JPH0975970A - Dipping type membrane separation device using hollow fiber membrane - Google Patents

Dipping type membrane separation device using hollow fiber membrane

Info

Publication number
JPH0975970A
JPH0975970A JP7252050A JP25205095A JPH0975970A JP H0975970 A JPH0975970 A JP H0975970A JP 7252050 A JP7252050 A JP 7252050A JP 25205095 A JP25205095 A JP 25205095A JP H0975970 A JPH0975970 A JP H0975970A
Authority
JP
Japan
Prior art keywords
hollow fiber
membrane
fiber membrane
tank
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.)
Pending
Application number
JP7252050A
Other languages
Japanese (ja)
Inventor
Mikio Kitagawa
幹夫 北川
Akishi Hori
晃士 堀
Tetsuro Fukase
哲朗 深瀬
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.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water 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 Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP7252050A priority Critical patent/JPH0975970A/en
Publication of JPH0975970A publication Critical patent/JPH0975970A/en
Pending 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

Landscapes

  • Biological Treatment Of Waste Water (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide such a dipping type membrane separation device that the total concn. of the sludge held in the treating tank is increased, permeation of the hollow fiber membrane does not decrease even when the device is operated with a high load, high-quality treated water can be stably obtd, and maintenance of the device is easy because the frequency for washing of the hollow fiber membrane is low. SOLUTION: This dipping type membrane separation device has such a structure that a membrane element 12 having lots of hollow fiber membranes 13 is made to stand in a water containing activated sludge in a treating tank 10, an air-lifted upward flow which rises and touches the hollow fiber membranes is generated by bubbles diffused from a diffusion pipe 7 in the bottom of the tank, and that the permeated water through the membranes of the hollow fiber membrane is recovered. In this device, a cleaning member 20 on which activated sludge can deposit is arranged in the water in the tank in such a manner that the member 20 is vibrated by the air-lifted flow in the tank and is brought into contact with the hollow fiber membrane 13.

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】この発明は、多数本の中空糸
膜を有する膜エレメントを用いた活性汚泥処理装置とし
ての浸漬型膜分離装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an immersion type membrane separation device as an activated sludge treatment device using a membrane element having a large number of hollow fiber membranes.

【0002】[0002]

【従来の技術】排水処理設備のコンパクト化と、高度な
処理水を安定して得るために、活性汚泥処理装置の処理
槽内の活性汚泥を含む水中に、多数本の中空糸膜を有す
る膜エレメントを立て、槽内底部の散気管が散気する気
泡により中空糸膜に接触して上昇するエアリフト上向流
を生じさせ、中空糸膜の膜を透過した透過水を採水する
中空糸膜による浸漬型膜分離装置が開発されている。活
性汚泥処理に中空糸膜を有する膜エレメントを浸漬する
主な目的は、固液分離を容易にし、その結果、槽内の水
中に浮遊している活性汚泥の濃度を高めることにある。
即ち、従来の活性汚泥を用いた沈殿槽による自然沈降の
固液分離に比較して中空糸膜を有する膜エレメントを浸
漬し、中空糸膜の膜を透過して中空部に得られる透過水
を採水すると、槽内の活性汚泥の濃度を従来の2倍以上
の10000mg/立以上まで高めることが可能であ
り、その結果、負荷量を高めた運転が行える。
2. Description of the Related Art A membrane having a large number of hollow fiber membranes in water containing activated sludge in a treatment tank of an activated sludge treatment device in order to make wastewater treatment equipment compact and stably obtain advanced treated water. A hollow fiber membrane that raises an element, causes an air lift upward flow that rises by contacting the hollow fiber membrane with air bubbles diffused by the air diffuser at the bottom of the tank, and collecting permeated water that has permeated the hollow fiber membrane. An immersion type membrane separation device has been developed. The main purpose of immersing the membrane element having a hollow fiber membrane in the activated sludge treatment is to facilitate solid-liquid separation and, as a result, increase the concentration of the activated sludge suspended in water in the tank.
That is, as compared with the conventional solid-liquid separation of natural sedimentation in a sedimentation tank using activated sludge, the membrane element having a hollow fiber membrane is immersed, and the permeated water obtained by permeating the membrane of the hollow fiber membrane to the hollow part is obtained. When water is sampled, the concentration of activated sludge in the tank can be increased to more than double that of the conventional method, to 10,000 mg / cubic or more, and as a result, operation with an increased load can be performed.

