JPH10128081A - Immersion type membrane module - Google Patents

Immersion type membrane module

Info

Publication number
JPH10128081A
JPH10128081A JP30126096A JP30126096A JPH10128081A JP H10128081 A JPH10128081 A JP H10128081A JP 30126096 A JP30126096 A JP 30126096A JP 30126096 A JP30126096 A JP 30126096A JP H10128081 A JPH10128081 A JP H10128081A
Authority
JP
Japan
Prior art keywords
membrane
membrane module
stock solution
elements
space
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
JP30126096A
Other languages
Japanese (ja)
Inventor
Tetsuro Adachi
哲朗 安達
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.)
Nitto Denko Corp
Original Assignee
Nitto Denko 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 Nitto Denko Corp filed Critical Nitto Denko Corp
Priority to JP30126096A priority Critical patent/JPH10128081A/en
Publication of JPH10128081A publication Critical patent/JPH10128081A/en
Pending legal-status Critical Current

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  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

PROBLEM TO BE SOLVED: To enable long-term stable operation by specifying a space between membrane elements of a module of a membrane separator and providing a leveling means. SOLUTION: In a membrane module, a space 'a' between membrane elements 2, 2 are made extremely narrow, being 3-15mm, but a leveling means is provided to direct the space 'a' between the membrane elements 2, 2 toward the vertical direction with high accuracy by leveling, and under such leveling, gas-liquid mixed fluid by jetting air from a diffusing pipe is forcibly and smoothly caused to flow upward in to the space 'a' between the membrane elements 2, 2. Therefore, the strong gas-liquid mixed fluid is caused to flow along the membrane surface to processed a filtration treatment while sufficiently restraining sludge from being stuck on the membrane surface. A rapid increase in a caused by the increase of filtration resistance is prevented to provide stable operation without an extreme change in a filtration flux and in a pressure decrease degree on the filtrate side of the membrane element 2 to enable long-term stable operation.

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、し尿、下水、生活
排水、工場排水等の汚水処理に使用する膜分離装置の膜
モジュ−ルに関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a membrane module for a membrane separation apparatus used for treating sewage such as human waste, sewage, domestic wastewater, and industrial wastewater.

【0002】[0002]

【従来の技術】近来、し尿、下水、家庭排水、工場排水
(以下、汚水と称する)の伝統的な処理方法である重力
分離活性汚泥処理法(曝気槽で微生物分解処理を行い、
この処理汚水を沈殿分離室に導き、活性汚泥を重力分離
により分離し、その分離汚泥の一部を曝気槽に返送する
方法)に代替する方法として、膜分離活性汚泥処理法が
注目されている。
2. Description of the Related Art Recently, a gravity separation activated sludge treatment method, which is a traditional treatment method for human waste, sewage, domestic wastewater, and industrial wastewater (hereinafter referred to as sewage) (microbial decomposition treatment in an aeration tank,
A membrane separation activated sludge treatment method is attracting attention as an alternative to the method of introducing the treated wastewater into a sedimentation separation chamber, separating the activated sludge by gravity separation, and returning a part of the separated sludge to an aeration tank. .

【0003】この処理法においては、固液分離を膜モジ
ュ−ルによる濾過で行い、濾過液を取出し、余剰汚泥を
直接曝気槽から引き抜いており、曝気槽のMLSS(混合
液浮遊性固形物)を重力分離法に較べて著しく高くでき
るので、曝気槽を重力分離法の場合に較べて相当に縮小
でき、更に沈殿分離室が不要であるので、装置全体を小
型化できる、曝気槽内のMLSS濃度を高く維持できるの
で、重力分離法とは異なり、余剰汚泥処理に際しての脱
水が軽減される、運転エネルギ−の省力化を図ること
ができる、等の利点がある。
In this treatment method, solid-liquid separation is carried out by filtration using a membrane module, a filtrate is taken out, and excess sludge is directly drawn out from an aeration tank, and MLSS (mixed liquid floating solids) in the aeration tank is used. The MLSS in the aeration tank can be significantly reduced compared to the gravity separation method, and the size of the entire apparatus can be reduced because the sedimentation separation chamber is unnecessary. Since the concentration can be maintained at a high level, there are advantages that, unlike the gravity separation method, dehydration during the treatment of excess sludge is reduced, and energy consumption of operating energy can be reduced.

