JPH10128085A - Operating method of membrane separation device - Google Patents
Operating method of membrane separation deviceInfo
- Publication number
- JPH10128085A JPH10128085A JP30125996A JP30125996A JPH10128085A JP H10128085 A JPH10128085 A JP H10128085A JP 30125996 A JP30125996 A JP 30125996A JP 30125996 A JP30125996 A JP 30125996A JP H10128085 A JPH10128085 A JP H10128085A
- Authority
- JP
- Japan
- Prior art keywords
- membrane
- stock solution
- undiluted
- flow
- filtrate
- 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
Links
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
(57)【要約】
【課題】内側を濾過液側とする膜エレメント2を原液中
に浸漬し、散気手段3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2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こ
と、すなわち、長期の安定運転を可能にする。
【解決手段】原液中に原液流れ異常検出器6を配設し、
原液旋回流の異常の検知により、その旋回流れを正常状
態に回復させる。
(57) [Summary] Filtration of a membrane element 2 while immersing a membrane element 2 having a filtrate side inside in a stock solution, swirling the stock solution by a diffuser 3, and washing the membrane surface with the stock solution flow. In a membrane separation method in which the undiluted solution is filtered by depressurizing the liquid side, particularly in a membrane separation activated sludge treatment method, it is possible to obtain a constant filtration flux at a stable degree of reduced pressure, that is, to enable long-term stable operation. An undiluted liquid flow abnormality detector is provided in the undiluted liquid,
By detecting an abnormality of the undiluted swirl flow, the swirl flow is restored to a normal state.
Description
【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運
転方法に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for operating 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積重ね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 to stack flat membrane elements 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】[0006]
【発明が解決しようとする課題】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、濾過抵
抗が増大していくから、濾過流束Iを一定に保持するに
は、膜エレメントの濾過液側減圧度△P、すなわち膜間
差圧を漸次に増加していかなければならない。而るに、
本発明者の経験によれば、ある時点を境にして上記減圧
度△Pの加速度的な増加が必要とされる。In this membrane separation, suspended sludge in the undiluted solution adheres to the membrane surface over time and the filtration resistance increases. Therefore, it is necessary to maintain the filtration flux I constant. , The pressure of the membrane element on the filtrate side, ie, the transmembrane pressure difference, must be gradually increased. Thus,
According to the inventor's experience, it is necessary to increase the pressure reduction degree ΔP at a certain point in time.
【0007】そこで、本発明者において、この原因を究
明したところ、散気装置のエア−量不足や不均一により
上記膜エレメント間の間隙(原液処理槽の容積に対する
膜面積率を大とし、膜分離装置の小型化を図るために、
15mm以下とされている)や膜モジュ−ルのフレ−ム
等の原液旋回流路の途中に活性汚泥が付着堆積し、これ
が原液旋回流に対する障害になり、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、汚泥ゲル層の生成が加速度的に増加するこ
とが主要な原因の一つであることを知った。The inventors of the present invention have investigated the cause and found that the gap between the membrane elements (the membrane area ratio with respect to the volume of the stock solution treatment tank was increased due to insufficient air volume and unevenness of the air diffuser). To reduce the size of the separation device,
Activated sludge adheres and accumulates in the middle of a stock solution swirling flow path such as a frame of a membrane module or the like, and this becomes an obstacle to the stock solution swirling flow, and the stock solution swirling flow is weakened, and the membrane surface is reduced. It was found that one of the main causes was that the sludge gel layer formation suppression effect due to the undiluted solution flow was reduced and the sludge gel layer formation increased at an accelerated rate.
【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
減圧度で得ること、すなわち、長期の安定運転を可能に
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, it is an object to obtain a constant filtration flux at a stable pressure reduction degree, that is, to enable a long-term stable operation.