【0003】[0003]

【発明が解決しようとする課題】しかし、槽内に活性汚
泥を高濃度に保持すると、浸漬した膜エレメントの中空
糸の表面に付着する汚泥が増加し、中空糸膜を透過する
透過水の量が低減する。通常、中空糸膜を透過する透過
水の水量が大幅に減少しない活性汚泥の濃度は1000
0mg/立付近であるとされている。又、槽内の活性汚
泥濃度を上記10000mg/立付近に設定して運転を
行っても、負荷量を10kg−BOD/m3 ・日以上の
高負荷域で運転を行うと、汚泥量当りの負荷量が増加す
るため、槽内に未分解の有機物が残溜し易くなる。そし
て、未分解の有機物や、分解過程で発生した中間代謝物
の濃度が高まると、それ等が中空糸膜の表面に付着し、
隣接した中空糸膜同志を塊状にするなどして同様に中空
糸膜を透過する透過水の水量を低減させる。このため、
中空糸膜を有する膜エレメントを浸漬した装置は、槽内
の活性汚泥の濃度は上限で10000mg/立、負荷量
は上限で5kg−BOD/m3 ・日で運転しているのが
現状である。
However, if the activated sludge is kept at a high concentration in the tank, the amount of sludge adhering to the surface of the hollow fiber of the immersed membrane element increases, and the amount of permeated water that permeates the hollow fiber membrane. Is reduced. Normally, the concentration of activated sludge is 1000, which does not significantly reduce the amount of permeated water that permeates the hollow fiber membrane.
It is said to be around 0 mg / stand. Even if the activated sludge concentration in the tank is set to the above-mentioned 10,000 mg / stand, even if the operation is carried out in the high load range of 10 kg-BOD / m 3 · day or more, Since the load amount increases, undecomposed organic matter is likely to remain in the tank. Then, when the concentration of undegraded organic matter or intermediate metabolites generated in the decomposition process increases, they adhere to the surface of the hollow fiber membrane,
The amount of permeated water that permeates the hollow fiber membranes is also reduced by forming adjacent hollow fiber membranes into a lump. For this reason,
An apparatus in which a membrane element having a hollow fiber membrane is immersed is currently operating at a maximum activated sludge concentration of 10000 mg / stand and a maximum load of 5 kg-BOD / m 3 · day. .

【0004】[0004]

【課題を解決するための手段】この発明は、処理槽全体
の保持汚泥濃度を高め、負荷量10kg−BOD/m3
・日以上で運転を行っても中空糸膜の透過性能が低減せ
ず、高度な処理水が安定して得られると共に、中空糸膜
の洗浄頻度が少なく、維持管理が容易な浸漬型膜分離装
置を得るために開発されたもので、処理槽内の活性汚泥
を含む水中に、多数本の中空糸膜を有する膜エレメント
を立て、槽内底部の散気管が散気する気泡により中空糸
膜に接触して上昇するエアリフト上向流を生じさせ、中
空糸膜の膜を透過した透過水を採水する中空糸膜による
浸漬型膜分離装置において、槽内の水中に、活性汚泥が
付着できる洗浄部材を、槽内のエアリフト上向流で揺れ
て中空糸膜に接触可能に配列したことを特徴とする。
SUMMARY OF THE INVENTION The present invention increases the concentration of retained sludge in the entire treatment tank to achieve a load of 10 kg-BOD / m 3
・ Permeability of the hollow fiber membrane does not decrease even if it is operated for more than a day, highly treated water can be stably obtained, and the frequency of cleaning the hollow fiber membrane is low, and the immersion type membrane separation is easy to maintain. It was developed to obtain a device, and a membrane element with a large number of hollow fiber membranes is set up in water containing activated sludge in a treatment tank, and the air diffusers at the bottom of the tank form hollow fiber membranes. In the submerged membrane separation device with a hollow fiber membrane, which causes upward airflow to rise by contact with the air and collects permeated water that has permeated through the membrane of the hollow fiber membrane, activated sludge can adhere to the water in the tank. The cleaning member is arranged so as to be capable of contacting the hollow fiber membrane while being swung by an upward flow of an air lift in the tank.

