JPH0999226A - Washing method of membrane - Google Patents
Washing method of membraneInfo
- Publication number
- JPH0999226A JPH0999226A JP25973195A JP25973195A JPH0999226A JP H0999226 A JPH0999226 A JP H0999226A JP 25973195 A JP25973195 A JP 25973195A JP 25973195 A JP25973195 A JP 25973195A JP H0999226 A JPH0999226 A JP H0999226A
- Authority
- JP
- Japan
- Prior art keywords
- membrane
- filtration tank
- cleaning
- filtration
- raw water
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】この発明は、濾過槽内に導入
した原水を膜モジュールに透過させ、固液分離を継続す
ることにより、付着物で閉塞された膜を効率よく洗浄す
る膜の洗浄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 cleaning a membrane, in which raw water introduced into a filtration tank is permeated through a membrane module and solid-liquid separation is continued to efficiently wash a membrane clogged with a deposit. It is about.
【0002】[0002]
【従来の技術】水処理設備においては、原水を濾過膜に
流して透過させ、固液分離を行っている。この膜濾過装
置は、濾過槽内に膜モジュールを浸漬してあり、濾過槽
内に導入した原水を膜モジュールの中空糸膜により濾過
する。透過水は、吸引ポンプにより送水され、浄水用の
処理水として供される。2. Description of the Related Art In a water treatment facility, raw water is passed through a filtration membrane and allowed to permeate to perform solid-liquid separation. In this membrane filtration device, a membrane module is immersed in a filtration tank, and raw water introduced into the filtration tank is filtered by a hollow fiber membrane of the membrane module. The permeated water is sent by a suction pump and provided as treated water for water purification.
【0003】上記の膜濾過装置において、膜濾過を継続
すると、濁質等の付着物により膜に目詰まりが生じ濾過
効率が低下するので、一定時間使用すると、透過水を膜
の透過水側から原水側に逆流させる逆洗浄といわれる方
法で膜を洗浄したり、濾過槽内の膜の下方に設けた空気
ノズルからの気泡により膜の表面を洗浄するようにして
いる。In the above membrane filtration device, when the membrane filtration is continued, the membrane is clogged due to the adhered substances such as turbidity and the filtration efficiency is lowered. The membrane is washed by a method called backwashing in which it flows back to the raw water side, or the surface of the membrane is washed by air bubbles from an air nozzle provided below the membrane in the filtration tank.
【0004】さらに、一定期間経過すると、濁質等の付
着物は膜層の内部にまで入り込み、上記の方法による洗
浄効果が著しく低下するので、このような事態に至った
ときは、従来、膜を装置から取り外して、洗浄用の薬液
(酸・アルカリ)が貯留された薬液洗浄槽内に浸漬させ
て膜の洗浄を行っている。また、膜を装置から取り外さ
ず、膜に洗浄用の薬液を供給して、この薬液により膜の
付着物を除去しようとする試みもなされている。Furthermore, after a certain period of time, the adhered substances such as turbidity penetrate into the inside of the membrane layer, and the cleaning effect by the above method is significantly reduced. Is removed from the apparatus, and the membrane is cleaned by immersing it in a chemical cleaning tank in which a cleaning chemical (acid / alkali) is stored. There has also been made an attempt to supply a cleaning chemical solution to the film without removing the film from the apparatus, and to remove the deposits on the film by the chemical solution.
【0005】[0005]
【発明が解決しようとする課題】しかしながら、上記の
従来の夫々の方法では、膜を閉塞する付着物の完全な除
去は難しい。中でも、付着物が有機物,金属等である場
合はともかく、これが微生物である場合には、その除去
作業がより困難となる。すなわち、特に浸漬型膜濾過装
置のように装置内の水の入れ替わりが比較的少ない系で
は、微生物が膜の表面に強固に付着しているので、膜の
フラックスが大きく低下し、従来の洗浄方法ではその除
去は到底不可能である。そして、従来の膜を濾過装置か
ら取り外して薬液洗浄槽内に浸漬させる方法では、クレ
ーン等、膜の移動および取り外し・取り付けのための設
備が必要となる。また、膜を装置から取り外さず膜に洗
浄用の薬液を供給させる方法では、薬液洗浄後の廃液処
理に手間がかかる欠点がある。However, it is difficult to completely remove the deposits clogging the membrane by the above-mentioned conventional methods. Above all, if the adhered matter is an organic matter, a metal, etc., and if it is a microorganism, the removal work becomes more difficult. That is, particularly in a system in which water is not exchanged in the apparatus such as an immersion type membrane filtration apparatus, since the microorganisms are strongly attached to the surface of the membrane, the flux of the membrane is greatly reduced, and the conventional cleaning method is used. Then its removal is impossible at all. The conventional method of removing the membrane from the filtration device and immersing the membrane in the chemical cleaning tank requires equipment such as a crane for moving and removing / attaching the membrane. Further, the method of supplying the cleaning chemical to the membrane without removing the membrane from the apparatus has a drawback that it takes a lot of time to process the waste liquid after cleaning the chemical.
