[go: up one dir, main page]

JP2013163141A - Membrane filtration system - Google Patents

Membrane filtration system Download PDF

Info

Publication number
JP2013163141A
JP2013163141A JP2012026312A JP2012026312A JP2013163141A JP 2013163141 A JP2013163141 A JP 2013163141A JP 2012026312 A JP2012026312 A JP 2012026312A JP 2012026312 A JP2012026312 A JP 2012026312A JP 2013163141 A JP2013163141 A JP 2013163141A
Authority
JP
Japan
Prior art keywords
membrane
water
pretreatment
treated
filtration system
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
JP2012026312A
Other languages
Japanese (ja)
Inventor
Ryoichi Arimura
良一 有村
Takeshi Matsushiro
武士 松代
Hidetake Shiire
英武 仕入
Miwa Ishizuka
美和 石塚
Futoshi Kurokawa
太 黒川
Shioko Kurihara
潮子 栗原
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.)
Toshiba Corp
Original Assignee
Toshiba 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 Toshiba Corp filed Critical Toshiba Corp
Priority to JP2012026312A priority Critical patent/JP2013163141A/en
Publication of JP2013163141A publication Critical patent/JP2013163141A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

PROBLEM TO BE SOLVED: To improve cleaning efficiency of a pretreatment membrane used with a reverse osmosis membrane.SOLUTION: A membrane filtration system includes: a pretreatment membrane; a high-pressure pump; a reverse osmosis membrane; and a fine bubble generator. The pretreatment membrane removes an insoluble component contained in water to be treated. The high-pressure pump applies pressure to the water to be treated from which the insoluble component is removed by the pretreatment membrane. The reverse osmosis membrane separates the water to be treated to which the pressure is applied into treatment water from which a soluble component containing the water to be treated is removed and concentrated water in which the soluble component is concentrated. The fine bubble generator generates fine bubbles by introducing the concentrated water discharged from the reverse osmosis membrane at high pressure and supplies the pretreatment membrane during cleaning with the concentrated water containing the fine bubbles.

Description

本発明は、前処理膜で前処理された被処理水を逆浸透膜で処理する膜ろ過システムに関する。   The present invention relates to a membrane filtration system for treating water to be treated pretreated with a pretreatment membrane with a reverse osmosis membrane.

イオンや塩類を含む海水、汽水または地下水等から生活用水、工業用水または農業用水等を製造する膜ろ過システムでは、逆浸透(reverse osmosis : RO)膜を利用する方法が用いられることがある。RO膜は、水を透過させるが、イオンや塩類など水以外の不純物は透過させない性質を持つ。このRO膜では、被処理水に溶質の濃度に応じた浸透圧以上の圧力をかけることで、水と溶質とを分離することができる。   In a membrane filtration system that produces domestic water, industrial water, agricultural water, or the like from seawater, brackish water, or groundwater containing ions and salts, a method that uses a reverse osmosis (RO) membrane may be used. The RO membrane has the property of allowing water to pass through but not allowing impurities other than water such as ions and salts to pass through. In this RO membrane, water and solute can be separated by applying a pressure equal to or higher than the osmotic pressure corresponding to the solute concentration to the water to be treated.

RO膜を用いる膜ろ過システムでは、被処理水に含まれる不溶解性成分を除去するための前処理を施すことが一般的である。例えば、海水を淡水化する場合、海水中に含まれる濁質、藻類、微生物等を前処理で除去することで、RO膜への汚濁負荷を低減し、RO膜の薬品洗浄の回数を減少させ、長期間にわたる安定した運転を可能とする。   In a membrane filtration system using an RO membrane, it is common to perform pretreatment for removing insoluble components contained in water to be treated. For example, when seawater is desalinated, the turbidity, algae, microorganisms, etc. contained in the seawater are removed by pretreatment, thereby reducing the pollution load on the RO membrane and reducing the number of times the RO membrane is chemically washed. , Enabling stable operation over a long period of time.

前処理には、不溶解性成分を除去可能な膜を利用することが一般的であるが、前処理で利用する前処理膜に多くの不溶解性成分が溜まると、この前処理膜を洗浄する必要が生じる。   For pretreatment, it is common to use a film that can remove insoluble components. However, if many insoluble components accumulate in the pretreatment film used in the pretreatment, the pretreatment film is washed. Need to do.

特開2007−289940号公報JP 2007-289940 A 特開2009−240903号公報JP 2009-240903 A 特開2007−289899号公報JP 2007-289899 A 特開2008−289959号公報JP 2008-289959 A 特開2011−16044号公報JP 2011-16044 A 特開2011−62632号公報JP 2011-62632 A 特開2011−72939号公報JP 2011-72939 A

しかしながら、前処理で溜まる不溶解性成分は除去が困難であり、不溶解性成分の除去に必要なエネルギーが大きくなる問題があった。   However, it is difficult to remove the insoluble component accumulated in the pretreatment, and there is a problem that the energy required for removing the insoluble component is increased.

したがって、本発明は、逆浸透膜とともに使用する前処理膜の洗浄効率を向上することができる膜ろ過システムを提供する。   Therefore, this invention provides the membrane filtration system which can improve the washing | cleaning efficiency of the pre-processing membrane used with a reverse osmosis membrane.

