JPH10249344A - Membrane separator, its operation, activated-sludge treating device and water treating equipment - Google Patents

Membrane separator, its operation, activated-sludge treating device and water treating equipment

Info

Publication number
JPH10249344A
JPH10249344A JP9061218A JP6121897A JPH10249344A JP H10249344 A JPH10249344 A JP H10249344A JP 9061218 A JP9061218 A JP 9061218A JP 6121897 A JP6121897 A JP 6121897A JP H10249344 A JPH10249344 A JP H10249344A
Authority
JP
Japan
Prior art keywords
raw water
membrane
water
supply means
tank
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
Application number
JP9061218A
Other languages
Japanese (ja)
Other versions
JP3726404B2 (en
Inventor
Toshiji Onoe
利次 尾上
Kazuhiko Nishimura
和彦 西村
Masahiro Kihara
正浩 木原
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.)
Toray Industries Inc
Original Assignee
Toray Industries Inc
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 Toray Industries Inc filed Critical Toray Industries Inc
Priority to JP06121897A priority Critical patent/JP3726404B2/en
Publication of JPH10249344A publication Critical patent/JPH10249344A/en
Application granted granted Critical
Publication of JP3726404B2 publication Critical patent/JP3726404B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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

Abstract

PROBLEM TO BE SOLVED: To prevent the lowering of performance in the initial stage of operation in the case where a separation membrane is dipped in a raw water tank to separate the component in the raw water supplied from a raw water supply means by providing a water supply means for dipping the membrane in a liq. lower in concn. than the raw water. SOLUTION: The raw water is supplied to a raw water tank 1 by a raw water supply means 3, and water is supplied by a water supply means 4. A separation membrane 2 is dipped in the raw water tank 1 so that an intermembrane differential pressure necessary for the separation is obtained by the difference between the liq. level in the tank and the level of the outlet 5 of the water permeated through the membrane 2. Since the raw water to be separated is high in concn., a cleaning means 7 is preferably furnished. Water is supplied to the raw water tank 1 by the water supply means 4 to make the liq. concn. in the tank lower than the concn. of the raw water supplied by the means 3, the membrane 2 is dipped in the raw water tank 1 kept at a low concn. or in the water to obtain a permeated water, then the separator is started, and the lowering of performance is suppressed in the initial stage of operation.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は排水処理等に使用する膜
分離装置およびその運転方法、活性汚泥処理装置、なら
びに処理設備に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a membrane separation device used for wastewater treatment and the like, an operation method thereof, an activated sludge treatment device, and a treatment facility.

【0002】[0002]

【従来の技術】家庭、産業等、目的を問わず、年々増え
続ける水の使用量に伴い排水量の増加の一途にあり今後
も水質汚濁防止の観点から、排水処理設備には常に高い
処理能力が要求されている。
2. Description of the Related Art Regardless of purpose, such as at home, industry, etc., the amount of water used is increasing year by year, and the amount of wastewater is steadily increasing. From the viewpoint of preventing water pollution, wastewater treatment equipment always has a high treatment capacity. Has been requested.

【0003】排水の処理方法として、現在、活性汚泥法
が最も広く採用されている。現行の活性汚泥法がかかえ
る問題点としては、汚泥管理が困難であること、処理水
と汚泥の固液分離に大きな沈殿池を必要とすること等が
ある。
[0003] As a method for treating wastewater, the activated sludge method is currently most widely adopted. Problems associated with the current activated sludge method include difficulty in sludge management and the necessity of a large sedimentation tank for solid-liquid separation of treated water and sludge.

【0004】そこでこの固液分離に膜分離を用いること
で処理量が増えるに従って広大になっていた沈殿池を縮
小或いは削減でき、その他にも汚泥の高濃度化による活
性汚泥槽の小型化、メンテナンス性の向上、処理水質の
安定などのメリットが期待できることから膜分離を用い
た排水処理の技術が要求されている。
[0004] By using membrane separation for the solid-liquid separation, the sedimentation basin, which has been enlarged as the processing amount increases, can be reduced or reduced. In addition, the activated sludge tank can be downsized and maintained by increasing the concentration of sludge. There are demands for a technology of wastewater treatment using membrane separation because it can be expected to have merits such as improvement in water quality and stability of treated water quality.

【0005】排水処理では膜分離に関わらず、大量処理
が可能で流入排水の変動に強く、長期にわたり安定して
運転でき、処理コストが低い技術が要求される。まず高
濃度の活性汚泥処理水を膜分離により処理する場合は、
分離の際に膜面への汚泥の堆積が激しく性能が低下しや
すい。
[0005] Regarding wastewater treatment, there is a demand for a technique capable of performing a large amount of treatment irrespective of membrane separation, being resistant to fluctuations in inflow wastewater, capable of operating stably for a long period of time, and having a low treatment cost. First, when treating high concentration activated sludge treated water by membrane separation,
At the time of separation, the sludge is deposited on the membrane surface, and the performance tends to deteriorate.