【0006】この発明は、このような従来の薬液による
膜の洗浄方法に代え、濾過槽内を嫌気状態として膜から
付着物を剥離する方法を採用することにより、膜のフラ
ックスを回復する膜の洗浄方法を提供することを目的と
する。The present invention replaces such a conventional method of cleaning a membrane with a chemical solution and employs a method of removing the deposits from the membrane by keeping the inside of the filtration tank in an anaerobic state, thereby recovering the flux of the membrane. The purpose is to provide a cleaning method.
【0007】[0007]
【課題を解決するための手段】上記の目的を達成するた
めの具体的手段として、この発明は、濾過槽内に導入し
た原水を膜モジュールに透過させ、固液分離を継続する
ことにより、付着物で閉塞された膜を洗浄するに当り、
濾過槽内を所定時間嫌気状態に維持した後、散気等によ
り、膜から付着物を剥離させ分離除去することを特徴と
する膜の洗浄方法を構成した。As a concrete means for achieving the above-mentioned object, the present invention provides a method for permeating raw water introduced into a filtration tank through a membrane module to continue solid-liquid separation. When cleaning the membrane blocked with a kimono,
After maintaining the inside of the filtration tank in an anaerobic state for a predetermined time, the method for cleaning a membrane is characterized in that the adhering matter is separated from the membrane by air diffusion or the like to be separated and removed.
【0008】この場合、濾過槽内を嫌気状態とする方法
としては、濾過槽内に還元剤(特に亜硫酸ナトリウム、
亜硫酸水素ナトリウム)を投入する方法、あるいは、濾
過槽内の原水中の酸素を窒素ガスで置換する方法が有効
である。また、嫌気状態を維持した後膜から付着物を剥
離するには、濾過槽内に、ブロワから送られた空気を吹
き込む方法が有効である。さらに、膜モジュールは、浸
漬型濾過膜とするとよい。In this case, as a method of making the inside of the filtration tank anaerobic, a reducing agent (particularly sodium sulfite,
A method of introducing sodium hydrogen sulfite) or a method of replacing oxygen in the raw water in the filtration tank with nitrogen gas is effective. Further, in order to remove the deposits from the membrane after maintaining the anaerobic state, it is effective to blow the air sent from the blower into the filtration tank. Further, the membrane module may be a submerged filtration membrane.
【0009】[0009]
【発明の実施の形態】以下に、この発明の実施の形態を
図面に基づき説明する。図1の(a)は、この発明に係
る膜の洗浄方法を説明するための浸漬型膜濾過装置の一
例を示す断面図であり、同図の(b)は、膜モジュール
の斜視図である。BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described below with reference to the drawings. FIG. 1A is a sectional view showing an example of an immersion type membrane filtration device for explaining the membrane cleaning method according to the present invention, and FIG. 1B is a perspective view of a membrane module. .
【0010】図1の(a)および(b)を参照して、下
部を円錐状とした略円筒形の濾過槽1内には原水2が公
知の手段により導入される。原水2中には、浸漬型濾過
膜である膜モジュール3が横配置で上下に2基吊設され
ている。膜モジュール3は、中空糸膜3a(以下、膜3
aという。)を多数集積したもので、個々の膜3aは両
端部を夫々連結するとともに、両端部で内側内を連通し
てある。原水2は、吸引ポンプ10に吸引されて膜モジ
ュール3の膜3aの外側から膜3aの内側に透過し濾過
される。透過水11は、膜モジュール3の両側の配管1
8,19を繋いだ送水管13を経由して濾過槽1の外部
に取り出され、吸引ポンプ10により処理水槽17へ送
られ、浄水用の処理水12として供される。15は、送
水管13上における吸引ポンプ10の濾過槽1側に介装
された開閉弁であり、送水中は開状態となっている。With reference to FIGS. 1 (a) and 1 (b), raw water 2 is introduced into a generally cylindrical filtration tank 1 having a conical lower portion by a known means. In the raw water 2, two membrane modules 3, which are submerged filtration membranes, are suspended horizontally in a horizontal arrangement. The membrane module 3 includes a hollow fiber membrane 3a (hereinafter, membrane 3
called a. 2) are integrated, and each film 3a has both ends connected to each other and both ends communicate with each other inside. The raw water 2 is sucked by the suction pump 10, permeates from the outer side of the membrane 3a of the membrane module 3 to the inner side of the membrane 3a, and is filtered. The permeated water 11 is the piping 1 on both sides of the membrane module 3.
