JPH0286893A - Activated sludge treating device - Google Patents
Activated sludge treating deviceInfo
- Publication number
- JPH0286893A JPH0286893A JP63238297A JP23829788A JPH0286893A JP H0286893 A JPH0286893 A JP H0286893A JP 63238297 A JP63238297 A JP 63238297A JP 23829788 A JP23829788 A JP 23829788A JP H0286893 A JPH0286893 A JP H0286893A
- Authority
- JP
- Japan
- Prior art keywords
- membrane
- filtration
- aeration
- treated water
- 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.)
- Granted
Links
- 239000010802 sludge Substances 0.000 title claims abstract description 27
- 239000012528 membrane Substances 0.000 claims abstract description 132
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 73
- 238000001914 filtration Methods 0.000 claims abstract description 49
- 238000005273 aeration Methods 0.000 claims abstract description 34
- 239000007788 liquid Substances 0.000 claims abstract description 12
- 239000008213 purified water Substances 0.000 claims description 13
- 238000000926 separation method Methods 0.000 claims description 4
- 230000000630 rising effect Effects 0.000 abstract description 3
- 238000004140 cleaning Methods 0.000 abstract 1
- 239000011248 coating agent Substances 0.000 abstract 1
- 238000000576 coating method Methods 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 12
- 230000000694 effects Effects 0.000 description 6
- 239000012510 hollow fiber Substances 0.000 description 6
- 239000012535 impurity Substances 0.000 description 6
- 238000010586 diagram Methods 0.000 description 4
- 239000007787 solid Substances 0.000 description 4
- 238000000605 extraction Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 239000000853 adhesive Substances 0.000 description 1
- 230000001070 adhesive effect Effects 0.000 description 1
- 238000013019 agitation Methods 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 230000029087 digestion Effects 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- -1 etc.) Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000003014 reinforcing effect Effects 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 239000010935 stainless steel Substances 0.000 description 1
- 238000000108 ultra-filtration Methods 0.000 description 1
- 230000002485 urinary effect Effects 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
- Activated Sludge Processes (AREA)
- Filtration Of Liquid (AREA)
Abstract
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。DETAILED DESCRIPTION OF THE INVENTION Field of Industrial Application The present invention relates to an activated sludge treatment apparatus that performs digestion treatment of organic wastewater and solid-liquid separation using a filtration membrane in a single tank.
従来の技術
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1O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−
7から散気管5を経て浄化処理水3中に吹き出される。2. Description of the Related Art In general, in this type of activated sludge treatment equipment, the filter membranes become clogged with sludge during use, and various proposals have been made to prevent this clogging. For example, the apparatus shown in FIG. 1O is one in which a hollow fiber membrane 4 is suspended and immersed in purified water 3 of raw water 2 in an aeration tank 1, and an aeration pipe 5 is placed directly below the hollow fiber membrane 4. It is. Aeration air 6 necessary for purifying raw water 2 is supplied by a blower.
7 and is blown out into the purified water 3 via the aeration pipe 5.
浄化処理水3は、吸引ポンプ8により中空糸@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を呼び、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設穴を貫設して一定間隔で並
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。The purified water 3 is separated into solid and liquid by being sucked into the hollow holes of the hollow fibers @4 by the suction pump 8, and the purified water 3 is separated into solid and liquid by the suction pump 8.
