JP2011212542A - Method for backwashing filter treatment means and water treatment apparatus therefor - Google Patents

Method for backwashing filter treatment means and water treatment apparatus therefor Download PDF

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Publication number
JP2011212542A
JP2011212542A JP2010081550A JP2010081550A JP2011212542A JP 2011212542 A JP2011212542 A JP 2011212542A JP 2010081550 A JP2010081550 A JP 2010081550A JP 2010081550 A JP2010081550 A JP 2010081550A JP 2011212542 A JP2011212542 A JP 2011212542A
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Prior art keywords
water
treated
filtration
reverse osmosis
osmosis membrane
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JP2010081550A
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Japanese (ja)
Inventor
Naoki Matsumoto
直樹 松本
Keijiro Tada
景二郎 多田
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Kurita Water Industries Ltd
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Kurita Water Industries Ltd
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Abstract

PROBLEM TO BE SOLVED: To provide a method for backwashing a filter treatment means that can supply clear treated water to a rear-stage reverse osmosis membrane treatment means and efficiently backwashes a hardly blocked and inexpensive filter treatment means and a water treatment apparatus therefor.SOLUTION: The method for backwashing a filter treatment means performs filter treatment on the treated water in parallel before a reverse osmosis membrane treatment where the treated water is treated with a reverse osmosis membrane, wherein the filter treatment means has a filter body where a sheet-like member is spirally wound and a filtration tank where the filter body is filled inside so the shaft center of the filter body as to be along the direction of passing water, the sheet-like member is one in which sheet surfaces of a sheet-like mesh-sheet having vacant holes through which the treated water passes and a sheet-like spacer through which the treated water more hardly passes than the mesh sheet are overlapped, and the filter treatment means is backwashed by passing the concentrated water discharged through the reverse osmosis membrane treatment to the filter treatment means through which the treated water is not allowed to pass from a reverse direction to the direction of passing the treated water.

Description

本発明は、工業用水、市水、井水、河川水、湖沼水、工場廃水など懸濁物質等を含む被
処理水を膜分離処理する逆浸透膜処理手段の前段に設けられる濾過処理手段の逆洗方法及
びこれを適用した水処理装置に関する。
The present invention relates to a filtration treatment means provided in the preceding stage of a reverse osmosis membrane treatment means for subjecting treated water containing suspended substances such as industrial water, city water, well water, river water, lake water, and factory wastewater to membrane separation treatment. The present invention relates to a backwashing method and a water treatment apparatus to which the backwashing method is applied.

工業用水、市水、井水、河川水、湖沼水、工場廃水などの被処理水を処理する方法とし
て、例えば被処理水に無機凝集剤及びアニオン性等の高分子凝集剤を添加して被処理水に
含まれる濁質を吸着や凝結等する凝集処理をした後、砂濾過や加圧浮上処理により濁質を
除去する方法がある。しかしながら砂濾過や加圧浮上処理では、装置が大きくなってしま
うという問題がある。また、被処理水の濁度が高い場合は濁質の除去が不十分になるおそ
れがある。
As a method of treating treated water such as industrial water, city water, well water, river water, lake water, and factory wastewater, for example, an inorganic flocculant and an anionic polymer flocculant are added to the treated water. There is a method of removing turbidity by sand filtration or pressurized flotation treatment after flocculation treatment such as adsorption or condensation of the turbidity contained in the treated water. However, sand filtration and pressure levitation processing have a problem that the apparatus becomes large. Moreover, when the turbidity of to-be-processed water is high, there exists a possibility that removal of a turbidity may become inadequate.

このような問題を解決するため最近では、濾過装置として、膜分離処理手段、具体的に
は、限外濾過膜(UF)装置又は精密濾過膜(MF)装置の適用が広がってきている。し
かしながら、限外濾過膜装置や精密濾過膜装置は、懸濁物質、無機物質や有機物質による
閉塞が発生するという問題や、膜のコストが高いという問題がある。
Recently, in order to solve such a problem, application of membrane separation processing means, specifically, an ultrafiltration membrane (UF) device or a microfiltration membrane (MF) device has been spreading as a filtration device. However, the ultrafiltration membrane device and the microfiltration membrane device have a problem that clogging occurs due to suspended substances, inorganic substances, and organic substances, and a problem that the cost of the membrane is high.

また、純水等を製造するために、被処理水を逆浸透膜(RO)装置で処理する技術があ
る。そして、逆浸透膜装置では、前段で上記砂濾過、加圧浮上処理や、限外濾過装置、精
密濾過膜装置等で処理したある程度清澄な被処理水を用いる必要がある。しかしながら、
砂濾過、加圧浮上処理、限外濾過装置、精密濾過膜装置等には、上述したように、濁質の
除去が不十分になることや、閉塞が発生する等の問題がある。
Moreover, in order to manufacture pure water etc., there exists a technique which processes to-be-processed water with a reverse osmosis membrane (RO) apparatus. And in a reverse osmosis membrane apparatus, it is necessary to use the water to be treated to a certain degree that has been treated by the sand filtration, the pressure levitation treatment, the ultrafiltration apparatus, the microfiltration membrane apparatus or the like in the previous stage. However,
As described above, sand filtration, pressure levitation treatment, ultrafiltration device, microfiltration membrane device, and the like have problems such as insufficient removal of turbidity and occurrence of blockage.