【0005】[0005]

【発明の実施の形態】図示の実施形態において、10
は、原水として有機性の廃水がポンプP1 、供給管11
により供給される活性汚泥処理装置の処理槽で、活性汚
泥が浮遊する槽内の水中には上下方向に配列された多数
本の中空糸膜13を有する複数の膜エレメント12が前
後方向に流路間隔16を保って一列に立て並べてある。
膜エレメントは、多数本の中空糸膜13の上端を固定し
た上部支持材14aと、下端を固定した下部支持部材1
4bとを有し、上部支持部材14aは1本宛の中空糸膜
13の中空部と連通した採水管であり、各膜エレメント
の採水管に採水用のヘッダー管15を連結し、ヘッダー
管15に接続した吸引ポンプP2 の吸引作用により槽内
の原水中の透過水を中空糸膜の中空部に透過させ、処理
水として採水する。処理槽の底部には、原水中の有機物
を活性汚泥で好気的に生物処理するためと、中空糸膜に
接触して上昇するエアリフト上向流を槽内の原水に生じ
させるため複数の散気管17が敷設してあり、散気管に
接続した散気用のヘッダー管18に設けてあるブロアB
からの送風を散気管17から気泡として散気する。
DETAILED DESCRIPTION OF THE INVENTION In the illustrated embodiment, 10
Is an organic wastewater as a raw water pump P1, supply pipe 11
In the treatment tank of the activated sludge treatment apparatus, a plurality of membrane elements 12 having a plurality of hollow fiber membranes 13 arranged in the vertical direction are flowed in the longitudinal direction in the water in the tank in which the activated sludge floats. They are arranged in a line with a space 16 kept therebetween.
The membrane element is composed of an upper support member 14a having the upper ends of a plurality of hollow fiber membranes 13 fixed and a lower support member 1 having the lower ends fixed.
4b and the upper support member 14a is a water sampling pipe communicating with the hollow part of the hollow fiber membrane 13 addressed to one, and the header pipe 15 for water sampling is connected to the water sampling pipe of each membrane element to form a header pipe. The permeated water in the raw water in the tank is permeated into the hollow portion of the hollow fiber membrane by the suction action of the suction pump P2 connected to 15, and is collected as treated water. At the bottom of the treatment tank, there are multiple spargers for aerobically biotreating organic matter in the raw water with activated sludge and for generating upward airlift flow in contact with the hollow fiber membrane in the raw water in the tank. A blower B having a trachea 17 laid and provided in a header pipe 18 for air diffusion connected to the air diffuser
The air blown from is diffused as air bubbles from the air diffuser 17.

【0006】20は、上記散気管17の散気により生じ
たエアリフト上向流で揺れて中空糸膜に接触する上下方
向の洗浄部材で、流路間隔16を保って対向する前後の
膜エレメントの中空糸膜の相対向した面を洗浄するた
め、流路間隔16内と、前端の膜エレメントの中空糸膜
の前面、及び後端の膜エレメントの中空糸膜の後面とに
沿って複数宛、上下の支持材23a,23b間に配列し
てある。
Reference numeral 20 is a cleaning member in the up-down direction that is swayed by the upward flow of the air lift generated by the air diffusion of the air diffusion pipe 17 and comes into contact with the hollow fiber membrane. In order to clean the opposite surfaces of the hollow fiber membrane, a plurality of them are provided along the flow path interval 16 and along the front surface of the hollow fiber membrane of the front end membrane element and the rear surface of the hollow fiber membrane of the rear end membrane element, They are arranged between the upper and lower support members 23a and 23b.