It is taken out of the filtration tank 1 through a water supply pipe 13 connecting 8 and 19, and is sent to a treated water tank 17 by a suction pump 10 and provided as treated water 12 for purification. Reference numeral 15 is an opening / closing valve provided on the water supply pipe 13 on the side of the filtration tank 1 of the suction pump 10 and is in an open state during water supply.
【0011】処理水槽10と送水管13との間には逆洗
浄用の配管20が接続され、逆洗ポンプ21と開閉弁1
6が介設される。膜モジュール3の膜3aに付着物が付
着し目詰まりが生じたときは、吸引ポンプ10を停止
し、開閉弁15を閉じ、開閉弁16を開状態として逆洗
ポンプ21を作動させて、膜3aの内側から圧縮された
空気および水を送り込み、逆洗浄を行う。なお、濾過槽
1の底部には、膜3aにより分離された付着物の集合体
である汚泥22が沈滞している。A pipe 20 for backwashing is connected between the treated water tank 10 and the water supply pipe 13, and a backwash pump 21 and an on-off valve 1 are provided.
6 are interposed. When deposits are attached to the membrane 3a of the membrane module 3 to cause clogging, the suction pump 10 is stopped, the opening / closing valve 15 is closed, the opening / closing valve 16 is opened, and the backwash pump 21 is operated to operate the membrane. Compressed air and water are sent from the inside of 3a to perform back washing. It should be noted that sludge 22 which is an aggregate of deposits separated by the membrane 3a is stagnant at the bottom of the filtration tank 1.
【0012】さて、膜濾過を継続しつつ、さらに、一定
期間経過することにより、膜3aに付着物、特に微生物
が堆積して膜3aが閉塞されると、原水2の供給を停止
し、また、吸引ポンプ10および逆洗ポンプ21を作動
停止した後、開閉弁15,16を閉じ、膜の洗浄が行わ
れる。その第1の手段としては、濾過槽1内に貯留され
た原水2中に還元剤5を投入し、濾過槽1内を嫌気状態
とする方法が挙げられる。還元剤には、例えば水溶性の
亜硫酸ナトリウムや亜硫酸水素ナトリウムその他の毒性
のない公知の化合物が選定される。第2の手段として
は、窒素ガスの散気で、濾過槽1内を嫌気状態とする方
法が挙げられる。すなわち、濾過槽1内に貯留された原
水2中に多孔管6を配置し、窒素ガスを貯蔵したボンベ
7から原水2中に窒素ガスを送り込み、原水2中の酸素
を窒素ガスで置換するものである。この嫌気状態を所定
時間、具体的には約1日以上維持することにより、付着
微生物は変質して膜表面から剥離され、分離除去され
る。なお、嫌気状態でさらに酸化還元電位を低下させる
と、金属類の多くが還元状態で溶解性となることより、
金属等の詰まりに関しても有効に除去できる。また、濾
過槽1内を所定時間嫌気状態に維持した後、膜を振動さ
せて膜から付着物を剥離させてもよい。さらに、振動に
代えて逆洗浄を行ってもよい。次いで、濾過槽1内に
は、ブロワ9から空気が送られ、これを原水2中に配置
した多孔管8で細かい気泡にして均一に原水2中に吹き
込む散気装置により、付着微生物を膜から剥離させた
後、運転が再開される。この場合、散気装置からの空気
は、膜の表面に当るようにするとよい。濾過槽1内の水
は、必要に応じてドレンする。When the membrane 3a is clogged by deposits, particularly microorganisms, on the membrane 3a during a certain period of time while continuing the membrane filtration, the supply of the raw water 2 is stopped, and After stopping the suction pump 10 and the backwash pump 21, the on-off valves 15 and 16 are closed to wash the membrane. As the first means, there is a method of introducing the reducing agent 5 into the raw water 2 stored in the filtration tank 1 to make the inside of the filtration tank 1 anaerobic. As the reducing agent, for example, water-soluble sodium sulfite, sodium bisulfite, and other known nontoxic compounds are selected. As a second means, there is a method of making the inside of the filtration tank 1 anaerobic by diffusing nitrogen gas. That is, the perforated pipe 6 is arranged in the raw water 2 stored in the filtration tank 1, the nitrogen gas is fed into the raw water 2 from the cylinder 7 storing the nitrogen gas, and the oxygen in the raw water 2 is replaced with the nitrogen gas. Is. By maintaining this anaerobic state for a predetermined time, specifically about 1 day or more, the adherent microorganisms are denatured and peeled off from the membrane surface to be separated and removed. If the redox potential is further lowered in the anaerobic state, many of the metals become soluble in the reduced state,
It is also possible to effectively remove clogging of metal and the like. Further, after the inside of the filtration tank 1 is maintained in an anaerobic state for a predetermined time, the membrane may be vibrated to remove the deposits from the membrane. Further, back washing may be performed instead of vibration. Next, air is sent from the blower 9 into the filtration tank 1, and the adhered microorganisms are removed from the membrane by an air diffuser that blows the air into the raw water 2 evenly by forming fine bubbles in the porous tube 8 arranged in the raw water 2. After the peeling, the operation is restarted. In this case, the air from the air diffuser may hit the surface of the membrane. The water in the filtration tank 1 is drained if necessary.