【0006】そこでチューブラー型分離膜を用いクロス
フロー運転によって活性汚泥処理水の固液分離を行う技
術がし尿処理等で実用化されている。この方法では内壁
に分離膜を有する管に活性汚泥処理水を供給し、管の入
口圧よりも出口圧を絞ることで膜間に圧力を与え、かつ
間内壁の分離膜面に所定の流速を与えて膜面へ堆積する
汚泥を流しとりながら汚泥分離を行うものである。しか
し、この方法は活性汚泥処理水を分離膜に循環供給する
必要があり、高濃度の活性汚泥処理水は高粘度となるた
め、その循環にかかる多くの動力を要し、処理コストが
高いこと、分離膜に強度が要求されることが難点であっ
た。
Therefore, a technique of performing solid-liquid separation of the activated sludge treated water by cross-flow operation using a tubular separation membrane has been put to practical use in human waste treatment and the like. In this method, activated sludge treatment water is supplied to a pipe having a separation membrane on the inner wall, pressure is applied between the membranes by narrowing the outlet pressure from the inlet pressure of the pipe, and a predetermined flow rate is applied to the separation membrane surface of the inner wall. Sludge separation is performed while sludge that is applied and accumulates on the membrane surface is washed away. However, in this method, it is necessary to circulate and supply the activated sludge treatment water to the separation membrane, and since the high-concentration activated sludge treatment water has a high viscosity, a large amount of power is required for the circulation and the treatment cost is high. However, it has been a problem that strength is required for the separation membrane.

【0007】最近では分離膜を活性汚泥処理槽に浸漬し
て分離膜の透過側を減圧あるいは透過水取り出し口を槽
内液位よりも低くし水位差により汚泥分離を行う方法が
研究されている。本技術は活性汚泥処理槽には生物処理
用の曝気流を膜面に効果的に付与することにより膜面に
堆積する汚泥を流しとりながら運転できるため、処理コ
ストが安価な点で期待されている技術である。
Recently, a method has been studied in which a separation membrane is immersed in an activated sludge treatment tank, and the permeate side of the separation membrane is depressurized or the permeate outlet is set lower than the liquid level in the tank to separate sludge by a difference in water level. . This technology can be operated while flowing sludge accumulated on the membrane surface by effectively applying an aeration flow for biological treatment to the membrane surface in the activated sludge treatment tank. Technology.

【0008】しかし高濃度の原水下で使用することか
ら、膜面への汚泥が付着堆積しやすく、膜に負担の大き
な運転を行うと、膜面に強固に堆積した汚泥を剥離する
ことができなくなる。よって膜に負担の少ない運転を行
わざるを得ず運転圧力が上昇した際には、取得水量の低
下が否めない。そこで膜面への汚泥の付着堆積を極力抑
える技術が重要となることが重要となる。
However, since it is used under high-concentration raw water, sludge easily adheres and deposits on the membrane surface, and when a heavy load is applied to the membrane, sludge that has firmly accumulated on the membrane surface can be removed. Disappears. Therefore, when the operation pressure increases due to the operation with a small burden on the membrane, the decrease in the obtained water amount cannot be denied. Therefore, it is important that technology to minimize the adhesion and deposition of sludge on the membrane surface becomes important.

【0009】そこで運転初期から膜面への汚泥の堆積を
抑止できれば、膜の運転寿命の増大につながるというた
め、初期の膜への負担を軽減する観点から特開平6−3
1141号公報に開示されているように、定量運転を行
う際に徐々に取得水量を上げ一定値に保持することで始
動時の膜性能の低下を抑える技術もある。
Therefore, if the accumulation of sludge on the membrane surface can be suppressed from the early stage of operation, the operating life of the membrane will be prolonged.
As disclosed in Japanese Patent Publication No. 1141, there is also a technique for suppressing a decrease in membrane performance at the time of starting by gradually increasing the obtained water amount and maintaining the obtained water amount at a constant value when performing a fixed amount operation.

【0010】[0010]

【発明が解決しようとする課題】しかし、始動時の透過
水の取得方法を軽減しても、分離膜を槽内に浸漬する方
法では、高濃度の活性汚泥槽内に分離膜を浸漬する場
合、あるいは分離膜を収容した原水槽内に高濃度の活性
汚泥処理水を供給する場合のどちらでも、槽内で膜が原
水中に浸漬された時点で既に膜面への汚泥が付着し運転
初期に性能低下が起こる。
However, even if the method of obtaining permeated water at the time of starting is reduced, the method of immersing the separation membrane in the tank is difficult in the method of immersing the separation membrane in a high-concentration activated sludge tank. , Or when supplying high-concentration activated sludge treatment water to the raw water tank containing the separation membrane, the sludge already adhered to the membrane surface when the membrane was immersed in the raw water in the tank. Performance is reduced.

【0011】これは運転開始時に分離膜の透過側を開放
したまま原水槽に高濃度の液体を供給すると水位差によ
り高濃度の液体が膜面を透過するとともに、膜面へ汚泥
が付着しはじめる。分離膜の透過側を閉止したままであ
ると液体の透過はないが運転開始(透過側の開放あるい
は減圧)とともに急激に液体が膜面を透過し、汚泥が付
着堆積しはじめる。
This is because when a high-concentration liquid is supplied to the raw water tank with the permeation side of the separation membrane open at the start of operation, the high-concentration liquid permeates through the membrane surface due to a difference in water level, and sludge starts to adhere to the membrane surface. . If the permeate side of the separation membrane is kept closed, there is no liquid permeation, but when the operation is started (opening of the permeate side or depressurization), the liquid permeates the membrane surface rapidly and sludge starts to deposit and accumulate.

【0012】曝気流を与えながら分離膜を浸漬しすれば
付着物除去の効果が期待できるが、分離膜の透過性能と
除去性能が高いと、高濃度の原水下では、膜面への付着
が多く強固になる。
If the separation membrane is immersed while applying an aeration flow, the effect of removing adhering substances can be expected. However, if the permeability and removal performance of the separation membrane are high, the adhesion to the membrane surface under high-concentration raw water is high. Many become strong.