【0004】本出願人においては、膜分離法による汚水
処理装置として、「散気装置を有し、膜面に沿い鉛直方
向通路を有する膜モジュ−ルを前記散気装置の直上に配
設し、該膜装置の膜体濾過側を負圧とするための手段を
設けた散気式曝気槽」を既に提案した(特公平4−70
958号、特許第1874881号)。この装置の膜モ
ジュ−ルとしては、平型の膜エレメントを相互間に鉛直
方向通路を保持するように立て並べて設置したものが好
適である。
[0004] In the present applicant, a sewage treatment apparatus using a membrane separation method is described as "a membrane module having an air diffuser and having a vertical passage along the membrane surface is disposed immediately above the air diffuser. And a diffuser-type aeration tank provided with means for reducing the pressure on the membrane filtration side of the membrane device ”(Japanese Patent Publication No. 4-70).
958, Patent No. 1874881). As the membrane module of this apparatus, it is preferable that flat membrane elements are arranged side by side so as to maintain a vertical passage therebetween.

【0005】この散気式曝気槽を使用して汚水を処理す
るには、散気装置からの噴出エアのエアバブリングで槽
内原液を旋回させ、汚水中の有機物を空気との接触下、
好気性微生物により吸着・代謝分解させ、有機物を減少
させると共に好気性微生物を増殖させ、膜エレメントの
膜面に沿う原液流れで膜面での汚泥ゲル層の生成を抑制
しつつ膜エレメントの濾過液側を減圧して膜間差圧を発
生させ、この膜間差圧下で活性汚泥液から水を濾過によ
り分離していく。
To treat sewage using this aeration type aeration tank, the undiluted solution in the tank is swirled by air bubbling of air spouted from the aeration device, and organic matter in the sewage is brought into contact with air.
Adsorbed and metabolized and decomposed by aerobic microorganisms to reduce organic matter and grow aerobic microorganisms, and to control the production of sludge gel layer on the membrane surface by the undiluted solution flow along the membrane surface of the membrane element, and the filtrate of the membrane element The pressure on the side is reduced to generate a transmembrane pressure, and water is separated from the activated sludge by filtration under the transmembrane pressure.

【0006】この膜分離においては、経時的に原液中の
浮遊汚泥が膜面に付着して濾過抵抗が増大していくか
ら、濾過流束を一定に保持するには、膜エレメントの濾
過液側減圧度、すなわち膜間差圧を漸次に増加しなけれ
ばならない。
In this membrane separation, suspended sludge in the undiluted solution adheres to the membrane surface with time and the filtration resistance increases. Therefore, in order to maintain the filtration flux constant, it is necessary to maintain the filtration flux at the filtrate side of the membrane element. The degree of vacuum, ie, the transmembrane pressure, must be gradually increased.

【0007】[0007]