The clean filtered water 9 that has passed through is sent to the filtered water tank 10. On the other hand, excess sludge 11 accumulated in the aeration tank 1 is drawn out to the outside at a suitable time. If this hollow fiber membrane 4 is subjected to continuous suction, clogging will cause clogging, which will become unrecoverable in a short period of time, so rapid clogging can be prevented by performing intermittent suction and periodically releasing the pressure. , which enables stable operation over a long period of time. Furthermore, the apparatus disclosed in Japanese Patent Application Laid-Open No. 61-274799 is equipped with a filtration means within the processing tank. This filtration means consists of a plurality of filtration plates each having a hole in the center, which are arranged in parallel at regular intervals through a hollow rotating shaft with a pre-pierced hole, and are rotated together by the drive mechanism of the hollow rotating shaft. Aeration means for discharging gas is provided between the plates, and the filter plate is a membrane support having filtered water passages, with semipermeable membranes covering both sides. The raw water sent into the treatment tank is aerated and digested with gas from the aeration means. The digested water is filtered by the semipermeable membrane of the rotating filter plate, and the clean filtered water is taken out to the outside through the filtered water passage of the membrane support and the hollow part of the hollow rotating shaft. On the other hand, the sludge that has adhered to the membrane surface due to filtration is removed from the membrane surface by the agitation action of the aeration gas itself and the purified water of the gas. The membrane surface passes through the gas discharge pipe of the aeration means every time the filtration means rotates once, so
Since it is cleaned in extremely short cycles, it is always kept clean and can be used stably for a long period of time.
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。Excess sludge accumulated in the treatment tank is discharged 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。Problem to be Solved by the Invention However, when raw water contains a large amount of fibrous impurities, in the former conventional device, the fibrous impurities are transferred to the hollow fiber membrane. There was a problem in that the hollow fiber membranes 4 became entangled with each other and eventually became like a stick of sludge, completely clogging the hollow fiber membranes 4. In addition, in the latter device, there was a problem in that fibrous impurities wrapped around the hollow rotating shaft and eventually blocked the space between the filter plates. Furthermore, in the latter device, since the gas-liquid multiphase flow is structured to cause uneven flow between the filter plates, the flow velocity on the membrane surface becomes non-uniform, and there is a possibility that a portion with low membrane permeation performance may occur. Therefore, in order to prevent this, the filtration means is rotated. Therefore.
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。There was a problem that the structure was not only complicated but also 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。The present invention aims to solve these problems by improving the conventional device.
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
モジュールが垂直に、または、垂直線に対して傾斜する
ように、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、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る構
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 apparatus of the present invention has a filtration membrane device for solid-liquid separation of the purified water in the purified raw water in the aeration tank. The membrane is submerged in water, and an aeration pipe is placed directly below the filtration membrane device to supply aeration gas. Each membrane module has a membrane support whose surface is covered with a filtration membrane, and a filtration water flow path formed inside the membrane module. The outlet side of the channel is connected to the filtered water suction pipe.
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
水吸引管の方に吸弓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。Effect: In the configuration of the present invention described above, the raw water sent into the aeration tank is aerated and purified by the aeration gas blown out between the membrane modules from the aeration tube. Purified water is
The inside of the filtered water flow path of the membrane support of the membrane module is sucked toward the filtered water suction pipe, where it is separated into solid and liquid by the filtration membrane, and the clean filtered water that has passed through the filtration membrane is transferred to the filtered water flow path. The filtered water is taken out to the outside through a suction pipe.
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。On the other hand, the sludge adhering to the membrane surface due to filtration is removed from the membrane surface and rises due to the upward flow generated by the air lift action of the aeration gas bubbles rising between the membrane modules.
It exits from the top of the filtration membrane device and returns to the purified water, where it is recycled and used as activated sludge. In addition, if the membrane module is installed so as to be inclined with respect to the vertical line, air bubbles collide with the downward facing membrane surface and disturb the membrane surface, making it easier for sludge to separate 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。The effect of the present invention is as described above, but if the spacing between the membrane modules is set appropriately, 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 it getting tangled with the module.
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6したがって、従来の装置のように膜モジユール
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。It is possible to prevent clogging of the filtration membrane due to adhesion of sludge. Furthermore, the air bubbles blown out from the diffuser tube rise between the membrane modules at a uniform density due to the rectification effect of the membrane modules, so there is no unbalanced flow in the liquid flow on the membrane surface. In other words, the entire membrane surface is uniformly disturbed by the bubble multiphase flow that rises at a uniform flow rate.6 Therefore, there is no need to rotate the membrane module as in conventional devices, which simplifies the structure and makes the device inexpensive. become.