【0007】各洗浄部材20は、図3に示すように、活
性汚泥が付着可能な芯糸21の回りから同様に活性汚泥
が付着可能な枝糸22が放射状に無数に突出して筒形の
ブラシ状を呈する。この洗浄部材としては、素材がポリ
エステル(芯糸)と、アクリル系繊維(枝糸)からなる
ダイヤバイオフリンジ(エヌ・イー・ティ株式会社商標
名)を使用することができる。直径100mmのダイヤ
バイオフリンジを処理槽の容積1m3 に対し長さ1m使
用すると、その表面に活性汚泥を20000mg/立以
上、保持することができ、処理槽内に10000mg/
立の活性汚泥が浮遊状態にあるように設定すると、処理
槽が保持する活性汚泥の量は、ダイヤバイオフリンジが
保持するものと合わせて30000mg/立に達し、1
5kg−BOD/m3 ・日の高負荷域で運転を行うこと
ができる。
As shown in FIG. 3, each cleaning member 20 has a cylindrical brush in which innumerable branch yarns 22 to which the activated sludge can be similarly radially projected from around the core yarn 21 to which the activated sludge can be attached. Take on a shape. As the cleaning member, a diabio fringe (trade name of NT Co., Ltd.) made of polyester (core yarn) and acrylic fiber (branch yarn) can be used. If a length of 1 m is used for a volume of 1 m 3 of a treatment tank with a diameter of 100 mm, it is possible to retain activated sludge at the surface of 20,000 mg / stand or more, and in the treatment tank 10,000 mg /
When the standing activated sludge is set to be in a floating state, the amount of activated sludge held in the treatment tank reaches 30000 mg / stand including the amount held by the diabio fringe.
It is possible to operate in a high load area of 5 kg-BOD / m 3 · day.

【0008】この洗浄部材20は上下の支持部材23
a,23bの間に弛ませて取付け、槽内の水中に生じる
エアリフト上向流により絶えず揺れて膜エレメントの中
空糸膜に接触し、膜の表面を枝糸22で撫でるようにす
る。
The cleaning member 20 is provided with upper and lower support members 23.
It is loosely attached between a and 23b, and is constantly shaken by the upward flow of the air lift generated in the water in the tank so as to come into contact with the hollow fiber membrane of the membrane element, and the surface of the membrane is rubbed with the branch yarn 22.

【0009】ポンプP1 ,P2 、ブロアBを駆動して運
転を行うと、処理槽内に供給管11で供給される有機物
を含んだ原水は、槽内の水中に浮遊する活性汚泥と、洗
浄部材20に付着して保持された活性汚泥とによって生
物処理され、有機物は分解する。そして、原水中の中空
糸膜を透過する透過水は、散気管17が噴出する気泡に
より各膜エレメント12の中空糸膜13に接触して上向
流する過程で、吸引ポンプP2 の負圧が作用する中空糸
膜の中空部に膜を透過して流入し、採水管14a、採水
用ヘッダー管15を経て採水される。
When the pumps P1 and P2 and the blower B are driven for operation, the raw water containing organic substances supplied through the supply pipe 11 into the treatment tank is activated sludge floating in the water in the tank and the cleaning member. The organic matter is decomposed by being biologically treated by the activated sludge that is attached to and retained by 20. Then, the permeated water that permeates the hollow fiber membrane in the raw water contacts the hollow fiber membranes 13 of each membrane element 12 by the bubbles ejected from the air diffuser 17 and flows upward, and the negative pressure of the suction pump P2 is increased. It permeates the membrane into the hollow portion of the hollow fiber membrane that acts, and flows into the hollow portion, and the water is sampled through the water sampling pipe 14a and the water sampling header pipe 15.