ここで、濾過体として長繊維束を用いる濾過装置を、逆浸透膜装置の上流側に設けた発
電所補給水の製造装置が開示されているが(特許文献1参照)、この装置においても、逆
浸透膜装置や濾過装置の閉塞が生じるという問題や、処理水質が悪化するという問題があ
る。
Here, although the filtration apparatus using a long fiber bundle as a filter body is disclosed on the upstream side of the reverse osmosis membrane apparatus, a power plant make-up water production apparatus is disclosed (see Patent Document 1), There is a problem that the reverse osmosis membrane device and the filtration device are clogged and the quality of the treated water is deteriorated.

また、このような逆浸透膜装置の上流側に設けた濾過装置の濁質による閉塞を抑制する
ために、被処理水の通水方向とは逆の方向に洗浄水を通水するいわゆる逆洗が行われるが
、例えば、逆浸透膜を透過した透過水(処理水)を洗浄水として用いると、透過水の回収
率が悪くなり、水処理効率が低くなることが問題になる。
In addition, in order to suppress clogging due to the turbidity of the filtration device provided on the upstream side of such a reverse osmosis membrane device, so-called backwashing in which wash water is passed in a direction opposite to the direction of water to be treated is passed. However, for example, when permeated water (treated water) that has permeated through a reverse osmosis membrane is used as washing water, the recovery rate of the permeated water is deteriorated, and the water treatment efficiency is lowered.

特開平6−134490号公報JP-A-6-134490

本発明は上述した事情に鑑み、後段の逆浸透膜処理手段に清澄な処理水を供給でき且つ
閉塞し難く安価な濾過処理手段を効率よく逆洗する濾過処理手段の逆洗方法及び水処理装
置を提供することを目的とする。
In view of the above-described circumstances, the present invention provides a backwashing method and a water treatment apparatus for a filtration treatment unit that can supply clear treatment water to a subsequent reverse osmosis membrane treatment unit and efficiently backwash an inexpensive filtration treatment unit that is difficult to block. The purpose is to provide.

上記課題を解決する本発明の態様は、被処理水を逆浸透膜で処理する逆浸透膜処理の前
に被処理水を並列に濾過処理する濾過処理手段の逆洗方法であって、前記濾過処理手段が
、シート状部材が渦巻状に巻回される濾過体本体と、被処理水が通水され、前記濾過体本
体の軸芯が通水方向に沿うように前記濾過体本体が内部に充填される濾過槽とを有し、前
記シート状部材は、被処理水が通過する空孔を有するシート状のメッシュシートと、メッ
シュシートに比べて被処理水が通過し難いシート状のスペーサーのシート面同士が重ねら
れたものであり、前記逆浸透膜処理で排出される濃縮水を、被処理水が通水されていない
前記濾過処理手段に被処理水の通水方向とは逆の方向から通水することにより、前記濾過
処理手段を逆洗することを特徴とする濾過処理手段の逆洗方法にある。
An aspect of the present invention that solves the above-described problem is a backwashing method of a filtration means for filtering the treated water in parallel before the reverse osmosis membrane treatment for treating the treated water with a reverse osmosis membrane, wherein the filtration The treatment means includes a filter body having a sheet-like member wound in a spiral shape, and water to be treated is passed, and the filter body is placed in the interior so that the axis of the filter body is along the direction of water passage. The sheet-like member includes a sheet-like mesh sheet having pores through which the water to be treated passes, and a sheet-like spacer in which the water to be treated is difficult to pass compared to the mesh sheet. The sheet surfaces are overlapped, and the concentrated water discharged in the reverse osmosis membrane treatment is in a direction opposite to the direction of water to be treated to the filtration treatment means in which the water to be treated is not passed. The filtration means is back-washed by passing water through In backwash method of filtration means.

そして、前記逆浸透膜処理は、前記濾過処理手段から排出された被処理水を並列に逆浸
透膜処理するものであってもよい。
And the said reverse osmosis membrane process may perform a reverse osmosis membrane process in parallel with the to-be-processed water discharged | emitted from the said filtration process means.

また、本発明の他の態様は、シート状部材が渦巻状に巻回される濾過体本体と、被処理
水が通水され、前記濾過体本体の軸芯が通水方向に沿うように前記濾過体本体が内部に充
填される濾過槽とを有し、前記シート状部材は、被処理水が通過する空孔を有するシート
状のメッシュシートと、メッシュシートに比べて被処理水が通過し難いシート状のスペー
サーのシート面同士が重ねられたものである濾過処理手段であって、被処理水を濾過処理
する並列に配置された複数の濾過処理手段と、前記濾過処理手段の後段に設けられ前記濾
過処理手段から排出される被処理水を逆浸透膜で逆浸透膜処理する逆浸透膜処理手段と、
前記逆浸透膜処理手段から排出される濃縮水を被処理水が通水されていない前記濾過処理
手段に被処理水の通水方向とは逆の方向から導入する濃縮水導入手段とを有することを特
徴とする水処理装置にある。
Further, according to another aspect of the present invention, the filter body having the sheet-like member wound in a spiral shape, the water to be treated is passed, and the shaft core of the filter body is along the water passing direction. The filter body has a filtration tank filled therein, and the sheet-like member has a sheet-like mesh sheet having pores through which the water to be treated passes, and the water to be treated passes compared to the mesh sheet. Filtration processing means in which sheet surfaces of difficult sheet-like spacers are overlapped with each other, a plurality of filtration processing means arranged in parallel for filtering the water to be treated, and provided after the filtration processing means Reverse osmosis membrane treatment means for treating the treated water discharged from the filtration treatment means with a reverse osmosis membrane,
Concentrated water introduction means for introducing the concentrated water discharged from the reverse osmosis membrane treatment means into the filtration treatment means through which the water to be treated is not passed from the direction opposite to the water flow direction of the water to be treated. It is in the water treatment apparatus characterized by this.