【発明が解決しようとする課題】上記膜モジュ−ルの小
型化には膜エレメントの間隔を狭くし、膜モジュ−ルの
容積に対する膜面積率を大とすることが有効である。而
るに、本発明者においては、膜エレメント間の間隔を1
0mm程度に狭くすると、処理槽での膜モジュ−ルの水
平度が上記の濾過特性に大きな影響を与え、水平度が悪
いほど、濾過流束一定のもとでの経時的な減圧度の増加
を急峻にしなければならず、減圧度が早期に減圧ポンプ
の限界値に達してしまい、安定運転を行い得ないことを
知った。そこで、本発明者において、この原因を究明し
たところ、上記膜エレメント間の間隙を10mm程度と
狭くすると、膜モジュ−ルの傾きによって散気管からの
噴出エアによる気液混合流体の上昇流に対する抵抗が増
し、上記の原液旋回流が弱められて膜面での原液流れに
よる汚泥ゲル層の生成抑制効果が減退されて汚泥ゲル層
の生成が加速度的に増加することが主要な原因であるこ
とを知った。
In order to reduce the size of the membrane module, it is effective to reduce the distance between the membrane elements and increase the membrane area ratio to the volume of the membrane module. Therefore, in the present inventor, the interval between the membrane elements is set to one.
When the width is reduced to about 0 mm, the level of the membrane module in the processing tank has a great influence on the above-mentioned filtration characteristics, and as the level is poor, the degree of pressure reduction with time under a constant filtration flux increases. Must be made steep, and the degree of pressure reduction reaches the limit value of the pressure reduction pump early, so that stable operation cannot be performed. Then, the present inventor has investigated the cause, and found that when the gap between the membrane elements was narrowed to about 10 mm, the inclination of the membrane module caused the resistance to the upward flow of the gas-liquid mixed fluid due to the air ejected from the diffuser tube. Increase, and the above-mentioned stock solution swirl flow is weakened, the effect of suppressing the formation of the sludge gel layer by the stock solution flow on the membrane surface is reduced, and the main cause is that the generation of the sludge gel layer is acceleratedly increased. Knew.

【0008】本発明の目的は、内側を濾過液側とする膜
エレメントを原液中に浸漬し、散気手段により原液を旋
回させ、膜面を原液流動で洗浄しつつ膜エレメントの濾
過液側を減圧して原液を濾過処理する膜分離法、特に膜
分離活性汚泥処理法において、一定の濾過流束を安定な
減圧度で得る浸漬型膜エレメント、すなわち、長期の安
定運転を可能にする浸漬型膜エレメントを提供すること
にある。
An object of the present invention is to immerse a membrane element having a filtrate side on the inner side in a stock solution, swirl the stock solution by aeration means, and wash the membrane surface with the stock solution flow while cleaning the membrane surface with the stock solution flow. In a membrane separation method in which a stock solution is filtered under reduced pressure, particularly in a membrane separation activated sludge treatment method, an immersion type membrane element that obtains a constant filtration flux at a stable degree of reduced pressure, that is, an immersion type element that enables long-term stable operation It is to provide a membrane element.

【0009】[0009]

【課題を解決するための手段】本発明に係る浸漬型膜モ
ジュ−ルは、内側を濾過液側とする平型膜エレメントが
複数枚立て並べられた膜モジュ−ルをその直下に散気手
段を配して原液処理槽内に設置し、散気手段により原液
を旋回させ、膜面を原液流動で洗浄しつつ膜エレメント
の濾過液側を減圧して原液を濾過処理する膜分離装置の
膜モジュ−ルであり、膜エレメント間の間隔が3〜15
mmであり、水平出し手段を備えていることを特徴とす
る構成であり、膜モジュ−ルに長さ調節可能な脚部を設
け、その脚部の長さ調節により水平出しを行うことがで
き、また、長さ調節可能な脚部を有する架台に膜モジュ
−ルを載置し、その脚部の長さ調節により水平出しを行
うことができる。
The immersion type membrane module according to the present invention includes a membrane module in which a plurality of flat membrane elements each having an inner side with a filtrate are arranged and arranged directly below the module. Is disposed in the stock solution processing tank, and the stock solution is swirled by the aeration means, and the membrane surface of the membrane separation device for filtering the stock solution by depressurizing the filtrate side of the membrane element while washing the membrane surface with the stock solution flow. A module with a spacing between membrane elements of 3 to 15
mm, and a leveling means is provided.The membrane module is provided with a leg whose length can be adjusted, and can be leveled by adjusting the length of the leg. Also, the membrane module can be placed on a gantry having legs with adjustable lengths, and leveling can be performed by adjusting the length of the legs.

