泥の付着によるろ過膜の
目詰りを防止することができる。また、散気管から吹き
出された気泡は一定の厚みと剛性を有する膜支持体にて
形成された膜モジュールの整流効果により膜モジュール
の間を均一な密度で上昇するので、膜面液流に偏流がな
い。すなわち、均一な流速で上昇する気泡混相流によ
り、全膜面が均一にかく乱される。またこのとき、散気
管を方形の箱枠で囲って設けたことによっても、膜モジ
ュールの位置にかかわらず均一な流速の膜面平行流を供
給でき、箱枠の周辺部においても膜モジュール間の閉塞
を防止できる。したがって、従来の装置のように膜モジ
ュール回転をさせる必要がないため、構造が簡単化さ
れ、装置が安価になる。
The operation of the present invention is as described above. However, if the distance between the membrane modules is appropriately set, even if a large amount of fibrous foreign matter is contained in the raw water, the foreign matter will be removed from the membrane. There is no risk of entanglement with the module, and clogging of the filtration membrane due to sludge adhesion can be prevented. Further, the air bubbles blown out from the air diffuser rise at a uniform density between the membrane modules due to the rectification effect of the membrane module formed by the membrane support having a certain thickness and rigidity, so that the flow on the membrane surface liquid flow is uneven. There is no. That is, the entire film surface is uniformly disturbed by the bubble multiphase flow rising at a uniform flow velocity. Also, at this time, by providing the air diffuser with a rectangular box frame, it is possible to supply a parallel flow on the membrane surface at a uniform flow rate regardless of the position of the membrane module, and even between the membrane modules in the peripheral part of the box frame. Blockage can be prevented. Therefore, since it is not necessary to rotate the membrane module as in the conventional device, the structure is simplified and the device is inexpensive.

実施例 以下、本発明の実施例を第1図〜第6図に基づいて説明
する。
Embodiment An embodiment of the present invention will be described below with reference to FIGS. 1 to 6.

第1実施例 本実施例は、第1図に示すように、曝気槽21内にろ過膜
装置22と散気管23とが設けられてなるものである。曝気
槽21は、原水供給管24から供給される原水25の浄化装置
を行なう槽であって、底部に汚泥引抜ポンプ26が汚泥引
抜管27を介して接続されている。ろ過膜装置22は、原水
25の消化処理により生じた消化処理水28の固液分離を行
なう装置であって、上下両面が開放された方形の箱枠29
内の上部に複数個の膜モジュール30が垂直に一定間隔A
をおいて並列に設けられてなり、消化処理水28中にその
頂部を水没せしめて浸されている。散気管23は、空気等
の酸素を含有する曝気用気体31を膜モジュール30の間に
吹き込む管であって、ろ過膜装置22の直下すなわち方形
の箱枠内の下部に配置され、給気管32を介してブロワー
33に接続されている。34は、ろ過膜装置2からのろ過処
理水35を貯留するろ過処理水槽である。前記膜ジュール
30は、第2図〜第4図に示すように、膜支持体36の両表
面にろ過膜37が接着剤により張り付けられたものであ
る。膜支持体36は、金属(例えばステンレス鋼等)製、
プラスチック製等で、両側縁に凹凸部38を有する方形の
支持板39の上縁に管状部材40と下縁に補強部材41とが固
着されてなり、一定の厚みと剛性を有している。管状部
材40は、凹凸部38の位置に連通孔42が設けられ、分岐管
43を介してろ過処理水吸引管44に接続されている(第1
図参照)。ろ過膜37は、精密ろ過膜、限外ろ過膜等のマ
クロポーラスな平膜である。ろ過膜37と膜支持体36との
間にはろ過処理水流路45(第2図および第3図中の矢印
で示す)が形成され、連通孔42、管状部材40の内部およ
び分岐管43を経てろ過処理水吸引管44に連通している。
ろ過処理水吸引管44は、途中に吸引ポンプ46が接続さ
れ、ろ過処理水槽34に至っている。
First Embodiment In this embodiment, as shown in FIG. 1, an aeration tank 21 is provided with a filtration membrane device 22 and an air diffusing pipe 23. The aeration tank 21 is a tank for purifying the raw water 25 supplied from the raw water supply pipe 24, and a sludge drawing pump 26 is connected to the bottom portion thereof via a sludge drawing pipe 27. The filtration membrane device 22 uses raw water
A device for solid-liquid separation of digested water 28 produced by digestion treatment of 25, which is a rectangular box frame 29 with open upper and lower surfaces.
A plurality of membrane modules 30 are vertically arranged at a fixed interval A in the upper part
They are arranged in parallel with each other and are immersed in the digested water 28 with its top part submerged. The air diffuser 23 is a tube for blowing an aeration gas 31 containing oxygen such as air between the membrane modules 30, and is disposed immediately below the filtration membrane device 22, that is, in the lower part of the rectangular box frame, and the air supply pipe 32 is provided. Blower through
Connected to 33. Reference numeral 34 is a filtered water tank that stores the filtered water 35 from the filtration membrane device 2. The membrane module
As shown in FIGS. 2 to 4, reference numeral 30 is a membrane support 36 having filter membranes 37 attached to both surfaces thereof with an adhesive. The membrane support 36 is made of metal (such as stainless steel),
A tubular member 40 and a reinforcing member 41 are fixed to the upper edge of a rectangular support plate 39, which is made of plastic or the like and has concave and convex portions 38 on both side edges, and has a certain thickness and rigidity. The tubular member 40 is provided with a communication hole 42 at the position of the uneven portion 38, and a branch pipe.
It is connected to the filtered water suction pipe 44 via 43 (first
See figure). The filtration membrane 37 is a macroporous flat membrane such as a microfiltration membrane or an ultrafiltration membrane. A filtration treatment water channel 45 (shown by an arrow in FIGS. 2 and 3) is formed between the filtration membrane 37 and the membrane support 36, and the communication hole 42, the inside of the tubular member 40 and the branch pipe 43 are formed. After that, it communicates with the filtered water suction pipe 44.
A suction pump 46 is connected in the middle of the filtered water suction pipe 44 to reach the filtered water tank 34.