【0013】また高濃度の原水に浸漬された分離膜から
運転開始時に透過水を取得しすると、膜面への付着堆積
が促進され、運転初期に性能の低下が大きくなる。
Further, if permeated water is obtained at the start of operation from a separation membrane immersed in high-concentration raw water, adhesion and deposition on the membrane surface is promoted, and the performance is greatly reduced at the beginning of operation.

【0014】よって高濃度の活性汚泥処理水を分離膜を
用いて処理するため運転開始以前と直後に膜面へ汚泥の
付着が起こり性能低下を起こす。使用に伴う性能低下は
否めないが、使用条件が過酷であること、大量処理にな
れば膜の性能低下は微量であっても大きく影響すること
から、できるだけ膜への負担の小さな運転を行う必要が
あった。
[0014] Therefore, since high-concentration activated sludge treated water is treated using a separation membrane, sludge adheres to the membrane surface immediately before and immediately after the start of operation, resulting in a deterioration in performance. It is undeniable that the performance decreases with use.However, it is necessary to operate with as little burden on the membrane as possible because the use conditions are severe and the performance of the membrane will be greatly affected even if the performance is very small even if the amount is large. was there.

【0015】[0015]

【発明を解決するための手段】本発明は、上記課題を解
決するために、基本的に下記の構成により達成される。
The present invention is basically achieved by the following constitutions in order to solve the above-mentioned problems.

【0016】即ち、「分離膜を原水槽に浸漬し、原水供
給手段から供給される原水中の成分を分離する膜分離装
置において、原水より低濃度の液体で浸漬するための水
供給手段を有することを特徴とする膜分離装置。」また
は「分離膜を原水槽に浸漬し、原水供給手段から供給さ
れる原水中の成分を分離する膜分離装置において、分離
膜が原水中へ浸漬される際に、水供給手段を用い槽内の
原水を低い濃度に調整して浸漬し、膜透過水を取得した
後に、該原水供給手段を用いて槽内原水の濃度を上げる
ことを特徴とする膜分離装置の運転方法。」である。
That is, "a membrane separation apparatus for immersing a separation membrane in a raw water tank and separating components in raw water supplied from the raw water supply means has a water supply means for immersion with a liquid having a lower concentration than the raw water. Or a membrane separation device that immerses a separation membrane in a raw water tank and separates components in raw water supplied from raw water supply means when the separation membrane is immersed in raw water. Then, the raw water in the tank is adjusted to a low concentration using a water supply means and immersed, and after obtaining the membrane permeated water, the concentration of the raw water in the tank is increased using the raw water supply means. Method of operating the device. "

【0017】本発明により膜分離装置に設けた水供給手
段を用いて原水槽内あるいは原水の濃度を低く調整する
ことによって、原水槽内に分離膜が浸漬される際、ある
いは原水槽内の分離膜に原水が供給される際に起こる、
膜面への被分離物の付着堆積が抑止でき、運転初期に起
こる性能低下を抑止することができる。
By adjusting the concentration of the raw water in the raw water tank or the raw water to be low by using the water supply means provided in the membrane separation apparatus according to the present invention, the separation membrane is immersed in the raw water tank, or the separation in the raw water tank is performed. Occurs when raw water is supplied to the membrane,
Adhesion and deposition of the separation object on the film surface can be suppressed, and performance degradation that occurs at the beginning of operation can be suppressed.

【0018】本発明を図面にしたがって説明するが特に
図面に限定されるものではない。図1は本発明の膜分離
装置の一例である。原水槽1は分離膜2を収容し、原水
供給手段3により原水を、あるいは水供給手段4により
水を収容可能であれば、大きさ、形状は特に限定するも
のではない。図2のように既設の原水槽1に分離膜を浸
漬し、それに水供給手段4を有するのもよい。また原水
槽1は底面が排出口に向かいテーパになっており、原水
を容易に排出可能な形状であると作業が短期化されるの
で好ましい。
The present invention will be described with reference to the drawings, but is not particularly limited to the drawings. FIG. 1 shows an example of the membrane separation device of the present invention. The size and shape of the raw water tank 1 are not particularly limited as long as the raw water tank 1 can store the separation membrane 2 and can store raw water by the raw water supply means 3 or water by the water supply means 4. As shown in FIG. 2, the separation membrane may be immersed in the existing raw water tank 1, and a water supply means 4 may be provided therein. Further, the bottom of the raw water tank 1 is tapered toward the discharge port, and it is preferable that the raw water tank 1 has a shape capable of easily discharging the raw water, since the work is shortened.

【0019】膜分離装置は分離膜2が原水槽1内に浸漬
され、図1のように槽内の液位と分離膜の透過水の取り
出し口5との水位差により分離に必要な膜間差圧を得る
もの、あるいは図2のように単に分離膜の透過側をポン
プ6等の吸引側に接続するような減圧によって膜間差圧
を得るものが好ましい。水位差とポンプを併用すればポ
ンプの負担が少なく処理水が安定して取得できより好ま
しい。しかしその方法については特に限定するものでは
ない。分離する原水が高濃度であるため洗浄手段を備え
ていることがより好ましい。
In the membrane separation apparatus, the separation membrane 2 is immersed in a raw water tank 1, and as shown in FIG. 1, the separation between the membranes required for separation is performed based on the difference between the liquid level in the tank and the outlet 5 of the permeated water of the separation membrane. It is preferable to obtain a differential pressure, or to obtain the transmembrane pressure by reducing the pressure by simply connecting the permeate side of the separation membrane to the suction side of the pump 6 or the like as shown in FIG. The combined use of a water level difference and a pump is more preferable because the burden on the pump is small and the treated water can be stably obtained. However, the method is not particularly limited. Since the raw water to be separated has a high concentration, it is more preferable to provide a washing means.