【0010】[0010]

【発明の実施の形態】以下、図面を参照しつつ本発明の
実施の形態を説明する。図1は本発明に係る浸漬型膜モ
ジュ−ルの一例を示し、内側を濾過液側とする平型膜エ
レメント2を複数枚、相互間の間隔aを3〜15mmに
して立て並べてフレ−ム1内に納め、フレ−ム1の脚部
11を長さ調整可能としてある。図2は本発明に係る浸
漬型膜モジュ−ルを別例を示し、内側を濾過液側とする
平型膜エレメント2を複数枚、相互間の間隔aを3〜1
5mmにして立て並べて脚なしフレ−ム1内に納め、こ
れを架台10上に載置し、架台10の脚部11を長さ調
整可能としてある。上記脚部11の長さ調整機構には、
タ−ンバクル機構、スライド・セットビス機構等を使用
できる。上記のフレ−ムや架台は、膜モジュ−ルの直下
に配する散気管からの噴出エアによる気液混合流体を膜
エレメント間の間隙に向けスム−ズに上昇させ得るよう
に開放型としてある。後述の散気管はフレ−ムや架台に
一体的に取り付けることもできる。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 shows an example of an immersion type membrane module according to the present invention, in which a plurality of flat type membrane elements 2 having an inner side as a filtrate side are arranged side by side at an interval a of 3 to 15 mm. 1, the leg 11 of the frame 1 is adjustable in length. FIG. 2 shows another example of the immersion type membrane module according to the present invention, in which a plurality of flat type membrane elements 2 each having an inner side as a filtrate are provided, and an interval a between them is 3-1.
The frame 11 is set up in 5 mm, placed side by side in the frame 1 without legs, placed on the gantry 10, and the length of the legs 11 of the gantry 10 can be adjusted. The length adjusting mechanism of the leg 11 includes:
A turn mechanism, a slide / set screw mechanism, or the like can be used. The above-mentioned frame and gantry are of an open type so that the gas-liquid mixed fluid by the air jetted from the air diffuser disposed immediately below the membrane module can smoothly rise toward the gap between the membrane elements. . The later-described air diffuser can be integrally attached to a frame or a gantry.

【0012】図3の(イ)及び図3の(ロ)〔図3の
(イ)におけるロ−ロ断面図〕は、上記の平型膜エレメ
ント2の一例を示し、濾過液集水管21を有する枠体2
0内に濾過液流路材22(例えば、織布、不織布、ネッ
ト等)を納め、枠体20の両面に平膜23(精密濾過
膜、限外濾過膜等)を接着剤24で接着してあり、平膜
23には、支持基材上に膜を張り合わせたもの、膜に織
布、不織布等を埋め込んだもの等を使用できる。図4の
(イ)及び図4の(ロ)〔図4の(イ)におけるロ−ロ
断面図〕は、上記の平型膜エレメントの別例を示し、プ
レ−ト20の両面に濾過液通路溝201,…を形成し、
プレ−ト20の一端面に前記濾過液通路溝201,…に
連通する濾過液取出し孔202を設け、プレ−ト20の
各面に順次に濾過液通路用スペ−サ21及び平膜23を
積層し、平膜23の周囲部をプレ−ト各面に接着剤によ
り封止してある。上記膜エレメント2の寸法は、処理槽
の寸法を、従来の散気型曝気槽の曝気室の寸法にほぼ等
しくする場合、通常、高さ50cm〜150cm、巾2
0cm〜100cm、厚み3mm〜15mmとされる。
FIGS. 3 (a) and 3 (b) [a cross-sectional view taken along a line in FIG. 3 (a)] show an example of the flat membrane element 2 described above. Frame 2 having
A filtrate flow channel material 22 (for example, a woven fabric, a nonwoven fabric, a net, etc.) is placed in the inside of a frame 0, and a flat membrane 23 (a microfiltration membrane, an ultrafiltration membrane, etc.) is bonded to both surfaces of the frame 20 with an adhesive 24. As the flat membrane 23, a membrane obtained by laminating a membrane on a supporting base material, a membrane in which a woven fabric, a nonwoven fabric, or the like is embedded can be used. 4 (a) and 4 (b) [a cross-sectional view taken along a roll in FIG. 4 (a)] show another example of the above-mentioned flat type membrane element. Forming passage grooves 201,.
On one end surface of the plate 20, a filtrate outlet hole 202 communicating with the filtrate passage grooves 201,... Is provided, and on each surface of the plate 20, a filtrate passage spacer 21 and a flat membrane 23 are sequentially placed. The layers are laminated, and the peripheral portion of the flat film 23 is sealed on each surface of the plate with an adhesive. The dimensions of the membrane element 2 are usually 50 cm to 150 cm in height and 2 cm in width when the size of the treatment tank is made substantially equal to the size of the aeration chamber of the conventional aeration type aeration tank.
0 cm to 100 cm, and 3 mm to 15 mm in thickness.