実施形態に係る膜ろ過システムは、前処理膜と、高圧ポンプと、逆浸透膜と、微細気泡発生装置とを備える。前処理膜は、被処理水に含まれる不溶解性成分を除去する。高圧ポンプは、前処理膜で不溶解性成分が除去された被処理水に圧力を与える。逆浸透膜は、高圧ポンプで圧力が与えられた被処理水を、被処理水に含まれる溶解性成分を除去した処理水と、溶解性成分が濃縮された濃縮水とに分離する。微細気泡発生装置は、逆浸透膜から高圧で排出される濃縮水を導入して微細気泡を発生し、洗浄中の前処理膜に微細気泡を含む濃縮水を供給する。   The membrane filtration system according to the embodiment includes a pretreatment membrane, a high-pressure pump, a reverse osmosis membrane, and a fine bubble generator. The pretreatment membrane removes insoluble components contained in the water to be treated. The high-pressure pump applies pressure to the water to be treated from which insoluble components have been removed by the pretreatment membrane. The reverse osmosis membrane separates water to be treated, which has been given pressure by a high-pressure pump, into treated water from which soluble components contained in the water to be treated have been removed and concentrated water in which soluble components have been concentrated. The fine bubble generating device introduces concentrated water discharged from the reverse osmosis membrane at a high pressure to generate fine bubbles, and supplies the concentrated water containing fine bubbles to the pretreatment membrane being cleaned.

本発明の第1実施形態に係る膜ろ過システムの構成を説明する概略図である。It is the schematic explaining the structure of the membrane filtration system which concerns on 1st Embodiment of this invention. 本発明の第2実施形態に係る膜ろ過システムの構成を説明する概略図である。It is the schematic explaining the structure of the membrane filtration system which concerns on 2nd Embodiment of this invention.

以下に、図面を用いて本発明の各実施形態について説明する。以下の説明について、同様の構成については同一の符号を用いて説明を省略する。本発明の実施形態に係る膜ろ過システムは、RO膜(逆浸透膜)を利用して塩類やイオンを含む海水、汽水、地下水等から塩類やイオンを除いて淡水化するとともに、RO膜の前段の前処理膜を洗浄する機能を有する水処理システムである。以下では、海水を取水して、淡水化する一例で説明する。   Embodiments of the present invention will be described below with reference to the drawings. In the following description, the same components are denoted by the same reference numerals and the description thereof is omitted. A membrane filtration system according to an embodiment of the present invention uses a RO membrane (reverse osmosis membrane) to desalinate salts and ions from seawater, brackish water, groundwater, and the like containing salts and ions, and at the front stage of the RO membrane This is a water treatment system having a function of cleaning the pretreatment film. Hereinafter, an example in which seawater is taken and desalinated will be described.

[第1実施形態]
図1に示すように、第1実施形態の膜ろ過システム1aは、取水源から取水した被処理水を貯留する取水槽11、取水槽11から導入された被処理水を前処理する前処理膜12、前処理された被処理水を導入してろ過する膜ろ過水槽13、膜ろ過水槽13から処理水を導入して淡水化するRO膜14、RO膜14から淡水を導入する処理水槽15を備えている。また、膜ろ過システム1aは、濃縮水の一部を利用して微細気泡を発生する微細気泡発生装置16を備えている。さらに、膜ろ過システム1aは、前処理膜12に超音波を与える超音波発生装置17を備えていてもよい。
[First Embodiment]
As shown in FIG. 1, the membrane filtration system 1a of 1st Embodiment is the pre-treatment membrane which pre-processes the to-be-processed water introduced from the intake tank 11 which stores the to-be-processed water taken from the intake source, and the intake tank 11 12. A membrane filtration water tank 13 for introducing and filtering pretreated water to be treated, an RO membrane 14 for introducing treated water from the membrane filtration water tank 13 for desalination, and a treated water tank 15 for introducing fresh water from the RO membrane 14 I have. Further, the membrane filtration system 1a includes a fine bubble generating device 16 that generates fine bubbles using a part of the concentrated water. Furthermore, the membrane filtration system 1a may include an ultrasonic generator 17 that applies ultrasonic waves to the pretreatment membrane 12.

取水槽11は、ラインL1及び取水ポンプP1を介して取水源である海から取水した海水を貯留する。   The intake tank 11 stores seawater taken from the sea that is the intake source via the line L1 and the intake pump P1.