【0020】洗浄手段7は図1に示すようにバブリング
により原水槽1内に循環流を起こし膜面の付着物を流し
取るものでもよいし、図2のようにプロペラ等の攪拌に
よる循環流を用いてもよい。スプレーのようなもので膜
面に液体を吹き付け付着物を除去したり、分離膜に設け
たバブリング等の振動手段等により膜を揺れ動かし付着
物を除去するものでもよい。しかし特に限定されるもの
ではない。洗浄手段7は常時あるいは間欠的に運転され
ても、性能低下時に運転されるてもよい。運転方法につ
いても特に限定するものではない。
The cleaning means 7 may be a means for generating a circulating flow in the raw water tank 1 by bubbling as shown in FIG. 1 to wash away the deposits on the membrane surface, or as shown in FIG. May be used. A liquid such as a spray may be applied to the surface of the membrane to remove the adhering substance, or the adhering substance may be removed by shaking the membrane by vibrating means such as bubbling provided on the separation membrane. However, it is not particularly limited. The cleaning means 7 may be operated constantly or intermittently, or may be operated when the performance is deteriorated. The driving method is not particularly limited.

【0021】原水供給手段3は原水槽1に分離される成
分を有する液体を供給可能なものであれば、形や方法に
ついては特に限定されるものではない。図1のようにポ
ンプや図2のように隣の液槽と連通可能に接続するもの
や図3のように隣の液槽から流下するものであってもよ
く、その設置位置も特に限定されるものではない。原水
供給手段3に図1,2,3のようにバルブまたは弁等を
設けておくと閉止したり、供給量を調節することができ
好ましい。槽内から原水があふれないように原水槽1に
オーバーフロー口、あるいは原水供給手段3ボールタッ
プあるいはレベルセンサーと連動したものであると過剰
に原水が供給されずより好ましい。
The raw water supply means 3 is not particularly limited in form and method as long as it can supply a liquid having a component to be separated into the raw water tank 1. As shown in FIG. 1, a pump may be connected to be communicable with an adjacent liquid tank as shown in FIG. 2, or may be a liquid that flows down from an adjacent liquid tank as shown in FIG. Not something. It is preferable to provide a valve or a valve or the like in the raw water supply means 3 as shown in FIGS. It is more preferable that the raw water tank 1 is provided with an overflow port, or a raw water supply means 3 in conjunction with a ball tap or a level sensor so that the raw water does not overflow from the tank, so that the raw water is not excessively supplied.

【0022】水供給手段4は原水槽1内に水を供給し原
水供給手段3より供給される原水の濃度よりも槽内の液
濃度を下げることができるものであればよく、方法につ
いては特に限定されるものではない。図1のように原水
供給手段3とは別個に設けてあれば本発明を実施可能で
あり好ましい。更に好ましくは図4のように原水供給手
段3と一体で切り替え可能に接続されていることで、原
水供給手段3、水供給手段4のバルブまたは弁の切り替
え、または開度を調節することにより濃度の低く調整し
た原水を槽内に直接供給できるのでよい。
The water supply means 4 is only required to supply water into the raw water tank 1 and lower the concentration of the raw water in the tank than the concentration of the raw water supplied from the raw water supply means 3. It is not limited. The present invention can be practiced if it is provided separately from the raw water supply means 3 as shown in FIG. More preferably, as shown in FIG. 4, the connection with the raw water supply means 3 is switchably connected so that the concentration of the raw water supply means 3 and the water supply means 4 can be changed by switching the valves or the valves or adjusting the opening degree. Raw water adjusted to a low level can be supplied directly into the tank.

【0023】原水供給手段3により供給される原水は用
途によって各種あり、排水の凝集処理液や菌体の分離等
も用途の一つである。使用する原水は高濃度であるほど
本発明の効果は大きくなるが、膜に負担の少ない運転を
行うのであれば低濃度の原水で実施することも好まし
い。固形分を含む原水であれば適用可能であり、原水、
用途ともに特に限定されるものではない。
There are various types of raw water supplied by the raw water supply means 3 depending on the use, and one of the uses is a flocculation treatment solution of wastewater or separation of cells. The higher the concentration of the raw water used, the greater the effect of the present invention, but if the operation is performed with less load on the membrane, it is also preferable to use the raw water with a low concentration. Any raw water containing solids is applicable.
The applications are not particularly limited.

【0024】水供給手段により供給される液体に関して
は水道水、河川水、海水等でもよい。一時的に原水を分
離した液を用いるのも良く、固形分の濃度が原水よりも
低ければ特に限定されるものではない。水供給手段4に
より低く調節される原水の濃度は、低いほど膜面への負
担が少なく好ましいが、濃度については特に限定される
ものではない。
The liquid supplied by the water supply means may be tap water, river water, seawater, or the like. It is also possible to use a liquid obtained by temporarily separating raw water, and there is no particular limitation as long as the concentration of the solid content is lower than that of the raw water. The lower the concentration of the raw water adjusted by the water supply means 4 is, the lower the load on the membrane surface is, and the more preferable, but the concentration is not particularly limited.