【0013】なお、上記の実施形態においては、原水中
に膜モジュールを2基吊設した例について説明したが、
規模に応じて増減される。また、膜モジュールは中空糸
膜に代えて平膜やスパイラル膜あるいは管状膜等を使用
してもよい。In the above embodiment, an example in which two membrane modules are suspended in raw water has been described.
Increases or decreases depending on the scale. Further, the membrane module may use a flat membrane, a spiral membrane, a tubular membrane or the like instead of the hollow fiber membrane.
【0014】[0014]
【発明の効果】以上説明したように、この発明に係る膜
の洗浄方法によれば、濾過槽内を嫌気化して膜から付着
物を剥離する方法を採用したので、膜の表面に強固に付
着し膜を閉塞している付着物、特に微生物が、濾過槽内
の嫌気状態を維持している間に変質して剥離し、膜のフ
ラックスを大きく回復し得た。したがって、従来の洗浄
方法では困難であった付着物の完全除去が可能である。
そして、従来の膜を濾過装置から取り外して薬液洗浄槽
内に浸漬させる方法が必要とした、クレーン等、膜の移
動および取り外し・取り付けのための設備が不要とな
る。また、従来の膜を装置から取り外さず膜に洗浄用の
薬液を供給させる方法が必要とした薬液洗浄後の廃液処
理は、窒素ガスの散気による場合は不要であり、還元剤
を投入する場合も少量の廃液で済む効果がある。As described above, according to the membrane cleaning method of the present invention, the method of anaerobicizing the inside of the filtration tank to remove the deposits from the membrane is used, so that the membrane firmly adheres to the surface of the membrane. The deposits clogging the membrane, especially the microorganisms, were deteriorated and peeled off while maintaining the anaerobic state in the filtration tank, and the flux of the membrane could be largely recovered. Therefore, it is possible to completely remove the deposit, which was difficult with the conventional cleaning method.
Then, the equipment for moving and removing / attaching the membrane, such as a crane, which is required in the conventional method of removing the membrane from the filtration device and immersing it in the chemical cleaning tank is not required. Also, the waste liquid treatment after chemical cleaning, which requires the conventional method of supplying a cleaning chemical to the film without removing it from the device, is not necessary when nitrogen gas is diffused, and when a reducing agent is added. Also has the effect of requiring a small amount of waste liquid.
【図1】(a)は、この発明に係る膜の洗浄方法を説明
するための浸漬型膜濾過装置の一例を示す断面図であ
り、(b)は、膜モジュールの斜視図である。FIG. 1 (a) is a cross-sectional view showing an example of a submerged membrane filtration device for explaining a membrane cleaning method according to the present invention, and FIG. 1 (b) is a perspective view of a membrane module.