シート状部材が渦巻状に巻回される濾過体本体と、被処理水が通水され、濾過体本体の
軸芯が通水方向に沿うように濾過体本体が内部に充填される濾過槽とを有し、シート状部
材が、被処理水が通過する空孔を有するシート状のメッシュシートと、メッシュシートに
比べて被処理水が通過し難いシート状のスペーサーのシート面同士が重ねられたものであ
る濾過処理手段(濾過処理装置)は、清澄な処理水が得られ、且つ、後段の逆浸透膜処理
手段(逆浸透膜装置)や濾過処理手段自体の閉塞を抑制でき、そして安価である。したが
って、後段の逆浸透膜処理手段で、好適に長期間被処理水を処理することができる。そし
て、逆浸透膜処理手段から排出される濃縮水を濾過処理手段の洗浄水とするため、水処理
効率を減少させることがなく、また、ポンプ等の洗浄液の送液手段も不要なため、低コス
ト化を図ることができる。
A filter body in which the sheet-like member is wound in a spiral shape, a filtration tank in which the water to be treated is passed, and the filter body is filled therein so that the axial core of the filter body is along the water passing direction; The sheet-like member has a sheet-like mesh sheet having pores through which the water to be treated passes, and the sheet surfaces of the sheet-like spacer in which the water to be treated is difficult to pass compared to the mesh sheet. Filtration treatment means (filtration treatment apparatus), which is a product, can provide clear treated water, and can prevent clogging of subsequent reverse osmosis membrane treatment means (reverse osmosis membrane apparatus) and filtration treatment means itself, and is inexpensive. is there. Therefore, the water to be treated can be suitably treated for a long period of time by the reverse osmosis membrane treatment means in the subsequent stage. Since the concentrated water discharged from the reverse osmosis membrane treatment means is used as the washing water for the filtration treatment means, the water treatment efficiency is not reduced, and no liquid feed means such as a pump is required. Cost can be reduced.

水処理装置例の概略系統図である。It is a schematic system diagram of the example of a water treatment apparatus. 濾過装置の構成を示す縦断面図である。It is a longitudinal cross-sectional view which shows the structure of a filtration apparatus. 濾過装置の横断面図である。It is a cross-sectional view of a filtration apparatus. 濾過処理装置の濾過体を示す斜視図である。It is a perspective view which shows the filter body of a filtration processing apparatus. メッシュシートの要部拡大図である。It is a principal part enlarged view of a mesh sheet. 逆浸透膜の差圧の測定方法を示す図である。It is a figure which shows the measuring method of the differential pressure | voltage of a reverse osmosis membrane.

以下、本発明を実施形態に基づいて詳細に説明する。
本発明は、被処理水を逆浸透膜で処理する逆浸透膜処理の前に被処理水を並列に濾過処
理する濾過処理手段の逆洗方法であって、濾過処理手段が、シート状部材が渦巻状に巻回
される濾過体本体と、被処理水が通水され、濾過体本体の軸芯が通水方向に沿うように濾
過体本体が内部に充填される濾過槽とを有し、シート状部材は、被処理水が通過する空孔
を有するシート状のメッシュシートと、メッシュシートに比べて被処理水が通過し難いシ
ート状のスペーサーのシート面同士が重ねられたものであり、逆浸透膜処理で排出される
濃縮水を、被処理水が通水されていない濾過処理手段に被処理水の通水方向とは逆の方向
から通水することにより、濾過処理手段を逆洗するものである。
Hereinafter, the present invention will be described in detail based on embodiments.
The present invention relates to a backwashing method for filtration treatment means for performing filtration treatment of water to be treated in parallel before the reverse osmosis membrane treatment for treating the water to be treated with a reverse osmosis membrane, wherein the filtration treatment means comprises a sheet-like member. A filter body that is wound in a spiral shape, and a filtration tank in which the water to be treated is passed and in which the filter body is filled so that the axial center of the filter body is along the water passing direction, The sheet-like member is a sheet-like mesh sheet having pores through which the water to be treated passes, and sheet surfaces of sheet-like spacers where the water to be treated is difficult to pass compared to the mesh sheet, By passing the concentrated water discharged by the reverse osmosis membrane treatment from the direction opposite to the direction in which the water to be treated is passed through the filtration means to which the water to be treated is not passed, the filtration means is backwashed. To do.

被処理水としては、例えば、フミン酸・フルボ酸系有機物、藻類等が生産する糖などの
生物代謝物、又は、界面活性剤等の合成化学物質などを含む水、具体的には、工業用水、
市水、井水、河川水、湖沼水、工場廃水(特に、工場からの廃水を生物処理した生物処理
水)などが挙げられるが、これらに限定されるものではない。なお、フミン質とは、植物
などが微生物に分解されることにより生じる腐食物質をいい、フミン酸等を含むものであ
り、フミン質を含有する水は、フミン質および/またはフミン質に由来する溶解性COD
成分、懸濁物質や色度成分を有する。
Examples of water to be treated include water containing a humic acid / fulvic acid organic substance, a biological metabolite such as sugar produced by algae, or a synthetic chemical substance such as a surfactant, specifically, industrial water. ,
Examples include, but are not limited to, city water, well water, river water, lake water, and factory wastewater (particularly, biologically treated water obtained by biologically treating wastewater from a factory). The humic substance refers to a corrosive substance generated by the decomposition of plants and the like into microorganisms, and includes humic acid, and the water containing the humic substance is derived from humic substance and / or humic substance. Soluble COD
Contains ingredients, suspended matter and chromaticity components.