【0025】活性汚泥処理水を原水とし、汚泥分離を行
う活性汚泥処理装置乃至はその設備に用いることも可能
である。活性汚泥処理装置は、生活排水や工業廃水ある
いは屎尿などBOD、COD乃至は窒素分などの多い排
水を被処理水として、曝気装置を備え好気的微生物処理
をして活性汚泥が発生する活性汚泥槽と、発生した活性
汚泥と液体成分を分離する原水槽からなり、この原水槽
に膜分離が適用される。活性汚泥槽から原水槽への被処
理水の移送手段としては、自然流入する配管を用いても
良いし、ポンプを用いることもできるが、エネルギーコ
ストやメンテナンスの観点からは前者の方が好ましい。
また、原水槽に堆積してくる汚泥は、排出口から取り出
し、水分をさらに除いて処分するか、調整槽乃至は活性
汚泥槽に戻し再処理することもできる。また、かかる活
性汚泥装置の前に、髪の毛などのゴミをのぞく除さ工程
設備、流量を一定に保つ調整槽を設けた活性汚泥設備と
して構成することが好ましい。
It is also possible to use the activated sludge treated water as raw water for an activated sludge treatment apparatus for separating sludge or its equipment. The activated sludge treatment device is provided with an aeration device and performs aerobic microbial treatment to generate activated sludge by using wastewater such as BOD, COD or nitrogen such as domestic wastewater, industrial wastewater, or human waste as a treatment target water. It comprises a tank and a raw water tank for separating the generated activated sludge from the liquid component, and membrane separation is applied to this raw water tank. As means for transferring the water to be treated from the activated sludge tank to the raw water tank, a pipe that naturally flows in may be used, or a pump may be used, but the former is preferable from the viewpoint of energy cost and maintenance.
Further, the sludge that has accumulated in the raw water tank can be taken out from the discharge port and disposed of after further removing water, or can be returned to the conditioning tank or the activated sludge tank for reprocessing. In addition, it is preferable that the activated sludge apparatus is provided as an activated sludge apparatus provided with a process facility for removing dust such as hair and an adjusting tank for keeping the flow rate constant before the activated sludge device.

【0026】活性汚泥装置では、初めて運転を開始する
とき、分離膜モジュールの交換、洗浄乃至はその他のメ
ンテナンスなどにより、膜が一旦浸漬状態でなくなった
場合などの後において、水供給手段により槽内の汚泥濃
度を3000mg/L以下に調節することが好ましく、
更に好ましくは1000mg/L以下とすることであ
る。最も膜に負担が少なく好ましいものは原水供給手段
3と別個あるいは一体であるに関わらず原水供給手段3
からの供給を停止し、水供給手段4のみを使用して分離
膜2を水中に浸漬することである。これにより槽内の汚
泥(固形分)濃度をほぼ0にすることができるためよ
い。
In the activated sludge apparatus, when the operation is started for the first time, after the membrane is temporarily out of the immersion state due to replacement of the separation membrane module, washing, or other maintenance, etc., the water supply means is used to supply water to the tank. It is preferable to adjust the sludge concentration to 3000 mg / L or less,
More preferably, it is 1000 mg / L or less. The one with the least burden on the membrane is preferable, regardless of whether it is separate or integral with the raw water supply means 3.
Is stopped, and the separation membrane 2 is immersed in water using only the water supply means 4. This is preferable because the sludge (solid content) concentration in the tank can be reduced to almost zero.

【0027】低濃度に調節された原水槽1内または水中
に分離膜2を浸漬した状態で透過水を取得し運転開始す
れば、高濃度の原水下で運転を開始するよりも膜への負
担が少なく好ましい。
If the permeated water is obtained and the operation is started in a state where the separation membrane 2 is immersed in the raw water tank 1 or the water adjusted to a low concentration, the load on the membrane is higher than when the operation is started under the high concentration of the raw water. Is preferred.

【0028】本発明の膜分離装置の運転方法は運転初期
に起こる膜面への汚れの付着を抑止するものである。低
濃度の原水にて膜透過水が取得できれば、水供給手段4
を停止あるいは閉止し、原水供給手段3を用いて原水槽
内の濃度を高めればよい。膜透過水の取得は、定量運転
であればインバータ制御等の自動制御を用いれば運転条
件の設定は数秒で行えてよい。水位差等を用いた場合は
槽内に浸漬した直後から膜透過水が取得できる。低濃度
の原水あるいは水中での運転は長いと膜面への負担は軽
くなる。取得の際の運転圧力の確認等、状態確認のため
に長く運転するのも好ましい。しかし運転開始から原水
の投入までの時間はできるだけ短い方が効率的であり、
正常な運転が行えれば10秒以内が好ましいが、これら
の時間については特に限定するものではない。膜透過水
は大量に取得すると膜面への汚れの付着が大きいため、
運転圧力を50kPa以下となるように取得することが
好ましい。更に好ましくは30kPaであり、最も好ま
しくは10kPa以下であるが、取得量については特に
限定するところではないが、槽内の濃度が3000mg
/L以下の状態で、膜面積当たりの取得量で0.05〜
1.2m3/m2が好ましく、0.2〜0.5m3/m2
より好ましい。
The method for operating the membrane separation apparatus of the present invention is to prevent the contamination of the membrane surface which occurs at the beginning of the operation. If the membrane permeated water can be obtained with low-concentration raw water, water supply means 4
May be stopped or closed, and the raw water supply means 3 may be used to increase the concentration in the raw water tank. The acquisition of the membrane permeated water can be performed in a few seconds by using automatic control such as inverter control in the case of quantitative operation. When a water level difference or the like is used, membrane permeated water can be obtained immediately after immersion in the tank. The longer the operation in low concentration raw water or water, the less the burden on the membrane surface. It is also preferable to operate for a long time to check the state, such as checking the operating pressure at the time of acquisition. However, the shorter the time from the start of operation until the input of raw water is more efficient,
If normal operation can be performed, the time is preferably within 10 seconds, but these times are not particularly limited. If a large amount of permeated water is obtained, the adhesion of dirt to the membrane surface is large.
It is preferable to obtain the operating pressure so as to be 50 kPa or less. More preferably, it is 30 kPa, and most preferably, it is 10 kPa or less. Although the amount to be obtained is not particularly limited, the concentration in the tank is 3000 mg.
/ L or less, the amount obtained per membrane area is 0.05 to
1.2 m 3 / m 2 is preferred, and 0.2 to 0.5 m 3 / m 2 is more preferred.