【0013】図5は本発明に係る膜モジュ−ルを用いた
膜分離装置を示す説明図である。図5において、30は
原液処理槽であり、従来の活性汚泥方式による散気式曝
気槽の曝気槽本体を使用することができる。Aは本発明
に係る膜モジュ−ルであり、水平出しにより膜エレメン
ト2,2間の間隙eを高精度で鉛直方向に向けてある。
3,3…は膜エレメント2,…の下方に設けた散気管で
あり、膜エレメント2,2間の間隙に原液をエアバブリ
ングにより効率良く昇流させ得るように配設してある。
このエアバブリングにより原液が原液処理槽30内に旋
回される。31は散気管3に接続した送気配管、32は
ブロワである。4は膜エレメント2,…の濾過液集水管
に接続した濾過液取出し配管、41はこの配管4に挿入
した減圧ポンプ、42は濾過液貯槽である。51は原液
供給配管、52はこの配管51に挿入した液送ポンプで
ある。
FIG. 5 is an explanatory view showing a membrane separation apparatus using the membrane module according to the present invention. In FIG. 5, reference numeral 30 denotes a stock solution treatment tank, which can use an aeration tank body of a conventional aeration type aeration tank using an activated sludge method. A is a membrane module according to the present invention, and the gap e between the membrane elements 2 and 2 is oriented in the vertical direction with high precision by leveling.
Numerals 3, 3,... Are diffuser tubes provided below the membrane elements 2,..., And are arranged in gaps between the membrane elements 2, 2 so that the stock solution can be efficiently raised by air bubbling.
The stock solution is swirled into the stock solution processing tank 30 by this air bubbling. 31 is an air supply pipe connected to the air diffuser 3, and 32 is a blower. Numeral 4 is a filtrate extraction pipe connected to the filtrate collecting pipe of the membrane element 2,..., 41 is a vacuum pump inserted into the pipe 4, and 42 is a filtrate storage tank. Reference numeral 51 denotes a stock solution supply pipe, and reference numeral 52 denotes a liquid feed pump inserted into the pipe 51.

【0014】上記の膜分離装置により汚水(し尿、下
水、生活排水、工場排水等)を処理するには、汚水を貯
槽に一旦貯えたうえ、図5において、この汚水を液送ポ
ンプ52により原液処理槽30に供給し、ブロワ32の
駆動により散気管3から空気を噴出させて原液を旋回さ
せ、同時に、減圧ポンプ41の駆動により膜エレメント
2,…の濾過液流路側を減圧して所定の膜間差圧を作用
させ、汚水中の有機物を噴出空気との接触下、好気性微
生物により吸着・代謝分解させると共に好気性微生物を
増殖させつつ、膜エレメント2,…の膜に水を透過さ
せ、これを濾過液取出し配管4を経て濾過液貯槽42に
取出していく。
In order to treat sewage (human waste, sewage, domestic wastewater, industrial wastewater, etc.) by the above-mentioned membrane separation device, the wastewater is temporarily stored in a storage tank, and in FIG. It is supplied to the processing tank 30, and the blower 32 is driven to blow air from the air diffuser 3 to rotate the stock solution. At the same time, the decompression pump 41 is driven to depressurize the filtrate flow channel side of the membrane elements 2,. By applying a transmembrane pressure, organic substances in the sewage are adsorbed and metabolized and decomposed by aerobic microorganisms in contact with the jet air, and water is permeated through the membranes of the membrane elements 2 while growing the aerobic microorganisms. This is taken out to the filtrate storage tank 42 via the filtrate take-out pipe 4.