本発明の濾過処理手段の逆洗方法を適用した水処理装置例である図1を用いて、本発明
の濾過処理手段の逆洗方法について説明する。図1は、水処理装置の概略系統図である。
The backwashing method for the filtration treatment means of the present invention will be described with reference to FIG. 1 which is an example of a water treatment apparatus to which the filtration treatment means for the filtration treatment means of the present invention is applied. FIG. 1 is a schematic system diagram of a water treatment apparatus.

図1に示すように、水処理装置10は、被処理水(原水)が貯留された原水槽11等か
ら被処理水が導入され並列に設けられている濾過処理手段12A及び12Bを有する。こ
の濾過処理手段12A及び12Bは、詳しくは後述するが、被処理中に含まれる濁質(S
S)を捕捉する濾過体を有するものである。そして、この濾過処理手段12A及び12B
の後段には、逆浸透膜を有する逆浸透膜処理手段13A及び13Bが設けられている。な
お、原水槽11、濾過処理手段12A及び12B、逆浸透膜処理手段13A及び13Bは
、被処理水や濃縮水等が後述のように通水されるように、図1の矢印で示すような配管で
繋がれている。
As shown in FIG. 1, the water treatment apparatus 10 includes filtration treatment means 12A and 12B that are introduced in parallel from the raw water tank 11 or the like in which the water to be treated (raw water) is stored. The filtration means 12A and 12B will be described later in detail, but turbidity (S
It has a filter body that captures S). And this filtration means 12A and 12B
At the subsequent stage, reverse osmosis membrane processing means 13A and 13B having reverse osmosis membranes are provided. The raw water tank 11, the filtration treatment means 12A and 12B, and the reverse osmosis membrane treatment means 13A and 13B are as shown by the arrows in FIG. 1 so that the water to be treated, concentrated water and the like are passed as described later. Connected by piping.

そして、本発明においては、この逆浸透膜処理手段13A及び13Bから排出された濃
縮水を、被処理水が通水されていない濾過処理手段12Aや濾過処理手段12Bに被処理
水の通水方向とは逆の方向から導入する濃縮水導入手段を有する。本実施形態では、濃縮
水導入手段は、濃縮水が排出される各逆浸透膜処理手段13A及び13Bの濃縮水排出口
から濾過処理手段12Aや濾過処理手段12Bへ濃縮水を供給するための配管、及び、自
動で開閉され通水される水の流路を規制する弁17A〜17Iで構成されている。なお、
図1においては、弁17A〜17Iは、その配管が締切りにならないように、各弁17A
〜17Iに遅延タイマーをプログラムに組み込んでいる。そして、後述する濾過処理手段
12A及び12Bの逆洗の頻度を、濾過処理手段12A及び12Bの被処理水処理時間、
処理量や、差圧などによって制御し、完全に自動運転ができるようにしたものである。も
ちろん、各弁17A〜17Iは自動弁ではなく、手動弁としてもよい。
In the present invention, the concentrated water discharged from the reverse osmosis membrane treatment means 13A and 13B is supplied to the filtration treatment means 12A and the filtration treatment means 12B through which the treatment water is not passed. Concentrated water introduction means for introducing from the opposite direction. In the present embodiment, the concentrated water introduction means is a pipe for supplying concentrated water from the concentrated water discharge ports of the reverse osmosis membrane treatment means 13A and 13B from which the concentrated water is discharged to the filtration treatment means 12A and the filtration treatment means 12B. And valves 17A to 17I that regulate the flow path of water that is automatically opened and closed and allowed to flow. In addition,
In FIG. 1, the valves 17 </ b> A to 17 </ b> I are arranged so that the pipes 17 </ b> A are not cut off.
A delay timer is incorporated into the program at ~ 17I. And the frequency of backwashing of the filtration means 12A and 12B, which will be described later, is the water treatment time of the treatment means 12A and 12B,
It is controlled by the processing amount and differential pressure, etc., so that it can be operated completely automatically. Of course, each of the valves 17A to 17I may be a manual valve instead of an automatic valve.

このような水処理装置10では、まず、被処理水が貯留された原水槽11から被処理水
が濾過処理手段12Aに導入される。そして、濾過処理手段12Aが有する濾過体に被処
理水中に含まれる濁質が捕捉され、濁質がある程度除去された被処理水が濾過処理手段1
2Aから排出される。この濾過処理手段12Aから排出された被処理水は、逆浸透膜処理
手段13A及び13Bに供給され、逆浸透膜により膜分離処理される。各逆浸透膜処理手
段13A及び13Bの逆浸透膜を透過した透過水が、処理水として排出される。また、各
逆浸透膜処理手段13A及び13Bから、逆浸透膜で処理していない被処理水、すなわち
、逆浸透膜を透過しておらず上記透過水よりも不純物を多く含んだいわゆる濃縮水が排出
される。なお、このような水処理の最中においては、原水槽11と濾過処理手段12Aと
をつなぐ配管に設けられた弁17A、濾過処理手段12Aと逆浸透膜処理手段13Aをつ
なぐ配管に設けられた弁17B、及び、逆浸透膜処理手段13A及び逆浸透膜処理手段1
3Bから排出される濃縮水が通水される配管に設けられた弁17Iは開けられており、そ
の他の弁17C〜17Hは閉じられている。
In such a water treatment device 10, first, the water to be treated is introduced into the filtration means 12A from the raw water tank 11 in which the water to be treated is stored. And the turbidity contained in to-be-processed water is capture | acquired by the filter body which 12A of filtration process means has, and the to-be-processed water from which the turbidity was removed to some extent is the filtration process means 1.
Discharged from 2A. The treated water discharged from the filtration means 12A is supplied to the reverse osmosis membrane treatment means 13A and 13B and subjected to membrane separation treatment by the reverse osmosis membrane. The permeated water that has permeated through the reverse osmosis membranes of the respective reverse osmosis membrane treatment means 13A and 13B is discharged as treated water. Further, from each reverse osmosis membrane treatment means 13A and 13B, water to be treated that has not been treated with the reverse osmosis membrane, that is, so-called concentrated water that does not permeate the reverse osmosis membrane and contains more impurities than the permeated water. Discharged. During such water treatment, the valve 17A provided in the pipe connecting the raw water tank 11 and the filtration treatment means 12A, and the pipe connecting the filtration treatment means 12A and the reverse osmosis membrane treatment means 13A were provided. Valve 17B and reverse osmosis membrane treatment means 13A and reverse osmosis membrane treatment means 1
The valve 17I provided in the pipe through which the concentrated water discharged from 3B is passed is opened, and the other valves 17C to 17H are closed.