【0029】原水供給手段3を用いて槽内の濃度を上げ
る際には急激に高濃度の原水を供給すると槽内の濃度が
急激に上がるため徐々に供給することが好ましい。しか
し透過水を取得した後、槽内の濃度を上げるのであれば
特に限定するところではない。
When the raw water supply means 3 is used to increase the concentration in the tank, it is preferable to supply the raw water at a high concentration suddenly because the concentration in the tank increases rapidly. However, there is no particular limitation as long as the concentration in the tank is increased after obtaining the permeated water.

【0030】本発明の膜分離装置乃至はその運転方法に
より、新品の分離膜を運転開始するときはもちろん、単
に槽内の原水を排出した際や、薬液により分離膜の機能
を回復した際に使用することも好ましい。
By using the membrane separation apparatus or its operation method of the present invention, not only when starting a new separation membrane, but also when simply discharging the raw water in the tank or when the function of the separation membrane is restored by a chemical solution. It is also preferred to use.

【0031】分離膜2は平膜であれば構造が簡単で、散
気流により付着する汚れを掻き取りやすく、管状膜であ
れば圧力に強く、中空糸膜は単位容積当りの膜面積を大
きくとれ、それぞれによい。しかし、いかなる形態の膜
であるかは特に限定されるものではない。ただ原水中に
浸漬され、透過水を取得するため、分離機能を有する膜
面が原水と接触するような形態をとっており、原水側と
膜透過側とが液密にシールされていることが好ましい。
分離機能としては精密ろ過膜、限外ろ過膜が適当であり
最も好ましい。精密瀘過膜は、膜面に多数の孔があいた
多孔質膜であり、孔径が1〜0.1μmである膜をい
う。限外瀘過膜は、やはり膜面に多数の孔があいた多孔
質膜であり、孔径が0.1〜0.01μmである膜をい
う。
If the separation membrane 2 is a flat membrane, it has a simple structure, and it is easy to scrape off dirt adhering by a diffused flow. If it is a tubular membrane, it is resistant to pressure, and a hollow fiber membrane can have a large membrane area per unit volume. Good for each. However, the type of film is not particularly limited. However, it is immersed in raw water to obtain permeate, so that the membrane surface with the separation function is in contact with raw water, and the raw water side and the membrane permeate side are sealed in a liquid-tight manner. preferable.
As the separation function, a microfiltration membrane or an ultrafiltration membrane is suitable and most preferable. The microfiltration membrane is a porous membrane having many pores on the membrane surface, and has a pore diameter of 1 to 0.1 μm. The ultrafiltration membrane is also a porous membrane having a large number of pores on the membrane surface, and has a pore diameter of 0.1 to 0.01 μm.

【0032】運転動力が小さければ逆浸透膜でもよく、
原水にあわせて選択することが好ましい、しかしこれに
ついても特に限定されるものではない。分離膜素材とし
ては有機素材であれば安価でありよい。有機素材として
酢酸セルロ−ス、ポリカ−ボネ−ト、ニトロセルロ−
ス、セルロ−ス、ポリスルホン、ポリエ−テルスルホ
ン、ポリアクリロニトリル、架橋ポリビニルアルコ−
ル、ポリフロロエチレン等が上げられるが、これらに限
定されるものではない。またその膜構造は膜の少なくと
も片面に緻密層を持ち、緻密層から膜内部あるいはもう
片方の面に向けて徐々に大きな孔径の微細孔を有する非
対称膜も例示できる。あるいは、繊維、多孔質体等の支
持基材の上に有機素材をコーティングするのもよい。無
機素材であれば薬液等に侵されにくく雑多な原水にも半
永久的に強度を保持できよい。また交換の予測される部
分と半永久的に使用される部分に使用素材を分けること
も好ましい。しかし分離機能を有する膜であれば素材は
特に限定するものではない。
If the driving power is small, a reverse osmosis membrane may be used.
It is preferable to select according to the raw water, but this is not particularly limited. The separation membrane material may be inexpensive as long as it is an organic material. Cellulose acetate, polycarbonate, nitrocellulose as organic materials
, Cellulose, polysulfone, polyethersulfone, polyacrylonitrile, cross-linked polyvinyl alcohol
And polyfluoroethylene, but are not limited thereto. The film structure can also be exemplified by an asymmetric film having a dense layer on at least one surface of the film and gradually having fine pores with a large diameter from the dense layer toward the inside of the film or the other surface. Alternatively, an organic material may be coated on a supporting substrate such as a fiber or a porous body. If it is an inorganic material, it can be semi-permanently maintained in various raw waters which are hardly affected by a chemical solution or the like. It is also preferable to divide the used material into a part expected to be replaced and a part used semi-permanently. However, the material is not particularly limited as long as it has a separation function.