【0009】[0009]
【課題を解決するための手段】本発明に係る膜分離装置
の運転方法は、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装置の運転方法において、
原液中に原液流れ異常検出器を配設し、原液旋回流の異
常の検知により、その旋回流れを正常状態に回復させる
ことを特徴とする構成であり、原液流れ異常検出器に
は、圧力センサ−を使用でき、原液旋回流の異常を警報
発信により検知することができる。According to a method of operating a membrane separation apparatus according to the present invention, a membrane element having an inner side as a filtrate is immersed in a stock solution, the stock solution is swirled by aeration means, and the membrane surface is unprocessed. In an operation method of a membrane separation device for filtering a stock solution by depressurizing a filtrate side of a membrane element while washing by flowing,
The undiluted liquid flow abnormality detector is disposed in the undiluted solution, and the undiluted liquid swirl flow is detected to be abnormal to recover the swirl flow to a normal state. -Can be used, and the abnormality of the undiluted liquid swirl flow can be detected by issuing an alarm.
【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は本発明において使用する
膜分離装置を示す説明図である。図1において、1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。2,2…は原
液処理槽内に所定の間隔で配設した膜エレメントであ
り、内部に濾過液流路を有している。20は膜エレメン
ト2の濾過液集水管であり、エレメント内の濾過液流路
に連通され、膜を通過した濾過液が濾過液流路を経てこ
の濾過液集水管に集められる。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1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20,…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。Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is an explanatory diagram showing a membrane separation device used in the present invention. In FIG. 1, reference numeral 1 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. Are membrane elements disposed at predetermined intervals in the undiluted solution treatment tank, and have a filtrate flow path therein. Reference numeral 20 denotes a filtrate collection pipe of the membrane element 2, which is connected to a filtrate flow path in the element, and the filtrate that has passed through the membrane is collected in the filtrate collection pipe via the filtrate flow path. Are diffusion tubes provided below the membrane elements 2,.
The undiluted solution is disposed in the gap between the two so that it can be efficiently raised by air bubbling. The stock solution is swirled into the stock solution processing tank 1 by this air bubbling. 31 is a diffuser 3
And 32 is a blower. 4 is a filtrate extraction pipe connected to the filtrate collecting pipes 20 of the membrane elements 2,..., 41 is a decompression pump inserted into the pipe 4,
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.
【0011】6は原液の流れ異常検出器原液であり、例
えば、原液旋回流の動圧を検出する圧力センサ−(例え
ば、ストレンゲ−ジタイプの圧力センサ−)を使用でき
る。その他、原液の流れ異常による液面の波動異常、例
えば、周波数や波高さの異常を検知するセンサ−の使用
も可能である。Reference numeral 6 denotes an undiluted liquid flow abnormality detector. An undiluted solution, for example, a pressure sensor for detecting the dynamic pressure of the undiluted swirl flow (for example, a strain gauge type pressure sensor) can be used. In addition, it is also possible to use a sensor for detecting an abnormal wave on the liquid surface due to an abnormal flow of the undiluted solution, for example, an abnormal frequency or wave height.
【0012】図2の(イ)及び図2の(ロ)〔図2の
(イ)におけるロ−ロ断面図〕は、上記膜エレメント2
の一例を示し、濾過液集水管21を有する枠体20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20cm〜100c
m、厚み3mm〜15mmとされる。FIG. 2 (a) and FIG. 2 (b) [a cross-sectional view taken along a roll in FIG. 2 (a)]
And a filtrate flow path material 22 (for example, woven cloth, non-woven cloth, net, etc.) in a frame 20 having a filtrate collection pipe 21.
And a flat membrane 23 (microfiltration membrane, ultrafiltration membrane, etc.) is adhered to both sides of the frame with an adhesive 24. The flat membrane 23 is formed by laminating a membrane on a supporting substrate, Embedded with a woven fabric, a non-woven fabric or the like can be used. 3 (a) and 3 (b) [a cross-sectional view taken along a line in FIG. 3 (a)]
Another example of the above membrane element is shown. Filtrate passage grooves 201,... Are formed on both sides of the plate 20, and a filtrate outlet hole communicating with the filtrate passage grooves 201,. 202, a filtrate passage spacer 21 and a flat membrane 23 are sequentially laminated on each side of the plate 20, and the periphery of the flat membrane 23 is sealed on each side of the plate with an adhesive. is there. The dimensions of the membrane element 2 are generally 50 cm to 150 cm in height and 20 cm to 100 c in width when the dimensions of the treatment tank are made substantially equal to the dimensions of the aeration chamber of the conventional aeration type aeration tank.
m and a thickness of 3 mm to 15 mm.