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。Embodiments Hereinafter, embodiments of the present invention will be explained based on 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2
5の浄化処理を行なう槽°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の直下に配置され、給気管32を介して
ブロワ−33に接続されている。34は、ろ過膜装置2
2からのろ過処理水35を貯留するろ過処理水槽である
。First Embodiment In this embodiment, as shown in FIG. 1, a filtration membrane device 22 and an aeration pipe 23 are provided in an aeration tank 21. The aeration tank 21 is supplied with raw water 2 from a raw water supply pipe 24.
A sludge drawing pump 26 is connected to the bottom of the tank 5 through a sludge drawing pipe 27. The filtration membrane device 22 is a device that performs solid-liquid separation of digested water 28 produced by digesting raw water 25. A plurality of membrane modules 30 are arranged vertically in a rectangular box frame 29 that is open on both upper and lower sides. are arranged in parallel at a constant interval A, and are immersed with their tops submerged in the digested water 28. The aeration pipe 23 is a pipe that blows an aeration gas 31 containing oxygen such as air between the membrane modules 30,
It is arranged directly below the filtration membrane device 22 and connected to a blower 33 via an air supply pipe 32. 34 is the filtration membrane device 2
This is a filtered water tank that stores filtered water 35 from No. 2.
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4
0と下縁に補強部材41とが固着されてなる。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。The membrane joule 30, as shown in FIGS. 2 to 4,
A filtration membrane 37 is attached to both surfaces of a membrane support 36 with an adhesive. The membrane support 36 is made of metal (for example, stainless steel, etc.), plastic, etc., and has a tubular member 4 attached to the upper edge of a rectangular support plate 39 having uneven parts 38 on both side edges.
0 and a reinforcing member 41 is fixed to the lower edge. The tubular member 40 is provided with a communication hole 42 at the position of the uneven portion 38, and is connected to a filtered water suction pipe 44 via a branch pipe 43 (see FIG. 1). The filtration membrane 37 is a macroporous flat membrane such as a precision filtration membrane or an ultrafiltration membrane. A filtered water flow path 45 (indicated by arrows in FIGS. 2 and 3) is formed between the filtration membrane 37 and the membrane support 36, and communicates with the communication hole 42, the inside of the tubular member 40, and the branch pipe 43. It communicates with the filtered water suction pipe 44 through the filter. The filtered water suction pipe 44 has a suction pump 46 connected therebetween and reaches 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 explained.
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−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4
6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3
0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。The raw water 25 sent from the raw water supply pipe 24 into the aeration tank 21 is aerated and purified by the aeration gas 31 blown out between the membrane modules 30 from the blower 33 via the air supply pipe 32 and the aeration pipe 23. Ru. The purified water 28 is supplied to the filtered water flow path 45 of the membrane module 30 by the suction pump 4.
The clean filtered water 35 that has passed through the filter membrane 37 is filtered through the filter membrane 37 through the communication hole 42, the inside of the tubular member 40, and the branch pipe 43. The filtered water is then sucked into the filtered water suction pipe 44 and sent into the filtered water tank 34. On the other hand, the sludge that has adhered to the membrane surface of the filtration membrane 37 due to filtration is removed from the membrane module 3.
Due to the upward flow generated by the air lift action of the bubbles of the aeration gas 31 rising between
Returning inside, the purified water 28 generated in the aeration tank 21
It reaches below the filtration membrane device 22 along the circulation flow B (see Fig. 1), and is recycled and used again as activated sludge. In addition,
Excess sludge in the aeration tank 21 is extracted to the outside via a sludge extraction pipe 27 by a sludge extraction pump 26.
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。This embodiment works as described above, except that the membrane module 30
If the interval A is set appropriately, even if the raw water 25 contains a large amount of fibrous impurities.
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和流により、全膜面が均
一にかく乱される。There is no risk that the foreign matter will become entangled with the membrane module 30, and the filtration membrane 37 will not be clogged due to adhesion of sludge. Furthermore, the air bubbles blown out from the air diffuser 23 rise between the membrane modules 30 at a uniform density due to the rectification effect of the membrane modules 30, so that there is no unbalanced flow in the liquid flow on the membrane surface. That is, the entire membrane surface is uniformly disturbed by the bubble mixing flow that rises at a uniform flow rate.