【0033】(実施例1)装置の原水供給手段には工場
排水の活性汚泥処理槽から処理水(MLSS約12000mg/
L)を水中ポンプを用いて原水槽(1.2×0.5×1.8=1.1
m3)にスクリーン(1mm目)を介してくみ上げるもの
を用いた。原水供給手段は原水槽上部に設け、水供給手
段は原水供給手段とは別に原水槽上部に設け、水供給手
段には工場内の湖水ラインを使用する。原水槽は高さ1.
6mのところにオーバーフロー口を設け液位を一定に保て
るようにした。分離膜はポリアクリロニトリル外圧多孔
質中空糸膜(公称孔径0.01μm、外径680μm内
径400μm)を5000本束ねた長さ750mm中空糸膜モジ
ュール(膜面積約6.5m2)を使用する。原水槽に中空糸
膜モジュールを浸漬し透過側をマグネットポンプにて吸
引して膜透過水を得る。また中空糸膜モジュールに設け
た散気手段により常時気体を噴出させることで中空糸膜
を揺動させ膜面を洗浄する。
(Embodiment 1) Raw water supply means of the apparatus was treated water (MLSS about 12000 mg / ml) from an activated sludge treatment tank of factory wastewater.
L) using a submersible pump in a raw water tank (1.2 x 0.5 x 1.8 = 1.1
m 3 ) was pumped through a screen (1 mm). The raw water supply means is provided above the raw water tank, the water supply means is provided above the raw water tank separately from the raw water supply means, and a lake water line in a factory is used as the water supply means. The raw water tank is 1.
An overflow port was provided at 6m so that the liquid level could be kept constant. As the separation membrane, a 750 mm long hollow fiber membrane module (membrane area of about 6.5 m 2 ) in which 5000 polyacrylonitrile external pressure porous hollow fiber membranes (nominal pore diameter: 0.01 μm, outer diameter: 680 μm, inner diameter: 400 μm) are bundled is used. The hollow fiber membrane module is immersed in the raw water tank, and the permeated side is suctioned by a magnet pump to obtain the permeated water. In addition, a gas is constantly ejected by a diffuser provided in the hollow fiber membrane module to swing the hollow fiber membrane and clean the membrane surface.

【0034】まず水中ポンプを運転せずに、湖水ライン
を開放し槽内に湖水を供給した。次に散気手段に気体を
供給しながら、湖水を供給し槽からオーバーフローし出
したところでポンプをインバータ制御し、流量を0.4
5L/minの一定値に設定し、運転を開始した。安定
して透過水が得られたため、水中ポンプを稼動し、湖水
の供給をストップした。0.5、2、6、12時間後の原
水槽内の濃度、ポンプ前の圧力計から運転圧力を記録し
た。12時間後の運転圧力は6.2kPaであった。
First, without operating the submersible pump, the lake water line was opened and the lake water was supplied into the tank. Next, while supplying gas to the air diffuser, the lake was supplied and overflowed from the tank.
The operation was started at a constant value of 5 L / min. Since the permeated water was obtained stably, the submersible pump was operated and the supply of lake water was stopped. After 0.5, 2, 6, and 12 hours, the concentration in the raw water tank and the operating pressure from the pressure gauge before the pump were recorded. The operating pressure after 12 hours was 6.2 kPa.

【0035】[0035]

【表1】 (実施例2)実施例1と同様にして膜モジュールを新品
に交換し、散気手段を始動し、湖水を槽内に供給しオー
バーフロー口まで40cmとなったところから原水を供
給し、湖水と原水の両方を供給した。オーバーフローし
た時点から同流量にて分離を開始した。分離開始から約
5分で湖水の供給をストップした。その際の0.5、2、
6、12時間後の原水槽内の濃度、ポンプ前の圧力計か
ら運転圧力を記録した。12時間後の運転圧力は6.2kPa
であった。
[Table 1] (Example 2) In the same manner as in Example 1, the membrane module was replaced with a new one, the air diffuser was started, the lake water was supplied into the tank, and the raw water was supplied from the point 40 cm up to the overflow port. Both raw waters were supplied. Separation was started at the same flow rate from the time of overflow. About 5 minutes after the start of separation, the supply of lake water was stopped. 0.5,2,
After 6 and 12 hours, the concentration in the raw water tank and the operating pressure from the pressure gauge before the pump were recorded. Operating pressure after 12 hours is 6.2kPa
Met.

【0036】[0036]

【表2】 (比較例1)膜モジュールを新品にし、散気手段を始動
し、原水を供給しオーバーフロー後、同流量にて分離を
開始した。12時間後の運転圧力は8.8kPaであっ
た。
[Table 2] (Comparative Example 1) A new membrane module was used, the air diffuser was started, raw water was supplied, and after overflow, separation was started at the same flow rate. The operating pressure after 12 hours was 8.8 kPa.