【0013】上記膜エレメント2,…のモジュ−ル構造
には、図4に示すように、複数箇の膜エレメント2,…
を交互間に原液通路用の間隙を介して並設し、この並設
群をフレ−ム200内に納めたものを使用できる。上記
モジュ−ルは原液処理槽の底面に直接据置くか、同底面
に設置した架台上に載置するか、吊り下げ方式により原
液処理槽内に浸漬する等により配設される。As shown in FIG. 4, the module structure of the membrane elements 2,...
Can be alternately arranged side by side through a gap for a stock solution passage, and a group in which the side-by-side group is accommodated in a frame 200 can be used. The module is placed directly on the bottom surface of the stock solution treatment tank, mounted on a gantry installed on the bottom surface, or immersed in the stock solution treatment tank in a suspended manner.
【0014】本発明により上記の膜分離装置を運転する
には、汚水(し尿、下水、生活排水、工場排水等)を貯
槽に一旦貯えたうえ、図1において、この汚水を液送ポ
ンプ52により原液処理槽1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 operate the above-mentioned membrane separation apparatus according to the present invention, sewage (human waste, sewage, domestic wastewater, factory wastewater, etc.) is temporarily stored in a storage tank, and the wastewater is fed by a liquid feed pump 52 in FIG. The solution is supplied to the stock solution treatment tank 1, and the blower 32 is driven to blow air from the air diffuser 3 to turn the stock solution. The membrane pressure of the membrane elements 2, ... is absorbed and metabolically decomposed by the aerobic microorganisms while the organic matter in the sewage is in contact with the jet air, and the aerobic microorganisms are propagated. This is taken out to the filtrate storage tank 42 through the filtrate take-out pipe 4.
【0015】この場合、エアバブリングによる原液の正
常時の旋回流速(平均流速)は、原液の液質や濃度や処
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 rate (average flow rate) of the stock solution by air bubbling at normal time varies depending on the liquid quality, concentration, processing speed, etc. of the stock solution, but is usually 0.1 to 1.0 m.
/ Sec.
【0016】上記膜エレメント2,2間の相互間隔は、
原液の水質等によっても異なるが、通常、3〜15mm
程度とされる。The mutual spacing between the membrane elements 2, 2 is
Usually 3 to 15 mm, although it depends on the quality of the stock solution.
Degree.
【0017】上記において、原液の旋回は散気管からの
エアにより原液が膜エレメント間の間隙を上昇され、そ
の上昇後にモジュ−ル周囲や下方から原液が引き込まれ
ることにより発生する。しかるに、汚水の活性汚泥濃度
は相当に高く、経時的に膜エレメントの間隙やモジュ−
ルのフレ−ムに活性汚泥が付着堆積し、これが原液の旋
回に対して障害物となり、原液の旋回流速が低下し、ま
たは旋回流分布が変動し、この原液旋回流れの異常を放
置すれば、膜面での原液流れが減退し膜面への汚泥付着
が急速に進行し、濾過抵抗が増大し、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 description, the swirling of the stock solution occurs when the stock solution is raised in the gap between the membrane elements by the air from the air diffuser, and after the rising, the stock solution is drawn from around the module or from below. However, the activated sludge concentration of the sewage is considerably high, and the space between the membrane elements and the
Activated sludge adheres and accumulates on the frame of the raw material, which becomes an obstacle to the swirling of the stock solution, and the swirling velocity of the stock solution decreases or the swirling flow distribution fluctuates. The flow of undiluted solution on the membrane surface decreases, the sludge adheres to the membrane surface rapidly, the filtration resistance increases, and a sudden decrease in filtration flux due to a sudden increase in load or a sudden increase in the degree of pressure reduction on the filtrate side of the membrane element can be avoided. Absent.