【0010】活性汚泥は槽内の水中に浮遊するほか、洗
浄部材20にも付着して保持されるため、浮遊する濃度
を10000mg/立に設定した場合、洗浄部材20に
濃度10000mg/立以上を保持させ、容易に200
00mg/立以上の濃度の活性汚泥により、負荷量10
kg−BOD/m3 ・日以上の高負荷域で運転を行い、
高度な処理水を得ることができる。そして、汚泥の保持
量が多く、高負荷域で運転を行っても、運転中は洗浄部
材20が絶えず中空糸膜13に接触して揺れ、中空糸膜
の表面に付着する汚泥や、汚染物質を除去して洗浄を行
うため、膜を透過する透過水の水量は減少しないと共
に、中空糸膜の隣接したもの同志が汚泥や、汚染物質で
塊状に固まることが防止できる。従って、洗浄頻度が大
幅に少なくなり、維持管理が容易である。
Since activated sludge floats in the water in the tank and also adheres to and is retained on the cleaning member 20, when the concentration of floating sludge is set to 10000 mg / stand, the concentration in the cleaning member 20 should be 10,000 mg / stand or more. Hold and easily 200
Loaded by activated sludge with a concentration of 00 mg / stand or more, 10
Operate in the high load range of kg-BOD / m 3 · day or more,
Highly treated water can be obtained. Even if the cleaning member 20 has a large amount of sludge retained and is operated in a high load range, the cleaning member 20 constantly contacts the hollow fiber membrane 13 and shakes during operation, and sludge and contaminants attached to the surface of the hollow fiber membrane. Since the water is removed and washed, the amount of permeated water that permeates the membrane does not decrease, and it is possible to prevent the adjoining members of the hollow fiber membrane from solidifying in sludge or contaminants. Therefore, the frequency of cleaning is greatly reduced and maintenance is easy.

【0011】図示の実施形態では、膜エレメント12の
上下の支持材14a,14bと、洗浄部材20の上下の
支持材23a,23bは処理槽10の相対向した側壁の
内面上部に固定したが、そうではなく、上下が開放した
筒枠の相対向した側壁の内面上部に固定して膜エレメン
トと、洗浄部材を筒枠の内部に収め、この筒枠を処理槽
の内部に引上げ可能に浸漬してもよい。更に、中空糸膜
の上端を固定した上部支持材14aを採水管にし、中空
糸膜の上端の固定と、中空糸膜を透過した透過水の採水
とを兼用させたが、中空糸膜の構造によっては中空糸膜
の上端を固定する支持部材と、中空糸膜を透過した透過
水の採水管を別個に設置してもよい。又、中空糸膜の下
端を固定する下部支持部材14bも採水管にし、中空糸
膜の下端の固定と、中空糸膜を透過した透過水の採水と
を兼用させてもよい。更に、中空糸膜は上下方向に配列
することに限定されず、水平方向に配列してもよい。
In the illustrated embodiment, the upper and lower support members 14a and 14b of the membrane element 12 and the upper and lower support members 23a and 23b of the cleaning member 20 are fixed to the upper inner surface of the side walls of the processing tank 10 which face each other. Instead, the membrane element and the cleaning member are housed inside the tubular frame by fixing them to the upper portions of the inner surfaces of the opposite side walls of the open and closed tubular frame, and the tubular frame is immersed in the treatment tank so that it can be pulled up. May be. Further, the upper support member 14a to which the upper end of the hollow fiber membrane is fixed is used as a water sampling tube, and the upper end of the hollow fiber membrane is fixed and the permeated water that permeates the hollow fiber membrane is also collected. Depending on the structure, a support member for fixing the upper end of the hollow fiber membrane and a pipe for collecting permeated water that has permeated the hollow fiber membrane may be installed separately. Further, the lower support member 14b for fixing the lower end of the hollow fiber membrane may also be used as a water sampling pipe so that the lower end of the hollow fiber membrane is fixed and the permeated water that has permeated through the hollow fiber membrane is also used. Furthermore, the hollow fiber membranes are not limited to being arranged vertically, but may be arranged horizontally.