前処理膜12は、例えば、精密ろ過膜(MF膜)や限外ろ過膜(UF膜)等であり、ラインL2及び膜ろ過ポンプP2を介して、取水槽11で貯留される被処理水(海水)を導入し、被処理水に含まれる不溶解性成分を被処理水から除去する。ろ過により前処理膜12の膜表面に残った不溶解性成分は、逆洗のタイミングで前処理膜12から除去される。すなわち、前処理膜12の膜表面には、海水中の濁質、微生物、微生物が放出する粘性の高い有機物、溶存有機物または無機イオン等の不溶解性成分が蓄積する。このような不溶解性成分が多く蓄積すると前処理膜12が目詰まりし、差圧が大きくなっていく。したがって、前処理膜12では、目詰まりを解消するため、定期的等のタイミングで、膜の逆側(二次側)から洗浄水を送水して膜面に付着した汚れを除去(逆洗)する必要がある。   The pretreatment membrane 12 is, for example, a microfiltration membrane (MF membrane), an ultrafiltration membrane (UF membrane) or the like, and water to be treated (stored in the intake tank 11 via the line L2 and the membrane filtration pump P2). Seawater) is introduced, and insoluble components contained in the water to be treated are removed from the water to be treated. The insoluble component remaining on the membrane surface of the pretreatment membrane 12 by filtration is removed from the pretreatment membrane 12 at the timing of backwashing. That is, insoluble components such as turbidity in seawater, microorganisms, organic matter with high viscosity released by microorganisms, dissolved organic matter, or inorganic ions accumulate on the membrane surface of the pretreatment membrane 12. When a large amount of such insoluble components accumulates, the pretreatment film 12 is clogged and the differential pressure increases. Therefore, in order to eliminate clogging in the pretreatment film 12, cleaning water is fed from the reverse side (secondary side) of the film at regular intervals to remove dirt adhering to the film surface (back washing). There is a need to.

膜ろ過水槽13は、ラインL3を介して、前処理膜12で処理された被処理水が導入される。膜ろ過水槽13の被処理水の一部は、逆洗のタイミングで膜ろ過水槽13から、ラインL8及び逆洗ポンプP5を介して、前処理膜12に通水される。   In the membrane filtration water tank 13, the water to be treated treated with the pretreatment membrane 12 is introduced through the line L3. A part of the water to be treated in the membrane filtration water tank 13 is passed from the membrane filtration water tank 13 to the pretreatment membrane 12 via the line L8 and the backwash pump P5 at the timing of backwashing.

RO膜14は、ラインL4、送水ポンプP3及び高圧ポンプP4を介して、膜ろ過水槽13で処理された被処理水を導入し、被処理水に含まれる塩類やイオンを除去したろ過水と、塩類やイオンを含む濃縮水とに分離する。RO膜14で処理するためには、溶質の浸透圧以上の圧力をかける必要がある。したがって、膜ろ過システム1aでは、送水ポンプP3で被処理水を送水するだけでなく、高圧ポンプP4で被処理水を塩類やイオンの浸透圧以上の圧力(例えば、約5〜6MPa程度)にした後にRO膜14に送ることが必要になる。   RO membrane 14 introduces the treated water treated in membrane filtration water tank 13 through line L4, water pump P3 and high-pressure pump P4, and filtered water from which salts and ions contained in the treated water are removed, Separated into concentrated water containing salts and ions. In order to process with the RO membrane 14, it is necessary to apply a pressure higher than the osmotic pressure of the solute. Therefore, in the membrane filtration system 1a, not only the water to be treated is fed by the water pump P3, but the water to be treated is set to a pressure (for example, about 5 to 6 MPa) higher than the osmotic pressure of salts and ions by the high pressure pump P4. It will be necessary to send it to the RO membrane 14 later.

RO膜14で得られた淡水は、淡水ラインL5を介して処理水槽15へ送られ、生活用水、工業用水または農業用水等として利用される。RO膜14で淡水と分離された濃縮水は、濃縮水ラインL6及び減圧弁Bを介し、例えば、取水源である海へ排出される。RO膜14では高圧で被処理水を処理することから、RO膜14から排出される濃縮水が高圧である為、減圧弁Bで減圧した後に排出している。また、RO膜14から排出された濃縮水の一部は、濃縮水ラインL6から分岐したラインL7を介して、微細気泡発生装置16に供給される。   The fresh water obtained by the RO membrane 14 is sent to the treated water tank 15 through the fresh water line L5 and used as domestic water, industrial water, agricultural water, or the like. The concentrated water separated from the fresh water by the RO membrane 14 is discharged, for example, to the sea as a water intake source through the concentrated water line L6 and the pressure reducing valve B. Since the RO membrane 14 treats the water to be treated at a high pressure, the concentrated water discharged from the RO membrane 14 is at a high pressure. A part of the concentrated water discharged from the RO membrane 14 is supplied to the fine bubble generating device 16 via a line L7 branched from the concentrated water line L6.

微細気泡発生装置16は、濃縮水ラインL6から分岐するラインL7を介してRO膜14から排出される濃縮水の一部を導入すると、前処理膜12の逆洗に利用する微細気泡を生成する。例えば、微細気泡発生装置16は、周囲の空気を取り込み、衝撃波方式や旋回方式等を利用して、マイクロバブルやナノバブル等の微細気泡を発生する。濃縮水はRO膜14から高圧で排出されるため、RO膜14から排出される濃縮水が有する圧力を利用することで、微細気泡発生装置16で必要な動力を低くすることができる。   When a part of concentrated water discharged from the RO membrane 14 is introduced through the line L7 branched from the concentrated water line L6, the fine bubble generating device 16 generates fine bubbles used for backwashing the pretreatment membrane 12. . For example, the fine bubble generating device 16 takes in ambient air and generates fine bubbles such as microbubbles and nanobubbles using a shock wave method, a swirl method, or the like. Since the concentrated water is discharged from the RO membrane 14 at a high pressure, the power necessary for the microbubble generator 16 can be reduced by using the pressure of the concentrated water discharged from the RO membrane 14.