次に、本実施例の作用について説明する。Next, the operation of this embodiment will be described.

原水供給管24から曝気槽21内に送られた原水25は、ブロ
ワー33から給気管32および散気管23を経て膜モジュール
30の間に吹き出される曝気用気体31により曝気され、浄
化処理される。浄化処理水28は、膜モジュール30のろ過
処理水流路45内が吸引ポンプ46により吸引されることに
よりろ過膜37で固液分離され、ろ過膜37を透過した清浄
なろ過処理水35は、ろ過処理水流路45から連通孔42、管
状部材40の内部および分岐管43を経てろ過処理水吸引管
44内に吸引され、ろ過処理水槽34内に送られる。他方、
ろ過によりろ過膜37の膜面に付着した汚泥は、膜モジュ
ール30の間を上昇する曝気用気体31の気泡のエヤリフト
作用により生じた上昇流により膜面から離脱させられて
上昇し、ろ過膜装置22の頂部から出て浄化処理水28中に
もどり、曝気槽21内に生じている浄化処理水28の循環流
B(第1図参照)に乗ってろ過膜装置22の下方に至り、
再び活性汚泥として循環使用される。なお、曝気槽21内
の余剰汚泥は、汚泥引抜ポンプ26により汚泥引抜管27を
経て外部に引き抜かれる。
Raw water 25 sent from the raw water supply pipe 24 into the aeration tank 21 passes through a blower 33, an air supply pipe 32 and an air diffusing pipe 23 to a membrane module.
It is aerated by the aeration gas 31 blown out during 30 and is purified. The purified treated water 28 is solid-liquid separated by the filtration membrane 37 by sucking the inside of the filtration treated water flow path 45 of the membrane module 30 by the suction pump 46, and the clean filtered treatment water 35 that has passed through the filtration membrane 37 is filtered. Filtered water suction pipe from treated water channel 45 through communication hole 42, inside tubular member 40 and branch pipe 43
It is sucked into 44 and sent into the filtered water tank 34. On the other hand,
The sludge attached to the membrane surface of the filtration membrane 37 by filtration is separated from the membrane surface by the ascending flow generated by the airlift action of the bubbles of the aeration gas 31 rising between the membrane modules 30 and rises, and the filtration membrane device It comes out from the top of 22 and returns to the purified water 28, rides on the circulating flow B (see FIG. 1) of the purified water 28 generated in the aeration tank 21, and reaches below the filtration membrane device 22,
It is recycled again as activated sludge. The excess sludge in the aeration tank 21 is drawn outside by the sludge drawing pump 26 through the sludge drawing pipe 27.