【0018】而るに、本発明においては、処理槽内の一
定位置に配設した原液流れ異常検出器によりこの原液旋
回流れの異常を検知して原液流れを正常に回復してい
る。例えば、原液旋回流速が前記正常値以下(通常、
0.1m/sec以下)になったことを検知し、即座に
ブロワ32の回転速度を増し、原液旋回流速を前記正常
値に回復している。従って、膜面での原液流れを充分に
維持し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。According to the present invention, the undiluted liquid swirl flow is detected by the undiluted liquid flow abnormality detector disposed at a fixed position in the processing tank, and the undiluted liquid flow is restored to normal. For example, the undiluted liquid swirling flow rate is equal to or less than the normal value (usually,
(0.1 m / sec or less), the rotation speed of the blower 32 is immediately increased, and the stock solution swirling flow rate is restored to the normal value. Therefore, it is possible to proceed with the filtration process while sufficiently maintaining the flow of the undiluted solution on the membrane surface and suppressing the adhesion of sludge to the membrane surface, preventing a sudden increase in load due to an increase in filtration resistance, and preventing the filtration flux and the membrane element from flowing. It can be operated stably without radical fluctuation of the pressure reduction degree on the filtrate side.
【0019】本発明に係る膜分離装置の運転方法におい
ては、原液処理槽内の複数箇所に原液流れ異常検出器を
配設しておき、これら複数の検出値の相互比較から原液
旋回流れの異常を検知することもできるる。上記原液流
れ異常検出器には、流速乃至は動圧の異常を検出するも
の外、液面の波動の異常、例えば周波数の異常を検出す
るものの使用も可能である。上記異常検知と同時に正常
回復処置、例えば、ブロワの増速による正常旋回流速の
回復を自動的に行わせることもできる。また、検出値を
コンピュ−タで解析させ、異常判定時に検出と同時に警
報を発信させることもできる。In the method for operating the membrane separation apparatus according to the present invention, the undiluted liquid flow abnormality detectors are provided at a plurality of positions in the undiluted liquid processing tank, and an abnormality of the undiluted liquid swirl flow is determined by comparing the plurality of detected values. Can also be detected. As the undiluted liquid flow abnormality detector, one that detects an abnormality of the flow velocity or the dynamic pressure, and one that detects an abnormality of the wave of the liquid surface, for example, an abnormality of the frequency can be used. At the same time as the abnormality detection, a normal recovery process, for example, a recovery of the normal swirling flow speed by increasing the speed of the blower can be automatically performed. In addition, the detected value can be analyzed by a computer, and when an abnormality is determined, an alarm can be issued simultaneously with the detection.
【0020】[0020]
〔実施例〕膜エレメントには図2に示すものを使用し、
枠体20の寸法は、縦1060mm、横(巾)610m
m、厚み最大13mm、最小2mmとし、膜23には膜
面積0.45m2のポリオレフィン系精密濾過膜を両面
に使用した。モジュ−ルには、図4に示したものを使用
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。膜分離装置には図1
に示したものを使用した。原液にはMLSS濃度10,00
0〜15,000mg/リットルの活性汚泥溶液を使用
し、所定位置にストレンゲ−ジタイプの圧力計を配設
し、その位置での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0.5
m3/m2・dayとするように減圧度を調整した。運転開
始5ケ月経過後、上記汚水旋回流速が0.1m/secに
低下したので、散気流量を増加して初期のほぼ0.5m
/secの旋回流速に回復させた。運転開始8ケ月に至る
までの減圧度は、0.1〜0.2kg/cm2であり、
安定していた。[Example] The membrane element shown in FIG. 2 was used,
The dimensions of the frame 20 are 1060 mm long and 610 m wide (width).
m, the maximum thickness was 13 mm, and the minimum was 2 mm. A polyolefin microfiltration membrane having a membrane area of 0.45 m 2 was used on both sides of the membrane 23. The module shown in FIG. 4 was used, the number of the membrane elements 2 was 10, and the minimum distance between the membrane elements was 4 mm. Fig. 1
The ones shown in Table 1 were used. MLSS concentration of 10,000 in stock solution
Using an activated sludge solution of 0 to 15,000 mg / liter, a strain gauge type pressure gauge is provided at a predetermined position, and a diffused air flow rate is set so that the sewage swirl flow velocity at that position is approximately 0.5 m / sec. And set the decompression pump to run for 8 minutes.