【0012】[0012]

【実施例】幅600mm、奥行900mm、深さ120
0mm、有効容量540立のテスト処理槽内の水中に、
分画特性0.1μm、素材がポリエチレン、幅486m
m、高さ798mm、有効表面積4m2 の中空糸UF膜
が上下方向に配列された膜エレメント(三菱レイヨン株
式会社、商品名ステラポアーL)を一基立て、その各片
面に洗浄部材として前述の直径100mm、高さ100
0mmのダイヤバイオフリンジを5本宛(両面で10
本)設置した。片面5本宛のダイヤバイオフリンジの中
心間の間隔は100mm、中空糸膜との中心間の間隔は
50mmにした。槽底には散気管を敷設し、底面全体か
ら均一に空気が噴出するようにした。
[Example] Width 600 mm, depth 900 mm, depth 120
0mm, in the water in a test tank with an effective capacity of 540
Fractionation characteristic 0.1μm, material is polyethylene, width 486m
m, height 798 mm, effective surface area 4 m 2 hollow fiber UF membranes arranged vertically, one membrane element (Mitsubishi Rayon Co., Ltd., product name Stellapore L) is set up, and the above-mentioned diameter is used as a cleaning member on each one side. 100 mm, height 100
5 0mm diamond bio fringes (10 on both sides)
Book) installed. The distance between the centers of the diamond biofringes for 5 fibers on one side was 100 mm, and the distance between the centers of the diamond biofringes and the hollow fiber membrane was 50 mm. An air diffuser was laid on the bottom of the tank so that air could be blown out uniformly from the entire bottom surface.

【0013】上記処理槽内には活性汚泥を汚泥濃度とし
て5000mg/立投入し、ペプトンとグルコースを用
いたBOD濃度10000mg/立の合成原水を滞流時
間48時間で通水した。負荷量は5kg−BOD/m3
・日である。処理水は、中空糸膜の中空部から−0.2
kg/cm2 の減圧で吸引した。12日間連続運転を行
った結果、槽内の浮遊汚泥濃度は10500mg/立
に、ダイヤバイオフリンジに付着した汚泥量は全体で3
500gに達し、処理槽全体の保持汚泥濃度は1700
0mg/立になった。その後、原水の滞流時間を24時
間、負荷量を10kg−BOD/m3 ・日に高め、7日
間連続運転を行った。この期間では槽内の浮遊汚泥濃度
を9000〜11000mg/立に保つように汚泥の引
抜きを行った。負荷量10kg−BOD/m3 ・日の運
転期間中、処理水のBODが10mg/立以下の高度な
処理が安定して行えた。又、中空糸膜から−0.3kg
/cm2 の減圧下で吸引可能な透過水の最大水量は0.
8〜1.1m3 /m2 ・日で、その水量が減少する傾向
は認められなかった。膜エレメントを水面上に引上げて
中空糸膜を観察したところ、膜の表面に汚泥は付着して
居らず、洗浄部材によって中空糸膜が良好に洗浄されて
いることが確認できた。
Activated sludge was introduced into the above treatment tank at a sludge concentration of 5000 mg / vertical, and synthetic raw water having a BOD concentration of 10000 mg / vertical using peptone and glucose was passed for 48 hours. Loadings 5kg-BOD / m 3
・ It is a day. Treated water is -0.2 from the hollow part of the hollow fiber membrane.
It was sucked at a reduced pressure of kg / cm 2 . As a result of continuous operation for 12 days, the concentration of suspended sludge in the tank was 10500 mg / stand and the amount of sludge attached to the diamond biofringe was 3 in total.
Reached 500g, the total sludge concentration in the treatment tank was 1700
It became 0 mg / stand. Then, the stagnant time of raw water was increased to 24 hours, the load was increased to 10 kg-BOD / m 3 · day, and continuous operation was performed for 7 days. During this period, sludge was drawn out so that the concentration of floating sludge in the tank was maintained at 9000 to 11000 mg / stand. During the operation period with a load of 10 kg-BOD / m 3 · day, the advanced treatment with BOD of treated water of 10 mg / cubic or less was stably performed. Also, from the hollow fiber membrane-0.3 kg
The maximum amount of permeated water that can be sucked in under a reduced pressure of / cm 2 is 0.
There was no tendency for the amount of water to decrease from 8 to 1.1 m 3 / m 2 · day. When the hollow fiber membrane was observed by pulling up the membrane element above the water surface, it was confirmed that sludge did not adhere to the surface of the membrane and the hollow fiber membrane was well washed by the washing member.