【0037】[0037]

【表3】 [Table 3]

【0038】[0038]

【発明の効果】本発明により、原水中の成分の膜への付
着を抑え、膜に負担の少ない膜分離装置及び運転方法を
提供することができる。
According to the present invention, it is possible to provide a membrane separation apparatus and an operation method in which the components of raw water are prevented from adhering to the membrane and the burden on the membrane is reduced.

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

【図1】 洗浄手段に散気を用いた本発明の膜分離装
置。
FIG. 1 shows a membrane separation apparatus of the present invention using a diffuser as a washing means.

【図2】 洗浄手段に撹拌を用いた本発明の膜分離装
置。
FIG. 2 is a membrane separation apparatus of the present invention using stirring as a washing means.

【図3】 隣に液槽から原液が流下する構造の本発明の
膜分離装置。
FIG. 3 shows a membrane separation device of the present invention having a structure in which a stock solution flows down from a liquid tank next to the device.

【図4】 切り替え接続されている本発明の膜分離装
置。
FIG. 4 shows a membrane separation device according to the invention which is switched and connected.

【符号の説明】[Explanation of symbols]

1:原水槽 2:分離膜 3:原水供給手段 4:水供給手段 5:透過水取り出し口 6:ポンプ 7:洗浄手段 1: Raw water tank 2: Separation membrane 3: Raw water supply means 4: Water supply means 5: Permeated water outlet 6: Pump 7: Cleaning means

Claims (11)

【特許請求の範囲】[Claims] 【請求項1】 分離膜を原水槽に浸漬し、原水供給手段
から供給される原水中の成分を分離する膜分離装置にお
いて、原水より低濃度の液体で浸漬するための水供給手
段を有することを特徴とする膜分離装置。
1. A membrane separation apparatus for immersing a separation membrane in a raw water tank and separating components in raw water supplied from the raw water supply means, comprising a water supply means for immersing in a liquid having a lower concentration than the raw water. A membrane separation device characterized by the above-mentioned.
【請求項2】 分離膜あるいは原水槽に洗浄手段を有す
ることを特徴とする請求項1記載の膜分離装置。
2. The membrane separation apparatus according to claim 1, further comprising a washing means in the separation membrane or the raw water tank.
【請求項3】 原水槽への原水供給手段とは別個に水供
給手段を有することを特徴とする請求項1記載の膜分離
装置。
3. The membrane separation apparatus according to claim 1, further comprising a water supply means separately from the raw water supply means to the raw water tank.
【請求項4】 原水槽への原水供給手段と水供給手段が
一体であり、切り替え可能に構成されていることを特徴
とする請求項1記載の膜分離装置。
4. The membrane separation device according to claim 1, wherein the raw water supply means and the water supply means for the raw water tank are integrated and switchable.
【請求項5】 分離膜を原水槽に浸漬し、原水供給手段
から供給される原水中の成分を分離する膜分離装置にお
いて、予め、水供給手段を用いて原水より低濃度の液体
で浸漬し、膜透過水を取得した後に、該原水供給手段を
用いて槽内原水の濃度を上げることを特徴とする膜分離
装置の運転方法。
5. A membrane separation device for immersing a separation membrane in a raw water tank and separating components in raw water supplied from raw water supply means by previously immersing the separation membrane in a liquid having a lower concentration than raw water using water supply means. A method of operating a membrane separation apparatus, wherein the concentration of raw water in a tank is increased using the raw water supply means after obtaining the membrane permeated water.
【請求項6】 原水が活性汚泥処理水であることを特徴
とする請求項5記載の膜分離装置の運転方法。
6. The method for operating a membrane separation device according to claim 5, wherein the raw water is treated activated sludge water.
【請求項7】 該原水より低濃度の液体の濃度が300
0mg/L以下であることを特徴とする請求項5記載の
膜分離装置の運転方法。
7. The concentration of a liquid having a concentration lower than that of the raw water is 300.
The method for operating a membrane separation device according to claim 5, wherein the amount is 0 mg / L or less.
【請求項8】 水供給手段のみを使用し、分離膜を水中
に浸漬し、膜透過水を取得した後に、該原水供給手段を
用いて槽内原水の濃度を上げることを特徴とする請求項
5記載の膜分離装置の運転方法。
8. The method according to claim 1, wherein the separation membrane is immersed in water using only the water supply means, and the concentration of the raw water in the tank is raised using the raw water supply means after obtaining the membrane permeated water. 6. The method for operating the membrane separation device according to 5.
【請求項9】 膜透過水を水位差あるいは透過側の減圧
により取得することを特徴とする請求項5記載の膜分離
方法。
9. The membrane separation method according to claim 5, wherein the water permeated through the membrane is obtained by a difference in water level or a reduced pressure on the permeation side.
【請求項10】 請求項1記載の膜分離装置を使用した
こと特徴とする活性汚泥処理装置。
10. An activated sludge treatment apparatus using the membrane separation apparatus according to claim 1.
【請求項11】 請求項1記載の膜分離装置を使用した
こと特徴とする水処理設備。
11. A water treatment facility using the membrane separation device according to claim 1.
JP06121897A 1997-03-14 1997-03-14 Membrane separation device and operation method thereof, activated sludge treatment device and water treatment facility Expired - Fee Related JP3726404B2 (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009285527A (en) * 2008-05-27 2009-12-10 Tsukishima Kikai Co Ltd Filter unit

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009285527A (en) * 2008-05-27 2009-12-10 Tsukishima Kikai Co Ltd Filter unit

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