そして、濾過処理手段12Aが濁質により汚染してきたら、例えば被処理水を通水後、
所定時間経過したら、濾過処理手段12Aを逆洗し、また、濾過処理は濾過処理手段12
Bにより行う。具体的には、弁17C、弁17D、弁17E及び弁17Fを開け、その他
の弁17A、弁17B、弁17G、弁17H及び弁17Iを閉じた状態とする。この状態
では、まず、被処理水が貯留された原水槽11から被処理水が濾過処理手段12Bに導入
される。この際、弁17Aは閉じているため、原水槽11からの被処理水は、濾過処理手
段12Aには供給されていない。そして、濾過処理手段12Bが有する濾過体に被処理水
中に含まれる濁質が捕捉され、濁質がある程度除去された被処理水が濾過処理手段12B
から排出される。この濾過処理手段12Bから排出された被処理水は、ポンプ等(図示無
し)の昇圧手段により昇圧されて逆浸透膜処理手段13A及び13Bに供給され、逆浸透
膜により膜分離処理される。逆浸透膜処理手段13A及び13Bの逆浸透膜を透過した透
過水が、処理水として排出される。また、逆浸透膜処理手段13A及び13Bから排出さ
れた濃縮水は、弁17Fを経由して濾過処理手段12Aに被処理水の通水方向とは逆側か
ら導入され、この濃縮水により濾過処理手段12Aが逆洗される。ここで、この濃縮水は
高圧であるため、ポンプ等の送液手段を設けなくても、逆浸透膜処理手段13A及び13
Bから濾過処理手段12Aへ送液することができる。したがって、ポンプ等のコストや使
用電力が不要である。また、ポンプ等の設置スペースも不要である。この逆洗により濾過
処理手段12Aから排出された濃縮水は、弁17Eを経由して原水槽11に戻される。そ
の後、濾過処理手段12Aの逆洗が終了したら、弁17E及び弁17Fを閉じ、弁17I
を開けることにより、逆浸透膜処理手段13A及び13Bから排出される濃縮水を、弁1
7Iを経由して排出するようにする。
And if the filtration processing means 12A has been contaminated by turbidity, for example, after passing the water to be treated,
When a predetermined time has elapsed, the filtration processing means 12A is back-washed, and the filtration processing is performed by the filtration processing means 12
Perform by B. Specifically, the valves 17C, 17D, 17E, and 17F are opened, and the other valves 17A, 17B, 17G, 17H, and 17I are closed. In this state, first, the water to be treated is introduced into the filtration means 12B from the raw water tank 11 in which the water to be treated is stored. At this time, since the valve 17A is closed, the water to be treated from the raw water tank 11 is not supplied to the filtration means 12A. And the turbidity contained in to-be-processed water is capture | acquired by the filter body which the filtration process means 12B has, and the to-be-processed water from which the turbidity was removed to some extent is the filtration process means 12B.
Discharged from. The water to be treated discharged from the filtration means 12B is boosted by a boosting means such as a pump (not shown), supplied to the reverse osmosis membrane treatment means 13A and 13B, and subjected to membrane separation treatment by the reverse osmosis membrane. The permeated water that has permeated through the reverse osmosis membranes of the reverse osmosis membrane treatment means 13A and 13B is discharged as treated water. Further, the concentrated water discharged from the reverse osmosis membrane treatment means 13A and 13B is introduced into the filtration treatment means 12A via the valve 17F from the side opposite to the water flow direction of the water to be treated. The means 12A is backwashed. Here, since this concentrated water has a high pressure, the reverse osmosis membrane treatment means 13A and 13A can be provided without providing a liquid feeding means such as a pump.
The liquid can be fed from B to the filtration means 12A. Therefore, the cost and power consumption of a pump etc. are unnecessary. Moreover, installation space for a pump or the like is not necessary. The concentrated water discharged from the filtration processing means 12A by this back washing is returned to the raw water tank 11 via the valve 17E. Thereafter, when the back washing of the filtration means 12A is completed, the valve 17E and the valve 17F are closed and the valve 17I is closed.
The concentrated water discharged from the reverse osmosis membrane treatment means 13A and 13B
Discharge via 7I.