1 …濾過槽 2 …原水 3 …膜モジュール 3a…中空糸膜 5 …還元剤 6 …多孔管 7 …ボンベ 8 …多孔管 9 …ブロワ 10 …吸引ポンプ 11 …透過水 12 …処理水 13 …送水管 15 …開閉弁 16 …開閉弁 17 …処理水槽 18 …配管 19 …配管 20 …配管 21 …逆洗ポンプ 22 …汚泥 1 ... Filtration tank 2 ... Raw water 3 ... Membrane module 3a ... Hollow fiber membrane 5 ... Reducing agent 6 ... Porous tube 7 ... Cylinder 8 ... Porous tube 9 ... Blower 10 ... Suction pump 11 ... Permeate 12 ... Treated water 13 ... Water pipe 15 ... Open / close valve 16 ... Open / close valve 17 ... Treatment water tank 18 ... Piping 19 ... Piping 20 ... Piping 21 ... Backwash pump 22 ... Sludge
───────────────────────────────────────────────────── フロントページの続き (72)発明者 小澤 源三 北海道札幌市北区北33条西12丁目3−23 (72)発明者 鈴木 辰彦 東京都中央区京橋1丁目3番3号前澤工業 株式会社内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Genzo Ozawa, 12-3-23 Kita 33, Kita-ku, Sapporo-shi, Hokkaido (72) Inventor Tatsuhiko Suzuki 1-3-3 Kyobashi, Chuo-ku, Tokyo Maesawa Industry Co., Ltd. In the company
Claims (6)
に透過させ、固液分離を継続することにより、付着物で
閉塞された膜を洗浄するに当り、濾過槽内を所定時間嫌
気状態に維持した後、膜から付着物を剥離させ分離除去
することを特徴とする膜の洗浄方法。1. When the raw water introduced into the filtration tank is permeated through the membrane module and solid-liquid separation is continued to wash the membrane clogged with the deposits, the filtration tank is anaerobic for a predetermined time. A method for cleaning a film, characterized in that after maintaining, the deposit is separated from the film to be separated and removed.
槽内を嫌気状態とする請求項1に記載の膜の洗浄方法。2. The method for cleaning a membrane according to claim 1, wherein a reducing agent is introduced into the filtration tank to make the inside of the filtration tank anaerobic.
ナトリウムである請求項2に記載の膜の洗浄方法。3. The method for cleaning a membrane according to claim 2, wherein the reducing agent is sodium sulfite or sodium hydrogen sulfite.
換して、当該濾過槽内を嫌気状態とする請求項1に記載
の膜の洗浄方法。4. The method for cleaning a membrane according to claim 1, wherein oxygen in the raw water in the filtration tank is replaced with nitrogen gas to make the inside of the filtration tank anaerobic.
き込んで膜から付着物を剥離させる請求項1に記載の膜
の洗浄方法。5. The method for cleaning a membrane according to claim 1, wherein air sent from a blower is blown into the filtration tank to remove the deposits from the membrane.
求項1ないし請求項5のいずれかに記載の膜の洗浄方
法。6. The method for cleaning a membrane according to claim 1, wherein the membrane module is an immersion type filtration membrane.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP25973195A JP3430385B2 (en) | 1995-10-06 | 1995-10-06 | Cleaning method of membrane |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP25973195A JP3430385B2 (en) | 1995-10-06 | 1995-10-06 | Cleaning method of membrane |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH0999226A true JPH0999226A (en) | 1997-04-15 |
JP3430385B2 JP3430385B2 (en) | 2003-07-28 |
Family
ID=17338167
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP25973195A Expired - Fee Related JP3430385B2 (en) | 1995-10-06 | 1995-10-06 | Cleaning method of membrane |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP3430385B2 (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2005074357A (en) * | 2003-09-02 | 2005-03-24 | Ngk Insulators Ltd | Membrane washing method in membrane separation activated sludge method |
JP2010188244A (en) * | 2009-02-17 | 2010-09-02 | Act:Kk | Sewage treatment apparatus and sewage treatment method |
KR101288003B1 (en) * | 2011-03-03 | 2013-07-19 | (주)씨엔원(CN 1 Co., Ltd) | Apparatus of waste water treatment using membrane module |
US8852438B2 (en) | 1995-08-11 | 2014-10-07 | Zenon Technology Partnership | Membrane filtration module with adjustable header spacing |
-
1995
- 1995-10-06 JP JP25973195A patent/JP3430385B2/en not_active Expired - Fee Related
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US8852438B2 (en) | 1995-08-11 | 2014-10-07 | Zenon Technology Partnership | Membrane filtration module with adjustable header spacing |
JP2005074357A (en) * | 2003-09-02 | 2005-03-24 | Ngk Insulators Ltd | Membrane washing method in membrane separation activated sludge method |
JP2010188244A (en) * | 2009-02-17 | 2010-09-02 | Act:Kk | Sewage treatment apparatus and sewage treatment method |
KR101288003B1 (en) * | 2011-03-03 | 2013-07-19 | (주)씨엔원(CN 1 Co., Ltd) | Apparatus of waste water treatment using membrane module |
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