【0015】この場合、エアバブリングによる原液の旋
回流速(平均流速)は、原液の濃度や処理速度等によっ
ても異なるが、通常、0.1〜1.0m/secの範囲
内とされる。
In this case, the swirling flow velocity (average flow velocity) of the stock solution by air bubbling varies depending on the concentration of the stock solution, the processing speed, and the like, but is usually in the range of 0.1 to 1.0 m / sec.

【0017】上記において、散気管3からの噴出エアに
より原液が膜エレメント2,2間の間隙eを経て上昇さ
れ、その上昇後にモジュ−ル周囲やモジュ−ル下方から
原液が引き込まれることにより原液が旋回される。しか
るに、膜面に沿っての上昇流が弱いと、膜面への汚泥付
着が急速に進行し、濾過抵抗が増大して負荷急増による
濾過流束の激減または膜エレメントの濾過液側減圧度の
急上昇が避けられない。
In the above, the undiluted solution rises through the gap e between the membrane elements 2 and 2 by the air ejected from the air diffuser 3, and after the rise, the undiluted solution is drawn from around the module and below the module. Is turned. However, if the upward flow along the membrane surface is weak, the sludge adheres to the membrane surface rapidly, and the filtration resistance increases, causing a sharp decrease in the filtration flux due to a sudden increase in the load or a decrease in the degree of pressure reduction on the filtrate side of the membrane element. Soaring is inevitable.

【0018】而るに、本発明に係る膜モジュ−ルおいて
は、膜エレメン2,2ト間の間隔eを5〜15mmと著
しく狭くしているが、水平出し手段を備え、水平出しに
より膜エレメント2,2相互間の間隙eを高精度で鉛直
方向に向け得、かかる水平出しのもとで、散気管3から
の噴出エアによる気液混合流体を膜エレメント2,2間
の間隙eに勢い良くスム−ズに昇流させ得る。従って、
膜面に沿い強い気液混合流体を流動させることができ、
膜面への汚泥付着をよく抑制しつつ濾過処理を進め得、
濾過抵抗の増大に起因する負荷急増を防止して濾過流束
や膜エレメントの濾過液側減圧度の過激な変動なく安定
に運転できる。また、膜エレメント間の間隔を5〜15
mmと著しく狭くしているので、膜モジュ−ルの体積に
対する膜面積を大きくでき、モジュ−ルを小型化でき
る。
In the membrane module according to the present invention, the distance e between the membrane elements 2 and 2 is remarkably narrowed to 5 to 15 mm. The gap e between the membrane elements 2 and 2 can be oriented in the vertical direction with high precision, and under such leveling, the gas-liquid mixed fluid due to the air ejected from the air diffuser 3 is passed through the gap e between the membrane elements 2 and 2. The flow can be made to flow smoothly and smoothly. Therefore,
Strong gas-liquid mixed fluid can flow along the membrane surface,
Filtration process can be advanced while well suppressing sludge adhesion to the membrane surface,
A sudden increase in load due to an increase in filtration resistance is prevented, and stable operation can be performed without radical fluctuations in filtration flux and the degree of pressure reduction on the filtrate side of the membrane element. Further, the interval between the membrane elements is 5 to 15
mm, the membrane area with respect to the volume of the membrane module can be increased, and the module can be downsized.