Intermittent operation with a repetition of 2 minutes of stoppage and a filtration flux of approximately 0.5
The degree of pressure reduction was adjusted to m 3 / m 2 · day. Five months after the start of operation, the sewage swirl flow velocity was reduced to 0.1 m / sec.
/ Sec. The degree of decompression until 8 months from the start of operation is 0.1 to 0.2 kg / cm 2 ,
It was stable.
【0021】〔比較例〕実施例に対し、汚水旋回流速の
回復操作を行わなかった以外、実施例に同じとした。運
転開始8ケ月経過後、減圧度がほぼ0.6kg/cm2
となり、運転続行が不可能となった。[Comparative Example] The same operation as in the example was performed except that the recovery operation of the sewage swirl velocity was not performed. After a lapse of 8 months from the start of operation, the degree of decompression is approximately 0.6 kg / cm 2
It became impossible to continue driving.
【0022】[0022]
【発明の効果】本発明に係る膜分離装置の運転方法によ
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つつ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 method for operating a membrane separation apparatus according to the present invention, in the treatment of sewage, in particular, the membrane separation activated sludge method, the membrane separation apparatus can sufficiently suppress the membrane contamination and sufficiently suppress the increase in load. Stable operation is possible, and stable operation is possible for a long period of time.
【図1】本発明において使用する膜分離装置の一例を示
す説明図である。FIG. 1 is an explanatory diagram showing an example of a membrane separation device used in the present invention.
【図2】図1の膜分離装置における膜エレメントの一例
を示す説明図である。FIG. 2 is an explanatory diagram showing an example of a membrane element in the membrane separation device of FIG.
【図3】図1の膜分離装置における膜エレメントの別例
を示す説明図である。FIG. 3 is an explanatory view showing another example of the membrane element in the membrane separation device of FIG.
【図4】図1の膜分離装置における膜モジュ−ルの一例
を示す説明図である。FIG. 4 is an explanatory diagram showing an example of a membrane module in the membrane separation device of FIG.
1 原液処理槽 2 膜エレメント 3 散気管 6 原液流れ異常検出器 Reference Signs List 1 stock solution processing tank 2 membrane element 3 air diffuser 6 stock solution flow abnormality detector
Claims (3)
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装置の運転方法において、原
液中に原液流れ異常検出器を配設し、原液旋回流の異常
の検知により、その旋回流れを正常状態に回復させるこ
とを特徴とする膜分離装置の運転方法。1. A membrane element whose inside is a filtrate side is immersed in a stock solution, the stock solution is swirled by a diffuser, and the filtrate side of the membrane element is decompressed while washing the membrane surface with the stock solution flow. A method for operating a membrane separation device for filtering a membrane, comprising: arranging an undiluted liquid flow abnormality detector in the undiluted solution, and recovering the undiluted swirl flow to a normal state by detecting the undiluted swirl flow abnormality. How to operate the device.
使用する請求項1記載の膜分離装置の運転方法。2. The method according to claim 1, wherein a pressure sensor is used as the undiluted liquid flow abnormality detector.
る請求項1記載の膜分離装置の運転方法。3. The method for operating a membrane separation apparatus according to claim 1, wherein an abnormality of the swirling flow of the stock solution is detected by issuing an alarm.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP30125996A JPH10128085A (en) | 1996-10-25 | 1996-10-25 | Operating method of membrane separation device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP30125996A JPH10128085A (en) | 1996-10-25 | 1996-10-25 | Operating method of membrane separation device |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH10128085A true JPH10128085A (en) | 1998-05-19 |
Family
ID=17894673
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP30125996A Pending JPH10128085A (en) | 1996-10-25 | 1996-10-25 | Operating method of membrane separation device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH10128085A (en) |
-
1996
- 1996-10-25 JP JP30125996A patent/JPH10128085A/en active Pending
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