【0014】[0014]

【発明の効果】以上で明らかなように、本発明では活性
汚泥が付着可能な洗浄部材を使用し、運転中、洗浄部材
で絶えず中空糸膜の表面を洗浄するので、槽内の水中に
浮遊する活性汚泥と、洗浄部材に付着した活性汚泥とに
よって処理槽全体の保持汚泥濃度を高め、10kg−B
OD/m3 ・日以上の高負荷域運転を行って高度の処理
水を安定して採水することができる。従って、装置のコ
ンパクト化、設置面積の低減化の要求に応えることがで
きると共に、運転中は洗浄部材が絶えず中空糸膜の表面
を洗浄するので、洗浄頻度が大幅に少なくなり、装置の
維持管理が著しく容易になる。
As is clear from the above, the present invention uses a cleaning member to which activated sludge can be adhered, and the cleaning member constantly cleans the surface of the hollow fiber membrane during operation, so that it floats in the water in the tank. By increasing the activated sludge and the activated sludge adhering to the cleaning member, the concentration of the retained sludge in the entire treatment tank is increased to 10 kg-B.
It is possible to stably collect highly treated water by operating in a high load area of OD / m 3 · day or more. Therefore, it is possible to meet the demands for downsizing of the equipment and reduction of the installation area, and since the cleaning member constantly cleans the surface of the hollow fiber membrane during operation, the frequency of cleaning is greatly reduced and the maintenance of the equipment is reduced. Is significantly easier.

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

【図1】(イ)は本発明の一実施形態の平面図、(ロ)
は(イ)のA−B線に沿う断面図である。
FIG. 1A is a plan view of an embodiment of the present invention, and FIG.
FIG. 4B is a sectional view taken along the line AB of FIG.

【図2】図1の実施形態の縦断側面図である。FIG. 2 is a vertical side view of the embodiment of FIG.

【図3】(イ)は洗浄部材の立面図、(ロ)はその平面
図である。
3A is an elevation view of the cleaning member, and FIG. 3B is a plan view thereof.

【符号の説明】[Explanation of symbols]

10 処理槽 11 原水の供給管 12 膜エレメント 13 中空糸膜 14 中空糸膜の上下の支持部材 15 採水用ヘッダー管 16 膜エレメント間の流路間隔 17 散気管 18 散気用ヘッダー管 20 洗浄部材 21 洗浄部材の芯糸 22 洗浄部材の枝糸 23 洗浄部材の上下の支持部材 10 Treatment Tank 11 Raw Water Supply Pipe 12 Membrane Element 13 Hollow Fiber Membrane 14 Upper and Lower Support Members of Hollow Fiber Membrane 15 Water Collection Header Pipe 16 Flow Path Interval Between Membrane Elements 17 Diffuser Pipe 18 Diffuser Header Pipe 20 Cleaning Member 21 core thread of cleaning member 22 branch thread of cleaning member 23 upper and lower support members of cleaning member