【0019】本発明に係る膜モジュ−ルを複数台、原液
処理槽内に設置し、上記送気配管31をこの複数台数に
応じて分岐し、共通のブロワ32で各膜モジュ−ル直下
の散気管に送気することもできる。この場合、各膜モジ
ュ−ルの水平出しにより各散気管のエア噴出抵抗を同じ
ように低抵抗にでき、ある散気管のエア噴出抵抗が高く
なる場合に避けられない不均等送気を排除して各膜モジ
ュ−ルに一様にエアを供給でき、全ての膜モジュ−ルを
一様に安定運転できる。
A plurality of membrane modules according to the present invention are installed in a stock solution treatment tank, and the air supply pipe 31 is branched in accordance with the plurality of membrane modules, and a common blower 32 is provided immediately below each membrane module. Air can also be sent to the air diffuser. In this case, the air ejection resistance of each diffuser can be similarly reduced by leveling each membrane module, and uneven air supply which cannot be avoided when the air ejection resistance of a certain diffuser becomes high is eliminated. As a result, air can be uniformly supplied to each membrane module, and all membrane modules can be uniformly operated stably.

【0020】[0020]

【実施例】【Example】

〔実施例〕膜モジュ−ルには図1に示すものを使用し、
膜エレメント2の寸法は、縦1060mm、横(巾)6
10mm、厚み最大13mm、最小2mmとし、膜には
膜面積0.45m2のポリオレフィン系精密濾過膜を両
面に使用し、膜エレメント2の枚数は10枚とし、膜エ
レメント相互間の最小間隔を4mmとした。この膜モジ
ュ−ルを、活性汚泥方式の散気式曝気槽の曝気槽本体内
に据付け、脚部の長さを調節して水平出しを行った。原
液にはMLSS濃度10,000〜15,000mg/リッ
トルの活性汚泥溶液を使用し、汚水旋回流速をほぼ0.
5m/secとするように散気流量を設定し、減圧ポンプ
を8分運転−2分停止の繰返しで間歇運転し、濾過流束
をほぼ0.5m3/m2・dayとするように減圧度を調整
した。運転開始直後の減圧度0.7kg/cm2に対
し、運転開始8ケ月経過後での減圧度は、0.18kg
/cm2であり安定していた。
[Embodiment] The membrane module shown in FIG. 1 was used.
The dimensions of the membrane element 2 are 1060 mm in length and 6 in width (width).
10 mm, maximum thickness 13 mm, minimum 2 mm, a polyolefin-based microfiltration membrane having a membrane area of 0.45 m 2 is used on both sides, the number of membrane elements 2 is 10 and the minimum distance between the membrane elements is 4 mm. And This membrane module was installed in the aeration tank main body of the activated sludge aeration type aeration tank, and the length of the leg was adjusted to level out. As the stock solution, an activated sludge solution having an MLSS concentration of 10,000 to 15,000 mg / liter was used, and the sewage swirling flow rate was set at approximately 0.1%.
The air diffusion flow rate was set so as to be 5 m / sec, and the decompression pump was operated intermittently by repeating the operation for 8 minutes and stopping for 2 minutes, and the pressure was reduced so that the filtration flux was approximately 0.5 m 3 / m 2 · day. The degree was adjusted. While the degree of decompression immediately after the start of operation was 0.7 kg / cm 2, the degree of decompression eight months after the start of operation was 0.18 kg.
/ Cm 2 and was stable.

【0021】〔比較例〕実施例に対し、水平出しを行わ
なかった以外、実施例に同じとした。膜モジュ−ルの傾
き角度は1°であった。運転開始8ケ月経過後、減圧度
がほぼ0.6kg/cm2にも達し、運転続行が不可能
となった。
[Comparative Example] The comparative example was the same as the example except that leveling was not performed. The tilt angle of the membrane module was 1 °. After a lapse of eight months from the start of operation, the degree of decompression reached approximately 0.6 kg / cm 2 , making it impossible to continue operation.

【0022】[0022]

【発明の効果】本発明に係る平型膜モジュ−ルによれ
ば、汚水の処理、特に膜分離活性汚泥法において、膜分
離装置を膜汚染をよく抑制し負荷の増加を充分に抑えて
安定に運転でき、長期間にわたり安定運転が可能にな
る。
According to the flat type membrane module according to the present invention, in the treatment of sewage, particularly in the membrane separation activated sludge method, the membrane separation device is sufficiently suppressed in membrane contamination, and the increase in load is sufficiently suppressed to be stable. And stable operation for a long period of time.