超音波発生装置17は、前処理膜12に接続され、前処理膜12の逆洗の際に超音波を発生する。   The ultrasonic generator 17 is connected to the pretreatment film 12 and generates ultrasonic waves when the pretreatment film 12 is backwashed.

〈前処理膜の洗浄〉
膜ろ過システム1aでは、前処理膜12を逆洗する際には、前処理膜12の二次側から逆洗水を供給する。具体的には、膜ろ過システム1aでは、ラインL8及び逆洗ポンプP5を介して、膜ろ過水槽13の膜ろ過水を逆洗水として供給する。これにより、前処理膜12では、膜表面の付着物質が剥離される。
<Cleaning of pretreatment film>
In the membrane filtration system 1a, backwash water is supplied from the secondary side of the pretreatment membrane 12 when the pretreatment membrane 12 is backwashed. Specifically, in the membrane filtration system 1a, the membrane filtrate in the membrane filtration water tank 13 is supplied as backwash water via the line L8 and the backwash pump P5. Thereby, in the pretreatment film | membrane 12, the adhering substance on the film | membrane surface is peeled.

また、膜ろ過システム1aでは、膜ろ過水槽13の膜ろ過水に加え、ラインL9を介して微細気泡発生装置16で発生された微細気泡を含有する微細気泡含有水を前処理膜12に供給する。これにより、前処理膜12では、微細気泡を利用して膜面を洗浄することができるため、膜ろ過水のみを利用する逆洗と比較して、洗浄効率を向上することができる。   Moreover, in the membrane filtration system 1a, in addition to the membrane filtrate in the membrane filtration water tank 13, fine bubble-containing water containing fine bubbles generated by the fine bubble generator 16 is supplied to the pretreatment membrane 12 via the line L9. . Thereby, in the pretreatment film | membrane 12, since a film | membrane surface can be wash | cleaned using a microbubble, compared with backwashing using only membrane filtration water, cleaning efficiency can be improved.

ここで、微細気泡は、例えば、(1)〜(3)の特性を有する。   Here, the fine bubbles have, for example, the characteristics (1) to (3).

(1)気泡径が小さく、単位体積あたりの表面積が大きい。   (1) The bubble diameter is small and the surface area per unit volume is large.

(2)自己加圧効果がある。すなわち、気泡が縮小して消滅する効果である。一般に、50μm以下の気泡は、自身の縮小作用により小さくなり消滅する。このとき、消える瞬間の泡の内部は、高温高圧になる。   (2) There is a self-pressurizing effect. That is, it is an effect that bubbles are reduced and disappear. In general, bubbles of 50 μm or less become smaller and disappear due to their shrinking action. At this time, the inside of the bubble disappears at a high temperature and high pressure.

(3)マイナスに帯電している。したがって、気泡同士が合体しにくい。   (3) It is negatively charged. Therefore, it is difficult for the bubbles to coalesce.

また、微細気泡は、(1)〜(3)の特性により、気体溶解効率上昇、付着性、比重低減、持続性、拡散性または圧壊(キャビテーションの一種)等の現象を生じる。これらの現象の中でも、圧壊という現象により病原性の微生物やウィルスなどの低減効果が確認されており、圧壊により、逆洗の効率を向上させることができる。   In addition, fine bubbles cause phenomena such as an increase in gas dissolution efficiency, adhesion, reduced specific gravity, sustainability, diffusivity, or collapse (a type of cavitation) due to the characteristics (1) to (3). Among these phenomena, the reduction effect of pathogenic microorganisms and viruses has been confirmed by the phenomenon of crushing, and the efficiency of backwashing can be improved by the crushing.

微細気泡の発生には大きな動力を必要とするが、膜ろ過システム1aでは、RO膜14を透過させるために被処理水を高圧にしている。したがって、膜ろ過システム1aは、このRO膜14でろ過するために高圧で排出された濃縮水を有効利用して微細気泡を生成する。   Although generation of fine bubbles requires a large amount of power, in the membrane filtration system 1a, the water to be treated is at a high pressure in order to allow the RO membrane 14 to permeate. Therefore, the membrane filtration system 1a generates fine bubbles by effectively using the concentrated water discharged at a high pressure for filtration through the RO membrane 14.

微細気泡発生装置16は、ラインL7の高圧の濃縮水を、微細気泡を発生するのに適した圧力、例えば1MPa程度に減圧する機能を有する。微細気泡発生装置16は、濃縮水への空気の混入を中断して微細気泡の発生を停止することで、微細気泡を含まない濃縮水のみを前処理膜12に供給することもできる。また、微細気泡発生装置16は、空気の混入を調整して、生成する微細気泡のサイズをコントロールすることもできる。このように、膜ろ過システム1aでは、微細気泡発生装置16において空気の混入を中断したり調整したりすることで、更に高い洗浄効果を得ることもできる。   The fine bubble generator 16 has a function of reducing the high-pressure concentrated water in the line L7 to a pressure suitable for generating fine bubbles, for example, about 1 MPa. The fine bubble generating device 16 can supply only the concentrated water not containing fine bubbles to the pretreatment membrane 12 by stopping the generation of fine bubbles by interrupting the mixing of air into the concentrated water. Moreover, the fine bubble generator 16 can also control the size of the fine bubbles to be generated by adjusting the mixing of air. As described above, in the membrane filtration system 1a, it is possible to obtain a higher cleaning effect by interrupting or adjusting the mixing of air in the fine bubble generating device 16.