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 処理槽内の活性汚泥を含む水中に、多数
本の中空糸膜を有する膜エレメントを立て、槽内底部の
散気管が散気する気泡により中空糸膜に接触して上昇す
るエアリフト上向流を生じさせ、中空糸膜の膜を透過し
た透過水を採水する中空糸膜による浸漬型膜分離装置に
おいて、槽内の水中に、活性汚泥が付着できる洗浄部材
を、槽内のエアリフト上向流で揺れて中空糸膜に接触可
能に配列したことを特徴とする中空糸膜による浸漬型膜
分離装置。
1. A membrane element having a large number of hollow fiber membranes is erected in water containing activated sludge in a treatment tank, and an air diffuser at the bottom of the tank contacts the hollow fiber membranes by air bubbles to rise. In a submerged membrane separation device using a hollow fiber membrane that produces an upward flow of an air lift and collects permeated water that has permeated the membrane of the hollow fiber membrane, a cleaning member that can attach activated sludge to the water in the tank An immersion type membrane separation device using a hollow fiber membrane, wherein the hollow fiber membranes are arranged so that they can be shaken by the upward flow of the air lift and contact the hollow fiber membranes.
JP7252050A 1995-09-06 1995-09-06 Dipping type membrane separation device using hollow fiber membrane Pending JPH0975970A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7252050A JPH0975970A (en) 1995-09-06 1995-09-06 Dipping type membrane separation device using hollow fiber membrane

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7252050A JPH0975970A (en) 1995-09-06 1995-09-06 Dipping type membrane separation device using hollow fiber membrane

Publications (1)

Publication Number Publication Date
JPH0975970A true JPH0975970A (en) 1997-03-25

Family

ID=17231877

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7252050A Pending JPH0975970A (en) 1995-09-06 1995-09-06 Dipping type membrane separation device using hollow fiber membrane

Country Status (1)

Country Link
JP (1) JPH0975970A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001286881A (en) * 2000-04-10 2001-10-16 Mitsubishi Rayon Co Ltd Water treating device and water treating system provided with the water treating device
JP2001286888A (en) * 2000-04-10 2001-10-16 Mitsubishi Rayon Co Ltd Water treating device and water treating system having the same
JP2001286864A (en) * 2000-04-10 2001-10-16 Mitsubishi Rayon Co Ltd Immersion type membrane separator and water purifying system provided with this separator
JP2001300568A (en) * 2000-04-20 2001-10-30 Mitsubishi Rayon Co Ltd Water treating apparatus and water treating system provided therewith
JP2004074120A (en) * 2002-08-22 2004-03-11 Taikisha Ltd Paint supply equipment
JP2008142640A (en) * 2006-12-11 2008-06-26 Hitachi Ltd Sewage treatment apparatus
JP2015112517A (en) * 2013-12-10 2015-06-22 三菱レイヨン株式会社 Water treatment apparatus

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001286881A (en) * 2000-04-10 2001-10-16 Mitsubishi Rayon Co Ltd Water treating device and water treating system provided with the water treating device
JP2001286888A (en) * 2000-04-10 2001-10-16 Mitsubishi Rayon Co Ltd Water treating device and water treating system having the same
JP2001286864A (en) * 2000-04-10 2001-10-16 Mitsubishi Rayon Co Ltd Immersion type membrane separator and water purifying system provided with this separator
JP2001300568A (en) * 2000-04-20 2001-10-30 Mitsubishi Rayon Co Ltd Water treating apparatus and water treating system provided therewith
JP4502453B2 (en) * 2000-04-20 2010-07-14 三菱レイヨン株式会社 Water treatment apparatus and water treatment system provided with the same
JP2004074120A (en) * 2002-08-22 2004-03-11 Taikisha Ltd Paint supply equipment
JP2008142640A (en) * 2006-12-11 2008-06-26 Hitachi Ltd Sewage treatment apparatus
JP2015112517A (en) * 2013-12-10 2015-06-22 三菱レイヨン株式会社 Water treatment apparatus

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