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

【図1】本発明に係る浸漬型膜モジュ−ルの一例を示す
説明図である。
FIG. 1 is an explanatory view showing an example of an immersion type membrane module according to the present invention.

【図2】本発明に係る浸漬型膜モジュ−ルの別例を示す
説明図である。
FIG. 2 is an explanatory view showing another example of the immersion type membrane module according to the present invention.

【図3】本発明に係る浸漬型膜モジュ−ルに使用する膜
エレメントの一例を示す図面である。
FIG. 3 is a drawing showing an example of a membrane element used in a submerged membrane module according to the present invention.

【図4】本発明に係る浸漬型膜モジュ−ルに使用する膜
エレメントの別例を示す図面である。
FIG. 4 is a drawing showing another example of the membrane element used for the immersion type membrane module according to the present invention.

【図5】本発明に係る浸漬型膜モジュ−ルを使用した膜
分離装置をを示す図面である。
FIG. 5 is a view showing a membrane separation apparatus using the immersion type membrane module according to the present invention.

【符号の説明】[Explanation of symbols]

1 フレ−ム 10 架台 11 脚部 2 膜エレメント 3 散気管 DESCRIPTION OF SYMBOLS 1 Frame 10 Stand 11 Leg 2 Membrane element 3 Air diffuser

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】内側を濾過液側とする平型膜エレメントが
複数枚立て並べられた膜モジュ−ルをその直下に散気手
段を配して原液処理槽内に設置し、散気手段により原液
を旋回させ、膜面を原液流動で洗浄しつつ膜エレメント
の濾過液側を減圧して原液を濾過処理する膜分離装置の
膜モジュ−ルであり、膜エレメント間の間隔が3〜15
mmであり、水平出し手段を備えていることを特徴とす
る浸漬型膜モジュ−ル。
A membrane module in which a plurality of flat membrane elements each having an inner side as a filtrate side are arranged in a line, and a diffuser is disposed immediately below the membrane module in a stock solution treatment tank. A membrane module of a membrane separation device for rotating a stock solution, filtering the stock solution by depressurizing the filtrate side of the membrane element while washing the membrane surface with the stock solution flow, wherein the distance between the membrane elements is 3 to 15.
mm, and provided with leveling means.
【請求項2】膜モジュ−ルが長さ調節可能な脚部を有す
る請求項1記載の浸漬型膜モジュ−ル。
2. The immersion type membrane module according to claim 1, wherein the membrane module has adjustable length legs.
【請求項3】膜モジュ−ルが長さ調節可能な脚部を有す
る架台に載設されている請求項1記載の浸漬型膜モジュ
−ル。
3. The immersion type membrane module according to claim 1, wherein the membrane module is mounted on a base having adjustable length legs.
JP30126096A 1996-10-25 1996-10-25 Immersion type membrane module Pending JPH10128081A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP30126096A JPH10128081A (en) 1996-10-25 1996-10-25 Immersion type membrane module

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP30126096A JPH10128081A (en) 1996-10-25 1996-10-25 Immersion type membrane module

Publications (1)

Publication Number Publication Date
JPH10128081A true JPH10128081A (en) 1998-05-19

Family

ID=17894683

Family Applications (1)

Application Number Title Priority Date Filing Date
JP30126096A Pending JPH10128081A (en) 1996-10-25 1996-10-25 Immersion type membrane module

Country Status (1)

Country Link
JP (1) JPH10128081A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2015092835A1 (en) * 2013-12-19 2015-06-25 川崎重工業株式会社 Membrane separation device

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2015092835A1 (en) * 2013-12-19 2015-06-25 川崎重工業株式会社 Membrane separation device
JPWO2015092835A1 (en) * 2013-12-19 2017-03-16 川崎重工業株式会社 Membrane separator

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