例えば、微細気泡発生装置16において濃縮水へ混入させる空気量を調整して微細気泡の気泡径を変化し、大きさの異なる微細気泡生成する。膜ろ過システム1aでは、異なる大きさの微細気泡を利用して前処理膜12を洗浄することで、逆洗の効果を向上させることができる。具体的には、洗浄の初期段階では空気の混入量を少なくして、気泡径の小さい微細気泡を生成し、膜の内部にまで気泡を入り込ませる。また、洗浄が進むにつれて、空気の混入量を多くし、初期段階より大きな微細気泡で濁質等の剥離を促進させることが考えられる。   For example, the amount of air mixed into the concentrated water in the fine bubble generator 16 is adjusted to change the bubble diameter of the fine bubbles to generate fine bubbles having different sizes. In the membrane filtration system 1a, the effect of backwashing can be improved by washing the pretreatment membrane 12 using fine bubbles of different sizes. Specifically, in the initial stage of cleaning, the amount of air mixed in is reduced to generate fine bubbles having a small bubble diameter, and the bubbles enter the inside of the film. In addition, as cleaning progresses, it is conceivable to increase the amount of air mixed in and promote separation of turbidity and the like with fine bubbles larger than the initial stage.

膜ろ過システム1aでは、前処理膜12の二次側のみから微細気泡含有水を供給してもよいし、前処理膜12の一次側のみから微細気泡含有水を供給してもよいし、一次側及び二次側の両方から微細気泡含有水を供給してもよい。例えば、二次側だけでなく、一次側、又は、一次側と二次側の両方から微細気泡含有水を供給することによって、膜の表面、膜の内部に付着した汚れを効果的に除去することができる。   In the membrane filtration system 1a, the fine bubble-containing water may be supplied only from the secondary side of the pretreatment membrane 12, the fine bubble-containing water may be supplied only from the primary side of the pretreatment membrane 12, or the primary You may supply fine bubble containing water from both a side and a secondary side. For example, by supplying fine bubble-containing water not only from the secondary side, but also from the primary side or from both the primary side and the secondary side, the surface of the membrane and dirt attached to the inside of the membrane are effectively removed. be able to.

前処理膜12を洗浄後、濁質等を含む洗浄排水は前処理膜12から排出され、処理される。   After washing the pretreatment film 12, washing wastewater containing turbidity is discharged from the pretreatment film 12 and processed.

膜ろ過システム1aは、前処理膜12の洗浄時に超音波発生装置17で、超音波を発生し、膜ろ過水や微細気泡含有水に超音波を与えてもよい。超音波を与えることで、膜を膜ろ過水や微細気泡のみで洗浄する場合と比較して、洗浄効果を向上させることができる。   The membrane filtration system 1a may generate ultrasonic waves with the ultrasonic generator 17 when cleaning the pretreatment membrane 12, and may apply ultrasonic waves to the membrane filtered water or the water containing fine bubbles. By applying ultrasonic waves, the cleaning effect can be improved as compared with the case where the membrane is cleaned only with membrane filtered water or fine bubbles.

超音波洗浄は、付着物質等の除去に効果が高いことが知られている。また、超音波によって微細気泡の圧壊(崩壊)を促進させることができるため、膜ろ過システム1aでは、微細気泡周囲で酸化力の高いOHラジカルを発生させ、OHラジカルが膜表面に付着している濁質等と反応することで、膜表面の洗浄効果を高めることができる。この微細気泡の圧壊現象を利用するためには、膜の表面だけでなく、膜の内部に微細気泡を浸透させていくことが、より高い洗浄効果を得ることができる。したがって、膜ろ過システム1aでは、微細気泡発生装置16で気泡径の小さい微細気泡を生成し、膜の内部にまで微細気泡を入り込ませたうえで超音波を与えることで、より高い洗浄効果を得ることができる。   It is known that ultrasonic cleaning is highly effective in removing adhered substances and the like. Moreover, since crushing (disintegration) of fine bubbles can be promoted by ultrasonic waves, in the membrane filtration system 1a, OH radicals having high oxidizing power are generated around the fine bubbles, and the OH radicals adhere to the film surface. By reacting with turbidity or the like, the cleaning effect on the film surface can be enhanced. In order to utilize this crushing phenomenon of the fine bubbles, it is possible to obtain a higher cleaning effect by allowing the fine bubbles to penetrate not only the surface of the membrane but also the inside of the membrane. Therefore, in the membrane filtration system 1a, the fine bubble generator 16 generates fine bubbles having a small bubble diameter, and the ultrasonic waves are applied to the inside of the membrane to obtain a higher cleaning effect. be able to.