次いで、濾過処理手段12Bが濁質により汚染してきたら、例えば被処理水を通水後、
所定時間経過したら、濾過処理手段12Bを逆洗し、また、濾過処理は濾過処理手段12
Aにより行うようにする。具体的には、弁17A、弁17B、弁17G及び弁17Hを開
け、その他の弁17C〜17F及び弁17Iを閉じた状態とする。この状態では、まず、
被処理水が貯留された原水槽11から被処理水が濾過処理手段12Aに導入される。この
際、弁17Cは閉じているため、原水槽11からの被処理水は、濾過処理手段12Bには
供給されていない。そして、濾過処理手段12Aが有する濾過体に被処理水中に含まれる
濁質が捕捉され、濁質がある程度除去された被処理水が濾過処理手段12Aから排出され
る。この濾過処理手段12Aから排出された被処理水は、ポンプ等(図示無し)の昇圧手
段により昇圧されて逆浸透膜処理手段13A及び13Bに供給され、逆浸透膜により膜分
離処理される。逆浸透膜処理手段13A及び13Bの逆浸透膜を透過した透過水が、処理
水として排出される。また、逆浸透膜処理手段13A及び13Bから排出された濃縮水は
、弁17Hを経由して濾過処理手段12Bに被処理水の通水方向とは逆側から導入され、
この濃縮水のより濾過処理手段12Bが逆洗される。ここで、この濃縮水は高圧であるた
め、ポンプ等の送液手段を設けなくても、逆浸透膜処理手段13A及び13Bから濾過処
理手段12Bへ送液することができる。この逆洗により濾過処理手段12Bから排出され
た濃縮水は、弁17Gを経由して原水槽11へ戻される。その後、濾過処理手段12Bの
逆洗が終了したら、弁17G及び弁17Hを閉じ、弁17Iを開けることにより、逆浸透
膜処理手段13A及び13Bから排出される濃縮水を、弁17Iを経由して排出するよう
にする。
Next, if the filtration means 12B is contaminated with turbidity, for example, after passing the water to be treated,
When the predetermined time has elapsed, the filtration processing means 12B is back-washed, and the filtration processing is performed by the filtration processing means 12
Do this by A. Specifically, the valves 17A, 17B, 17G, and 17H are opened, and the other valves 17C to 17F and the valve 17I are closed. In this state,
Water to be treated is introduced into the filtration means 12A from the raw water tank 11 in which the water to be treated is stored. At this time, since the valve 17C is closed, the water to be treated from the raw water tank 11 is not supplied to the filtration means 12B. Then, turbidity contained in the water to be treated is captured by the filter body of the filtration means 12A, and the water to be treated from which the turbidity has been removed to some extent is discharged from the filtration means 12A. The water to be treated discharged from the filtration means 12A is boosted by a boosting means such as a pump (not shown), supplied to the reverse osmosis membrane treatment means 13A and 13B, and subjected to membrane separation treatment by the reverse osmosis membrane. The permeated water that has permeated through the reverse osmosis membranes of the reverse osmosis membrane treatment means 13A and 13B is discharged as treated water. Further, the concentrated water discharged from the reverse osmosis membrane treatment means 13A and 13B is introduced into the filtration treatment means 12B via the valve 17H from the opposite side to the water flow direction of the treated water.
The filtration means 12B is backwashed from the concentrated water. Here, since this concentrated water is high-pressure, it can be fed from the reverse osmosis membrane treatment means 13A and 13B to the filtration treatment means 12B without providing a liquid feed means such as a pump. The concentrated water discharged from the filtration means 12B by this back washing is returned to the raw water tank 11 via the valve 17G. Thereafter, when the backwashing of the filtration means 12B is completed, the concentrated water discharged from the reverse osmosis membrane treatment means 13A and 13B is passed through the valve 17I by closing the valve 17G and the valve 17H and opening the valve 17I. Try to drain.

以上を繰り返すことにより、逆浸透膜処理手段13A及び13Bから排出される不要な
濃縮水を用いて、濾過処理手段12A及び12Bを洗浄するため、透過水(処理水)を使
用しないので、水処理の効率が高い。また、逆洗のためのポンプ等の送液手段を設けなく
てもよいため低コスト化等を図ることができる。そして、濾過処理及び逆浸透膜処理から
なる水処理を継続しながら、濾過処理を行う濾過処理手段の洗浄を行うことができるため
、継続して水処理を行うことができる。
By repeating the above, the permeated water (treated water) is not used to wash the filtration treatment means 12A and 12B using unnecessary concentrated water discharged from the reverse osmosis membrane treatment means 13A and 13B. High efficiency. Moreover, since it is not necessary to provide liquid feeding means such as a pump for backwashing, cost reduction can be achieved. And since the filtration processing means which performs a filtration process can be wash | cleaned, continuing the water treatment which consists of a filtration process and a reverse osmosis membrane process, a water treatment can be performed continuously.

なお、上述した例では、逆浸透膜処理手段を2つ設けたが、3つ以上でもよく、また、
1つでもよい。例えば逆浸透膜処理手段が1つの場合は、濾過処理手段12Aを洗浄する
際には、被処理水を濾過処理手段12B、逆浸透膜処理手段13Aに通水して水処理を行
うと共に、逆浸透膜処理手段13Aから排出される濃縮水を濾過処理手段12Aに被処理
水の通水方向とは逆に通水するようにすればよく、また、濾過処理手段12Bを洗浄する
際には、被処理水を濾過処理手段12A、逆浸透膜処理手段13Aに通水して水処理を行
うと共に、逆浸透膜処理手段13Aから排出される濃縮水を濾過処理手段12Bに被処理
水の通水方向とは逆に通水すればよい。
In the above example, two reverse osmosis membrane treatment means are provided, but three or more may be used,
One may be sufficient. For example, when there is one reverse osmosis membrane treatment means, when washing the filtration treatment means 12A, the water to be treated is passed through the filtration treatment means 12B and the reverse osmosis membrane treatment means 13A for water treatment, The concentrated water discharged from the osmotic membrane treatment means 13A may be passed through the filtration means 12A in the direction opposite to the direction of water to be treated, and when the filtration means 12B is washed, The treated water is passed through the filtration treatment means 12A and the reverse osmosis membrane treatment means 13A for water treatment, and the concentrated water discharged from the reverse osmosis membrane treatment means 13A is passed through the filtration treatment means 12B. It is only necessary to pass water in the opposite direction.