本実施例は上記のように作用するが、膜モジュール30の
間隔Aを適当に設定しておけば、原水25中に多量の繊維
状きよう雑物が含まれていても、そのきよう雑物が膜モ
ジュール30に絡み付くおそれがなく、汚泥の付着による
ろ過膜37の目詰りは生じない。また、散気管23から吹き
出された気泡は一定の厚みと剛性を有して形成された膜
モジュール30の整流効果により膜モジュール30の間を均
一な密度で上昇するので、膜面液流に偏流がない。すな
わち、均一な流速で上昇する気泡混相流により、全膜面
が均一にかく乱される。またこのとき、散気管を方形の
内部に設けたことによっても均一な流速の膜面平行流を
供給でき、箱枠の周辺部においても膜モジュール間の閉
塞を防止できる。したがって、従来の装置のように膜モ
ジュール30を回転させる必要がないため、構造が簡単で
あり、装置は安価である。
This embodiment operates as described above, but if the interval A of the membrane module 30 is set appropriately, even if the raw water 25 contains a large amount of fibrous foreign matters, it will be There is no risk that substances will become entangled in the membrane module 30, and clogging of the filtration membrane 37 due to adhesion of sludge does not occur. Further, the air bubbles blown out from the air diffuser 23 rise at a uniform density between the membrane modules 30 due to the rectification effect of the membrane module 30 formed to have a constant thickness and rigidity, so that the flow on the membrane surface liquid flow is uneven. There is no. That is, the entire film surface is uniformly disturbed by the bubble multiphase flow rising at a uniform flow velocity. Further, at this time, by providing the air diffuser inside the rectangular shape, it is possible to supply a parallel flow on the membrane surface with a uniform flow rate, and it is possible to prevent clogging between the membrane modules even in the peripheral portion of the box frame. Therefore, since it is not necessary to rotate the membrane module 30 as in the conventional device, the structure is simple and the device is inexpensive.

第2実施例 本実施例は、第5図に示すように、膜モジュール30が垂
直線に対して傾斜するように設けられていること以外
は、第1実施例と全く同じ構成としたものである。した
がって、その作用効果も第1実施例とほとんど異ならな
いが、膜モジュール30の下向きの膜面に気泡が衝突して
膜面をかく乱するので、汚泥はより一層膜面から離脱し
易くなり、ろ過膜37の透過抵抗が減少するという利点が
ある。
Second Embodiment This embodiment has exactly the same configuration as the first embodiment except that the membrane module 30 is provided so as to be inclined with respect to the vertical line as shown in FIG. is there. Therefore, the action and effect thereof are almost the same as those of the first embodiment, but the bubbles collide with the downward membrane surface of the membrane module 30 and disturb the membrane surface, so that the sludge is more easily separated from the membrane surface and the filtration is performed. The advantage is that the permeation resistance of the membrane 37 is reduced.

その他の実施例 (1)膜支持体36は、金属またはプラスチック製のネッ
ト状のもの、多孔質の板状のもの等でもよく、また、そ
の凹凸部38は、第6図に示すように、凹凸のある板を2
枚反対向きに重ねて形成してもよい。
Other Examples (1) The membrane support 36 may be a net-like one made of metal or plastic, a porous plate-like one or the like, and the uneven portion 38 thereof is, as shown in FIG. 2 uneven boards
They may be formed by stacking them in opposite directions.

(2)ろ過膜37は、第2実施例の場合には膜支持体36の
片面にのみ張り付けてもよい。また、第7図に示すよう
に、ろ過膜37を袋状に形成して膜支持体36に被せ、開口
部47を止めバンド48により管状部材40の固定してもよ
く、ろ過膜37の交換が容易になる。また、第8図〜第9
図に示すように、膜支持体36を中実体で形成してもよ
い。
(2) In the case of the second embodiment, the filtration membrane 37 may be attached to only one side of the membrane support 36. Further, as shown in FIG. 7, the filtration membrane 37 may be formed in a bag shape and covered with the membrane support 36, and the opening 47 may be fixed with the band 48 to fix the tubular member 40. Will be easier. Moreover, FIGS.
As shown, the membrane support 36 may be formed of a solid body.