上述したように、第1実施形態に係る膜ろ過システム1aは、前処理膜12の洗浄に、RO膜14で使用した圧力を使って発生させた微細気泡を利用している。これにより、微細気泡発生のために新たな動力源を使用することなく、前処理膜12の洗浄効率を向上させることができる。またこの際、前処理膜12のサイズ等に合わせて、微細気泡発生装置16で発生する微細気泡のサイズを調整したり、微細気泡発生装置16が異なるサイズの微細気泡を発生してこれらの異なるサイズの微細気泡を供給するタイミングを調整することで、洗浄効率を向上することができる。   As described above, the membrane filtration system 1 a according to the first embodiment uses fine bubbles generated by using the pressure used in the RO membrane 14 for cleaning the pretreatment membrane 12. Thereby, the cleaning efficiency of the pretreatment film 12 can be improved without using a new power source for generating fine bubbles. At this time, the size of the microbubbles generated by the microbubble generator 16 is adjusted according to the size of the pretreatment film 12 or the like, or the microbubble generator 16 generates microbubbles of different sizes, and these are different. The cleaning efficiency can be improved by adjusting the timing of supplying the fine bubbles having the size.

[第2実施形態]
図2に示すように、第2実施形態の膜ろ過システム1bは、図1を用いて上述した膜ろ過システム1aと比較して、微細気泡含有水槽18を備えている点で異なる。この膜ろ過システム1bでは、前処理膜12の逆洗の際には、微細気泡発生装置16からラインL9を介して排出される微細気泡含有水が、微細気泡含有水槽18で貯留された後、ラインL11を介してラインL8に合流した後、逆洗ポンプP5を介して膜ろ過水とともに前処理膜12に供給される。
[Second Embodiment]
As shown in FIG. 2, the membrane filtration system 1b of 2nd Embodiment differs in the point provided with the microbubble containing water tank 18 compared with the membrane filtration system 1a mentioned above using FIG. In this membrane filtration system 1b, when the pretreatment membrane 12 is backwashed, after the fine bubble-containing water discharged from the fine bubble generator 16 via the line L9 is stored in the fine bubble-containing water tank 18, After joining the line L8 via the line L11, it is supplied to the pretreatment membrane 12 together with the membrane filtrate through the backwash pump P5.

上述した第2実施形態に係る膜ろ過システム1bでは、RO膜14でろ過を行なっていないタイミングでも、微細気泡を用いた洗浄を継続することが可能になる。また、膜ろ過システムの規模が大きく前処理膜とRO膜を複数有しており、前処理膜とRO膜が1対1のペアで無い場合、1台のRO膜から複数の前処理膜に微細気泡を注入する必要が生じる。したがって、微細気泡発生装置16から前処理膜12に微細気泡含有水を直接供給した場合、圧力や流量の調整が複雑になるため、予め微細気泡を発生させて微細気泡含有水を貯留することが有用となる。   In the membrane filtration system 1b according to the second embodiment described above, it is possible to continue the cleaning using the fine bubbles even at the timing when the RO membrane 14 is not filtered. In addition, when the membrane filtration system is large and has a plurality of pretreatment membranes and RO membranes, and the pretreatment membrane and the RO membrane are not in a one-to-one pair, a single RO membrane is converted into a plurality of pretreatment membranes. It becomes necessary to inject fine bubbles. Therefore, when the fine bubble-containing water is directly supplied from the fine bubble generator 16 to the pretreatment film 12, the adjustment of pressure and flow rate is complicated, and therefore, it is possible to generate fine bubbles and store the fine bubble-containing water in advance. Useful.

第2実施形態に係る膜ろ過システム1bでも、第1実施形態に係る膜ろ過システム1aと同様に、前処理膜12の洗浄に、RO膜14で使用した圧力を使って発生させた微細気泡を利用している。これにより、微細気泡発生のために新たな動力源を使用することなく、前処理膜12の洗浄効率を向上させることができる。   In the membrane filtration system 1b according to the second embodiment, fine bubbles generated using the pressure used in the RO membrane 14 are used for cleaning the pretreatment membrane 12 as in the membrane filtration system 1a according to the first embodiment. We are using. Thereby, the cleaning efficiency of the pretreatment film 12 can be improved without using a new power source for generating fine bubbles.

上記のように、本発明を各実施形態によって記載したが、この開示の一部をなす論述および図面はこの発明を限定するものであると理解すべきではない。この開示から当業者には様々な代替実施形態、実施例および運用技術が明らかとなる。また、本発明はここでは記載していない様々な実施形態等を含むことは勿論である。   As mentioned above, although this invention was described by each embodiment, it should not be understood that the description and drawing which form a part of this indication limit this invention. From this disclosure, various alternative embodiments, examples and operational techniques will be apparent to those skilled in the art. Further, the present invention naturally includes various embodiments not described herein.