また、上述した例では、逆浸透膜処理手段13A及び13Bから排出される濃縮水のみ
を洗浄液として、濾過処理手段12A及び12Bを逆洗したが、濃縮水に次亜塩素酸ナト
リウム等の殺菌剤等の添加剤を添加した液を濾過処理手段12A及び12Bに供給して、
濾過処理手段12A及び12Bを逆洗するようにしてもよい。例えば、殺菌剤を添加する
と、濾過処理手段12A及び12Bの生物由来の汚染物質による閉塞を抑制することがで
きる。
In the above-described example, only the concentrated water discharged from the reverse osmosis membrane treatment means 13A and 13B is used as a washing liquid, and the filtration treatment means 12A and 12B are backwashed. However, the bactericide such as sodium hypochlorite is added to the concentrated water. The liquid to which the additive such as is added is supplied to the filtration means 12A and 12B,
The filtration means 12A and 12B may be backwashed. For example, when a bactericidal agent is added, blockage of the filtration means 12A and 12B due to biological contaminants can be suppressed.

また、上述した例では、逆洗により濾過処理手段12A及び12Bから排出された濃縮
水を原水槽11に戻し再び濾過処理及び逆浸透膜処理をするようにして、水処理効率がよ
り高くなるようにしたが、濃縮水が有する濁質等が、水処理装置系内の配管、逆浸透膜処
理手段や濾過処理手段を汚染する場合があるため、逆洗により濾過処理手段12A及び1
2Bから排出された濃縮水は、原水槽11に戻さず、水処理装置10の系外へ排出するよ
うにしてもよい。
In the above-described example, the concentrated water discharged from the filtration treatment means 12A and 12B by backwashing is returned to the raw water tank 11, and the filtration treatment and the reverse osmosis membrane treatment are performed again so that the water treatment efficiency becomes higher. However, the turbidity etc. of the concentrated water may contaminate the piping in the water treatment system, the reverse osmosis membrane treatment means and the filtration treatment means, so the filtration treatment means 12A and 1 by backwashing.
The concentrated water discharged from 2B may be discharged out of the system of the water treatment apparatus 10 without returning to the raw water tank 11.

そして、本発明においては、濾過処理手段12A及び12Bは、所定の濾過体を有する
ものである。濾過処理手段12A及び12Bの一例について、図2〜図4に基づいて説明
する。図2は、濾過処理手段である濾過装置の構成を示す被処理水の通水方向の縦断面図
であり、図3は、横断面図であり、図4は、濾過装置の濾過体を示す斜視図である。
In the present invention, the filtration means 12A and 12B have a predetermined filter body. An example of the filtration means 12A and 12B will be described with reference to FIGS. FIG. 2 is a longitudinal sectional view in the direction of water flow of the water to be treated showing the configuration of the filtration device as the filtration means, FIG. 3 is a transverse sectional view, and FIG. 4 shows the filter body of the filtration device. It is a perspective view.

図2及び図3に示すように、濾過装置(濾過処理手段)12は、被処理水が通水される
筒状の濾過槽41と、通水される被処理水中の濁質を捕捉する濾過体42とを有する。該
濾過体42は、濾過槽41の通水方向の両端に接続される芯材43と、芯材43に渦巻状
に巻回されたシート状部材からなる濾過体本体44を有する。このシート状部材は、被処
理水が通過する空孔を有するシート状のメッシュシート45と、メッシュシート45に比
べて被処理水が通過し難いシート状のスペーサー46のシート面同士が重ねられたもので
ある。
As shown in FIG.2 and FIG.3, the filtration apparatus (filtration process means) 12 is the filtration which capture | acquires the turbidity in the cylindrical filtration tank 41 into which the to-be-processed water flows, and the to-be-processed water to flow through And a body 42. The filter body 42 includes a core member 43 connected to both ends of the filtration tank 41 in the water passage direction, and a filter body main body 44 including a sheet-like member wound around the core member 43 in a spiral shape. In this sheet-like member, the sheet-like mesh sheet 45 having holes through which the water to be treated passes and the sheet surfaces of the sheet-like spacer 46 where the water to be treated is difficult to pass compared to the mesh sheet 45 are overlapped. Is.

また、濾過槽41の通水方向両端には、濁質(懸濁物質)等を含有する被処理水が自由
に通水できる程度の穴が複数設けられた樹脂製等の円形のプレート47が設けられ、各プ
レート47の中心に芯材43の両端が固定されている。そして、濾過体42は、濾過体本
体44の軸芯が被処理水の通水方向に沿うように、濾過体42が濾過槽41内部全体に充
填されている。また、濾過槽41の内壁と濾過体本体44の外周との隙間や、芯材43付
近の隙間は、接着剤等の被処理水が通過しない水不透過部材48で埋められており被処理
水が通過できない構成になっている。なお、濾過体本体44の軸芯とは、渦巻状に巻回さ
れた濾過体本体44の渦巻きの中心であり、本実施形態では芯材43が該当する。
In addition, a circular plate 47 made of resin or the like provided with a plurality of holes to allow water to be treated containing turbidity (suspended substance) or the like to freely pass therethrough at both ends of the filtration tank 41 in the direction of water flow. Provided, and both ends of the core member 43 are fixed to the center of each plate 47. And as for the filter body 42, the filter body 42 is filled with the whole inside of the filtration tank 41 so that the axial center of the filter body main body 44 may follow the water flow direction of to-be-processed water. Further, the gap between the inner wall of the filtration tank 41 and the outer periphery of the filter body main body 44 and the gap near the core member 43 are filled with a water-impermeable member 48 through which the water to be treated such as an adhesive does not pass. Cannot pass through. The shaft core of the filter body 44 is the center of the spiral of the filter body 44 wound in a spiral shape, and the core material 43 corresponds to this embodiment.