(3)ろ過処理水吸引管44は、膜モジュール30の上縁の
みならず、両側縁や下縁に複数本接続してもよい。
(3) A plurality of filtration water suction pipes 44 may be connected not only to the upper edge of the membrane module 30 but also to both side edges and lower edges.

発明の効果 以上説明したように本発明によれば、膜モジュールの間
隔を適当に設定することができるので、原水中に多量の
繊維状きよう雑物が含まれていても、そのきよう雑物が
膜モジュールに絡み付くおそれがない。したがって、汚
泥の付着によるろ過膜の目詰りを防止することができ
る。また、ろ過膜装置の直下に配置された散気管から吹
き出される気泡が一定の厚みと剛性を有して形成された
膜モジュールの整流効果により膜モジュールの間を均一
な密度で上昇するので、膜面液流に偏流がない。すなわ
ち、均一な流速で上昇する気泡混相流により、全膜面が
均一にかく乱される。またこのとき、散気管を方形の箱
枠で囲って設けたことによっても、膜モジュールの位置
にかかわらず均一な流速の膜面平行流を供給でき、箱枠
の周辺部においても膜モジュール間の閉塞を防止でき
る。したがって、従来の装置のように膜モジュールを回
転させる必要がないため、構造が簡単化され、装置が安
価になる。
EFFECTS OF THE INVENTION As described above, according to the present invention, the interval between the membrane modules can be set appropriately, so that even if a large amount of fibrous foreign matters are contained in the raw water, the fine foreign matters are mixed. There is no risk of objects getting entangled in the membrane module. Therefore, it is possible to prevent clogging of the filtration membrane due to adhesion of sludge. Further, the bubbles blown out from the air diffusing tube arranged immediately below the filtration membrane device rises at a uniform density between the membrane modules due to the rectification effect of the membrane module formed with a certain thickness and rigidity, There is no drift in the liquid flow on the membrane surface. That is, the entire film surface is uniformly disturbed by the bubble multiphase flow rising at a uniform flow velocity. Also, at this time, by providing the air diffuser with a rectangular box frame, it is possible to supply a parallel flow on the membrane surface at a uniform flow rate regardless of the position of the membrane module, and even between the membrane modules in the peripheral part of the box frame. Blockage can be prevented. Therefore, since it is not necessary to rotate the membrane module as in the conventional device, the structure is simplified and the device is inexpensive.