1a,1b…膜ろ過システム
11…取水槽
12…前処理膜
13…膜ろ過水槽
14…RO膜
15…処理水槽
16…微細気泡発生装置
17…超音波発生装置
18…微細気泡含有水槽
DESCRIPTION OF SYMBOLS 1a, 1b ... Membrane filtration system 11 ... Intake tank 12 ... Pretreatment membrane 13 ... Membrane filtration water tank 14 ... RO membrane 15 ... Treated water tank 16 ... Fine bubble generator 17 ... Ultrasonic generator 18 ... Fine bubble containing water tank

Claims (6)

被処理水に含まれる不溶解性成分を除去する前処理膜と、
前記前処理膜で不溶解性成分が除去された被処理水に圧力を与える高圧ポンプと、
前記高圧ポンプで圧力が与えられた被処理水を、被処理水に含まれる溶解性成分を除去した処理水と、溶解性成分が濃縮された濃縮水とに分離する逆浸透膜と、
前記逆浸透膜から高圧で排出される濃縮水を導入して微細気泡を発生し、洗浄中の前記前処理膜に微細気泡を含む濃縮水を供給する微細気泡発生装置と、
を備えることを特徴とする膜ろ過システム。
A pretreatment film for removing insoluble components contained in the water to be treated;
A high-pressure pump that applies pressure to the water to be treated from which insoluble components have been removed by the pretreatment membrane;
A reverse osmosis membrane that separates water to be treated, which has been pressurized by the high-pressure pump, into treated water from which soluble components contained in the treated water have been removed, and concentrated water in which soluble components are concentrated;
A fine bubble generator that introduces concentrated water discharged from the reverse osmosis membrane at high pressure to generate fine bubbles, and supplies the concentrated water containing fine bubbles to the pretreatment membrane being cleaned;
A membrane filtration system comprising:
被処理水に含まれる不溶解性成分を除去する前処理膜と、
前記前処理膜で不溶解性成分が除去された被処理水に圧力を与える高圧ポンプと、
前記高圧ポンプで圧力が与えられた被処理水を、被処理水に含まれる溶解性成分を除去した処理水と、溶解性成分が濃縮された濃縮水とに分離する逆浸透膜と、
前記逆浸透膜から高圧で排出される濃縮水を導入し、微細気泡を発生する微細気泡発生装置と、
前記微細気泡生成装置で発生した微細気泡を含む濃縮水を貯留する微細気泡含有水槽と、
前記前処理膜を洗浄するタイミングで、前記微細気泡含有水槽が貯留する濃縮水を前記前処理膜に送水するポンプと、
を備えることを特徴とする膜ろ過システム。
A pretreatment film for removing insoluble components contained in the water to be treated;
A high-pressure pump that applies pressure to the water to be treated from which insoluble components have been removed by the pretreatment membrane;
A reverse osmosis membrane that separates water to be treated, which has been pressurized by the high-pressure pump, into treated water from which soluble components contained in the treated water have been removed, and concentrated water in which soluble components are concentrated;
A fine bubble generator that introduces concentrated water discharged at high pressure from the reverse osmosis membrane and generates fine bubbles;
A microbubble-containing water tank for storing concentrated water containing microbubbles generated by the microbubble generator;
A pump for feeding the concentrated water stored in the water tank containing fine bubbles to the pretreatment membrane at the timing of washing the pretreatment membrane;
A membrane filtration system comprising:
前記前処理膜の洗浄時に、超音波を発生して発生した超音波を前記前処理膜に与える超音波発生装置をさらに備える、
ことを特徴とする請求項1又は2記載の膜ろ過システム。
An ultrasonic generator that applies ultrasonic waves generated by generating ultrasonic waves to the pretreatment film when the pretreatment film is washed;
The membrane filtration system according to claim 1 or 2.
前記前処理膜の洗浄時に、前記前処理膜の一次側から微細気泡を含む濃縮水を供給する
ことを特徴とする請求項1乃至3いずれか記載の膜ろ過システム。
The membrane filtration system according to any one of claims 1 to 3, wherein concentrated water containing fine bubbles is supplied from a primary side of the pretreatment membrane during cleaning of the pretreatment membrane.
前記前処理膜の洗浄時に、前記前処理膜の一次側からの微細気泡を含む濃縮水を供給と、前記前処理膜の二次側からの微細気泡を含む濃縮水の供給とを切り替える
ことを特徴とする、請求項1乃至3いずれか記載の膜ろ過システム。
When cleaning the pretreatment membrane, switching between supplying concentrated water containing fine bubbles from the primary side of the pretreatment membrane and supplying concentrated water containing fine bubbles from the secondary side of the pretreatment membrane. The membrane filtration system according to any one of claims 1 to 3, wherein the membrane filtration system is characterized.
前記微細気泡発生装置は、空気の混入量を調整して異なる複数のサイズの微細気泡を発生する
ことを特徴とする請求項1乃至5いずれか記載の膜ろ過システム。

The membrane filtration system according to any one of claims 1 to 5, wherein the fine bubble generating device generates fine bubbles having a plurality of different sizes by adjusting an amount of air mixed therein.