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。Therefore, unlike conventional devices, there is no need to rotate the membrane module 30, so 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 structure 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. be. Therefore, the operation and effect are almost the same as in the first embodiment, but the air bubbles collide with the downward facing membrane surface of the membrane module 30 and disturb the membrane surface, making it easier for sludge to separate from the membrane surface and filtration. The advantage is that the permeation resistance of 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 metal or plastic net-like material, a porous plate-like material, etc.
The uneven portion 38 may be formed by stacking two uneven plates in opposite directions, as shown in FIG.
(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4
0の固定してもよく、ろ過膜37の交換が容易になる。(2) In the case of the second embodiment, the filtration membrane 37 may be attached only to one side of the membrane support 36. Further, as shown in FIG. 7, the filtration membrane 37 is formed into a bag shape and the membrane support 36 is
and the opening 47 is secured with a stopper band 48 to secure the tubular member 4.
It may be fixed at 0, making it easier to replace the filtration membrane 37.
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。Further, as shown in FIGS. 8 and 9, 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3゜
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 filtered water suction pipes 44 may be connected not only to the upper edge of the membrane module 3° but also to both side edges and the lower edge.
発明の詳細
な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。As described in detail, according to the present invention, the spacing between membrane modules can be set appropriately.
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
る気泡混和流により、全膜面が均一にかく乱される。Even if the raw water contains a large amount of fibrous impurities, there is no risk of the impurities getting entangled with the membrane module.
Therefore, clogging of the filtration membrane due to adhesion of sludge can be prevented. In addition, the air bubbles blown out from the air diffuser placed directly below the filtration membrane device rise between the membrane modules at a uniform density due to the rectification effect of the membrane modules.
There is no deviation in the membrane surface liquid flow, that is, the bubble mixing flow rises at a uniform flow rate, and the entire membrane surface is uniformly disturbed.
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。Therefore, unlike conventional devices, there is no need to rotate the membrane module, which simplifies the structure and reduces the cost of the device.
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・・・−定間隔
。
代理人 森 本 義 私
用1
2/ −、4’L−槽
22− う通繰像↑
23、−、朕馬皆
25−・−原水
2i−シシヒ処理永
図
8θ 16.膿壬、シ゛ニール
31・・−III気吊気本
41.−う@M永永別引
責・−一一楚聞埠
第2図
第
図
30−一一膿モシ”エール
3A04月東支持体
4左
う遁膿
ろ過処理女流路−
第S図
第1ρ図
第4図
/ゴ
ニ:7
図
第7図
第1
図FIG. 1 is a circuit diagram of the first embodiment of the present invention, FIG. 2 is a cross-sectional view of the membrane module of the present invention, FIG. 3 is a cross-sectional view taken along the line xx in FIG. 2, and FIG. Perspective view of the membrane module in Figure 5.
The figure is a circuit diagram of the 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 diagram 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 Y-Y arrow in FIG. 8, and FIG. 10 is a circuit diagram showing an example of a conventional device. It is. 21... Aeration tank, 22... Filtration membrane device, 23...
Diffusion pipe, 25... Raw water, 28... Purified water, 30
...Membrane module, 31...Aeration gas, 36...
- Membrane support, 37...filtration membrane, 44...filtered water suction pipe, 45...filtered water channel, A...-regular interval. Agent Yoshi Morimoto Private 1 2/ -, 4'L-tank 22- Utsu repeating image ↑ 23, -, Touma Minami 25 - - Raw water 2i - Shishihi treatment Eiji 8θ 16. Yujin, Shinir 31...-III Qi Suikihon 41. -U@M Eiyobetsu Responsibility - 11 Sounbu Figure 2 Figure 30 - 11 Pus Moshi Ale 3A0 April East Support 4 Left Urinary Pus Filtration Processing Female Channel- Figure S Figure 1 ρ Figure 4 Figure/Goni: 7 Figure 7 Figure 1
Claims (1)
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、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
れていることを特徴とする活性汚泥処理装置。 2、膜モジュールが、垂直線に対して傾斜するように設
けられている請求項1記載の活性汚泥処理装置。[Claims] 1. A filtration membrane device for solid-liquid separation of purified water is immersed in the purified water in the aeration tank with its top submerged, and aeration gas is placed directly below the filtration membrane device. A filtration membrane device has a plurality of membrane modules arranged vertically in parallel at regular intervals, and each membrane module has a membrane support whose surface is It is covered with a filtration membrane, and a filtered water flow path is formed inside.