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

第1図は本発明の第1実施例の回路図、第2図は本発明
の膜モジュールの断面図、第3図は第2図のX−X矢視
断面図、第4図は第2図の膜モジュールの斜視図、第5
図は本発明の第2実施例の回路図、第6図は本発明の膜
支持体の他の実施例の部分断面図、第7図は本発明のろ
過膜の他の実施例の説明図、第8図は本発明の膜支持体
の他の実施例の部分断面図、第9図は第8図のY−Y矢
視断面図、第10図は従来の装置の一例を示す回路図であ
る。 21…曝気槽、22…ろ過膜装置、23…散気管、25…原水、
28…浄化処理水、30…膜モジュール、31…曝気用気体、
36…膜支持体、37…ろ過膜、44…ろ過処理水吸引管、45
…ろ過処理水流路、A…一定間隔。
1 is a circuit diagram of the first embodiment of the present invention, FIG. 2 is a sectional view of the membrane module of the present invention, FIG. 3 is a sectional view taken along the line XX of FIG. 2, and FIG. Perspective view of the membrane module in the figure, fifth
FIG. 7 is a circuit diagram of a second embodiment of the present invention, FIG. 6 is a partial sectional view of another embodiment of the membrane support of the present invention, and FIG. 7 is an explanatory view of another embodiment of the filtration membrane of the present invention. FIG. 8 is a partial sectional view of another embodiment of the membrane support of the present invention, FIG. 9 is a sectional view taken along the line YY of FIG. 8, and FIG. 10 is a circuit diagram showing an example of a conventional device. Is. 21 ... Aeration tank, 22 ... Filtration membrane device, 23 ... Air diffuser, 25 ... Raw water,
28 ... Purified water, 30 ... Membrane module, 31 ... Aeration gas,
36 ... Membrane support, 37 ... Filtration membrane, 44 ... Filtration-treated water suction tube, 45
... Filtered water flow path, A ... at regular intervals.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】曝気槽内の原水の浄化処理水中に、浄化処
理水の固液分離を行うろ過膜装置がその頂部を水没せし
めて浸され、ろ過膜装置の直下に曝気用気体を供給する
散気管が配置されたものであって、ろ過膜装置は、複数
個の膜モジュールが上下両面開放された方形の箱枠内の
上部に垂直に一定間隔をおいて並列に設けられてなり、
各膜モジュールは、一定の厚みと剛性を有する膜支持体
の表面がろ過膜によりおおわれ、内部にろ過処理水流路
が形成されてなり、各ろ過処理水流路の出口側がろ過処
理水吸引管に接続されていて、散気管は、前記方形の箱
枠内の下部に設けられたことを特徴とする活性汚泥処理
装置。
1. A filtration membrane device for solid-liquid separation of purified treatment water is immersed in the purified water of the raw water in the aeration tank with its top submerged, and an aeration gas is supplied directly below the filtration membrane device. An air diffuser is arranged, and the filtration membrane device comprises a plurality of membrane modules arranged vertically in parallel at regular intervals in an upper part of a rectangular box frame whose upper and lower surfaces are open.
In each membrane module, the surface of a membrane support having a certain thickness and rigidity is covered with a filtration membrane, and a filtration-treated water channel is formed inside, and the outlet side of each filtration-treated water channel is connected to a filtration-treated water suction pipe. The activated sludge treatment device is characterized in that the air diffuser is provided in the lower part of the rectangular box frame.
JP63238297A 1988-09-22 1988-09-22 Activated sludge treatment equipment Expired - Lifetime JPH0720592B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63238297A JPH0720592B2 (en) 1988-09-22 1988-09-22 Activated sludge treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63238297A JPH0720592B2 (en) 1988-09-22 1988-09-22 Activated sludge treatment equipment

Publications (2)

Publication Number Publication Date
JPH0286893A JPH0286893A (en) 1990-03-27
JPH0720592B2 true JPH0720592B2 (en) 1995-03-08

Family

ID=17028103

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63238297A Expired - Lifetime JPH0720592B2 (en) 1988-09-22 1988-09-22 Activated sludge treatment equipment

Country Status (1)

Country Link
JP (1) JPH0720592B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103351057A (en) * 2013-07-30 2013-10-16 居文钟 Full-brush type non-backwashing single-net and double-net dynamic membrane micro net assemblies

Families Citing this family (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04271816A (en) * 1991-02-27 1992-09-28 Ebara Infilco Co Ltd Filter/seperator
JP3023928B2 (en) * 1991-03-07 2000-03-21 株式会社クボタ Solid-liquid separator
JPH04313400A (en) * 1991-04-11 1992-11-05 Kubota Corp Sludge treating equipment
TW255835B (en) * 1994-01-07 1995-09-01 Kubota Kk Filtration membrane module
US5451317A (en) * 1994-09-08 1995-09-19 Kubota Corporation Solid-liquid separator
TW283657B (en) 1995-03-31 1996-08-21 Mitsui Eng & Shipbuilding Co Membrane device and its processing device
JP3160609B2 (en) * 1995-03-31 2001-04-25 三造環境エンジニアリング株式会社 Membrane equipment and membrane treatment equipment
JP3866399B2 (en) * 1997-12-16 2007-01-10 住友重機械工業株式会社 Membrane filtration device and operation method thereof
JP5728075B2 (en) * 2013-12-28 2015-06-03 志摩環境事業協業組合 Immersion membrane separator and filtration method using such an immersion membrane separator

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61129094A (en) * 1984-11-26 1986-06-17 Nitto Electric Ind Co Ltd Apparatus for treating membrane

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103351057A (en) * 2013-07-30 2013-10-16 居文钟 Full-brush type non-backwashing single-net and double-net dynamic membrane micro net assemblies
CN103351057B (en) * 2013-07-30 2014-08-06 居文钟 Full-brush type non-backwashing single-net and double-net dynamic membrane micro net assemblies

Also Published As

Publication number Publication date
JPH0286893A (en) 1990-03-27

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