JP2012026312A 2012-02-09 2012-02-09 Membrane filtration system Pending JP2013163141A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2012026312A JP2013163141A (en) 2012-02-09 2012-02-09 Membrane filtration system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2012026312A JP2013163141A (en) 2012-02-09 2012-02-09 Membrane filtration system

Publications (1)

Publication Number Publication Date
JP2013163141A true JP2013163141A (en) 2013-08-22

Family

ID=49174876

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2012026312A Pending JP2013163141A (en) 2012-02-09 2012-02-09 Membrane filtration system

Country Status (1)

Country Link
JP (1) JP2013163141A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2016016397A (en) * 2014-07-11 2016-02-01 水ing株式会社 Filtration membrane cleaning method and membrane filtration apparatus
US9333464B1 (en) 2014-10-22 2016-05-10 Koch Membrane Systems, Inc. Membrane module system with bundle enclosures and pulsed aeration and method of operation
USD779632S1 (en) 2015-08-10 2017-02-21 Koch Membrane Systems, Inc. Bundle body
KR20240135346A (en) * 2023-03-03 2024-09-10 (주)엘에스티에스 Operation method for reserve osmosis seawater desalination system that can reduce fouling of reserve osmosis membrane through nanobubble-injected concentrated water cleaning

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5317581A (en) * 1976-07-31 1978-02-17 Toshiba Machine Co Ltd Method and apparatus for cleaning semipermeable membrane
JPS5451981A (en) * 1977-10-03 1979-04-24 Yuasa Battery Co Ltd Filtration
JPS56111006A (en) * 1980-02-07 1981-09-02 Ebara Infilco Co Ltd Method for utilization of back pressure in membrane separating process
JPS6295702U (en) * 1985-12-02 1987-06-18
JP2011104488A (en) * 2009-11-13 2011-06-02 Central Filter Mfg Co Ld Washing method of filtration apparatus

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5317581A (en) * 1976-07-31 1978-02-17 Toshiba Machine Co Ltd Method and apparatus for cleaning semipermeable membrane
JPS5451981A (en) * 1977-10-03 1979-04-24 Yuasa Battery Co Ltd Filtration
JPS56111006A (en) * 1980-02-07 1981-09-02 Ebara Infilco Co Ltd Method for utilization of back pressure in membrane separating process
JPS6295702U (en) * 1985-12-02 1987-06-18
JP2011104488A (en) * 2009-11-13 2011-06-02 Central Filter Mfg Co Ld Washing method of filtration apparatus

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2016016397A (en) * 2014-07-11 2016-02-01 水ing株式会社 Filtration membrane cleaning method and membrane filtration apparatus
US9333464B1 (en) 2014-10-22 2016-05-10 Koch Membrane Systems, Inc. Membrane module system with bundle enclosures and pulsed aeration and method of operation
US9956530B2 (en) 2014-10-22 2018-05-01 Koch Membrane Systems, Inc. Membrane module system with bundle enclosures and pulsed aeration and method of operation
US10702831B2 (en) 2014-10-22 2020-07-07 Koch Separation Solutions, Inc. Membrane module system with bundle enclosures and pulsed aeration and method of operation
USD779632S1 (en) 2015-08-10 2017-02-21 Koch Membrane Systems, Inc. Bundle body
USD779631S1 (en) 2015-08-10 2017-02-21 Koch Membrane Systems, Inc. Gasification device
KR20240135346A (en) * 2023-03-03 2024-09-10 (주)엘에스티에스 Operation method for reserve osmosis seawater desalination system that can reduce fouling of reserve osmosis membrane through nanobubble-injected concentrated water cleaning
KR102860910B1 (en) * 2023-03-03 2025-09-17 (주)엘에스티에스 Operation method for reserve osmosis seawater desalination system that can reduce fouling of reserve osmosis membrane through nanobubble-injected concentrated water cleaning

Similar Documents

Publication Publication Date Title
JP5691522B2 (en) Fresh water generation system and operation method thereof
KR101744400B1 (en) Apparatus for cleaning reverse osmosis membrane filter
WO2008053700A1 (en) Method of desalting, apparatus for desalting, and bubble generator
US20130206697A1 (en) Fresh Water Generating Apparatus and Fresh Water Generating Method
JPWO2012098969A1 (en) Membrane module cleaning method, fresh water generation method and fresh water generation device
JP6358878B2 (en) Membrane filtration device
JP2013163141A (en) Membrane filtration system
EP1894612B1 (en) Method for purifying water by means of a membrane filtration unit
JP6580338B2 (en) Film processing apparatus and film processing method
WO2012111731A1 (en) Compound desalination system
JP5801249B2 (en) Desalination apparatus and desalination method
JPWO2014034845A1 (en) Fresh water generation method
JP2011104504A (en) Washing method of water treatment facility
JP2011041907A (en) Water treatment system
JP2016159241A (en) Membrane filtration system
JP2003117552A (en) Desalination apparatus
JP2004082020A (en) Operation method of hollow fiber membrane module
CA3003979A1 (en) Improved reverse osmosis or nanofiltration process for cleaning water
KR101558341B1 (en) Apparatus for membrane filtration and method for membrane physical cleaning and its drainage water treatment using microbubble
US20130082001A1 (en) Fresh Water Generating Apparatus and Fresh Water Generating Method
JP5802580B2 (en) Membrane filtration device
JP6609236B2 (en) Water treatment apparatus and water treatment method
Thiemig et al. Experiences with a reinforced UF hollow-fiber water filtration system for pretreatment of desalinated water
JP2009273972A (en) System for producing purified water by membrane treatment
US10052591B2 (en) System and method for filtration

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20140311

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20141218

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20150106

A02 Decision of refusal

Free format text: JAPANESE INTERMEDIATE CODE: A02

Effective date: 20150511