An activated sludge treatment device characterized in that the outlet side of each filtered water flow path is connected to a filtered water suction pipe. 2. The activated sludge treatment apparatus according to claim 1, wherein the membrane module is provided so as to be inclined with respect to a vertical line.
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 true JPH0286893A (en) | 1990-03-27 |
JPH0720592B2 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 (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH04271816A (en) * | 1991-02-27 | 1992-09-28 | Ebara Infilco Co Ltd | Filter/seperator |
JPH04281828A (en) * | 1991-03-07 | 1992-10-07 | Kubota Corp | Solid-liquid separator |
JPH04313400A (en) * | 1991-04-11 | 1992-11-05 | Kubota Corp | Sludge treating equipment |
EP0662341A1 (en) * | 1994-01-07 | 1995-07-12 | Kubota Corporation | Filtration membrane module |
EP0700713A1 (en) * | 1994-09-08 | 1996-03-13 | Kubota Corporation | Solid-liquid separator |
EP0734758A1 (en) | 1995-03-31 | 1996-10-02 | Mitsui Petrochemical Industries, Ltd. | Membrane device having means for charging the membranes |
JPH08323165A (en) * | 1995-03-31 | 1996-12-10 | Mitsui Zosen Eng Kk | Membrane device and membrane treating device |
GB2332380A (en) * | 1997-12-16 | 1999-06-23 | Sumitomo Heavy Industries | Cleaning membrane filters |
JP2014057967A (en) * | 2013-12-28 | 2014-04-03 | Shima Kankyo Jigyo Kyogyo Kumiai | Immersion-type membrane separation apparatus and filtration method using the immersion-type membrane separation apparatus |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
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 |
Citations (1)
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 |
-
1988
- 1988-09-22 JP JP63238297A patent/JPH0720592B2/en not_active Expired - Lifetime
Patent Citations (1)
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 (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH04271816A (en) * | 1991-02-27 | 1992-09-28 | Ebara Infilco Co Ltd | Filter/seperator |
JPH04281828A (en) * | 1991-03-07 | 1992-10-07 | Kubota Corp | Solid-liquid separator |
JPH04313400A (en) * | 1991-04-11 | 1992-11-05 | Kubota Corp | Sludge treating equipment |
EP0662341A1 (en) * | 1994-01-07 | 1995-07-12 | Kubota Corporation | Filtration membrane module |
EP0700713A1 (en) * | 1994-09-08 | 1996-03-13 | Kubota Corporation | Solid-liquid separator |
EP0734758A1 (en) | 1995-03-31 | 1996-10-02 | Mitsui Petrochemical Industries, Ltd. | Membrane device having means for charging the membranes |
JPH08323165A (en) * | 1995-03-31 | 1996-12-10 | Mitsui Zosen Eng Kk | Membrane device and membrane treating device |
GB2332380A (en) * | 1997-12-16 | 1999-06-23 | Sumitomo Heavy Industries | Cleaning membrane filters |
GB2332380B (en) * | 1997-12-16 | 2001-04-25 | Sumitomo Heavy Industries | Membrane filter apparatus and method for operating the membrane filter apparatus |
JP2014057967A (en) * | 2013-12-28 | 2014-04-03 | Shima Kankyo Jigyo Kyogyo Kumiai | Immersion-type membrane separation apparatus and filtration method using the immersion-type membrane separation apparatus |
Also Published As
Publication number | Publication date |
---|---|
JPH0720592B2 (en) | 1995-03-08 |
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