このような濾過装置12に被処理水を通水すると、スペーサー46はメッシュシート4
5に比べて被処理水が通過し難いため、被処理水の多くは、メッシュシート45の空孔を
通りメッシュシート45を略縦断、すなわちメッシュシート45を面方向に通過し、その
際被処理水に含まれる濁質がメッシュシート45にトラップされ、濁質が除去された被処
理水が濾過槽41から排出される。このように、被処理水が通過する空孔を有し濁質を捕
捉することができるメッシュシート45を、厚さ方向に横断するのではなく縦断するよう
に、被処理水が通水される構造の濾過装置12とすることで、清澄な処理水が得られる。
したがって、濾過装置12は、上述した図1に示すように、逆浸透膜(RO膜)を有する
逆浸透膜装置(逆浸透膜処理手段)13の前段で使用することができ、逆浸透膜装置の閉
塞を抑制することができる。そして、濾過装置12は、限外濾過膜置又は精密濾過膜装置
のように、膜を用いた濾過ではないので閉塞し難く、また安価である。
When the water to be treated is passed through such a filtration device 12, the spacer 46 becomes the mesh sheet 4.
Since the water to be treated is less likely to pass than 5, most of the water to be treated passes through the pores of the mesh sheet 45 and substantially passes through the mesh sheet 45, that is, passes through the mesh sheet 45 in the surface direction. The turbidity contained in the water is trapped in the mesh sheet 45, and the water to be treated from which the turbidity has been removed is discharged from the filtration tank 41. In this way, the water to be treated is passed through the mesh sheet 45 that has pores through which the water to be treated passes and can capture turbidity, not vertically across the thickness direction but in a longitudinal direction. By setting it as the filtration apparatus 12 of a structure, clear treated water is obtained.
Therefore, as shown in FIG. 1 described above, the filtration device 12 can be used in the preceding stage of the reverse osmosis membrane device (reverse osmosis membrane treatment means) 13 having the reverse osmosis membrane (RO membrane). Can be prevented. The filtration device 12 is not filtered using a membrane as in the case of an ultrafiltration membrane device or a microfiltration membrane device, so it is difficult to block and is inexpensive.

ここで、メッシュシート45は、被処理水が通過することができる空孔を有し被処理水
が含有する濁質を所望の程度除去できればよく、特に限定はないが、例えば、図5に示す
ような、縦糸49aと横糸49bで形成された織物が挙げられる。なお、図5は、メッシ
ュシート45の要部拡大平面図(図5(a))及び図5(a)のA−A´断面図(図5(
b))である。
Here, the mesh sheet 45 is not particularly limited as long as the mesh sheet 45 has pores through which the water to be treated can pass and can remove the turbidity contained in the water to be treated to a desired extent. For example, FIG. Examples thereof include a woven fabric formed of warp yarns 49a and weft yarns 49b. 5 is an enlarged plan view of the main part of the mesh sheet 45 (FIG. 5A) and a cross-sectional view taken along the line AA ′ in FIG.
b)).

そして、メッシュシート45の隣り合う縦糸49a同士や隣り合う横糸49b同士の距
離、すなわち、オープニング(図5中OPで示す。)は200〜4000μm程度が好ま
しく、また、空孔(図5中斜線で示す。)の大きさ、すなわち、メッシュシート45の平
面視の空間率(オープニングエリア)は40〜90%程度とすることが好ましく、そして
、交点部の高さ(図中Tで示す厚さ)は500〜1200μmであることが好ましい。具
体的な商品としては、例えば、100目〜8目(NBC社)程度のものを用いればよい。
この範囲であれば、特に好適に濁質を除去することができる。また、逆浸透膜装置、例え
ば逆浸透膜を巻き回した形状のスパイラル型逆浸透膜装置では、交点部の高さが通常0.
65〜1.2mm程度のメッシュシートを原水流路スペーサーとして用いているため、逆
浸透膜装置の前段で用いる濾過装置、すなわち、逆浸透膜装置に処理水を供給する濾過装
置として用いて逆浸透膜装置の閉塞を防止させる場合、逆浸透膜装置よりも交点部の高さ
の低いメッシュシートを用いることが好ましいためである。
The distance between adjacent warp yarns 49a and adjacent weft yarns 49b of the mesh sheet 45, that is, the opening (indicated by OP in FIG. 5) is preferably about 200 to 4000 μm, and air holes (indicated by diagonal lines in FIG. 5) ), That is, the space ratio (opening area) in a plan view of the mesh sheet 45 is preferably about 40 to 90%, and the height of the intersection (thickness indicated by T in the figure) Is preferably 500 to 1200 μm. As a specific product, for example, a product of about 100th to 8th (NBC) may be used.
If it is this range, a turbidity can be removed especially suitably. Further, in a reverse osmosis membrane device, for example, a spiral type reverse osmosis membrane device having a shape in which a reverse osmosis membrane is wound, the height of the intersection is usually 0.
Since a mesh sheet of about 65 to 1.2 mm is used as the raw water flow path spacer, it is used as a filtration device used in the preceding stage of the reverse osmosis membrane device, that is, as a filtration device for supplying treated water to the reverse osmosis membrane device. This is because it is preferable to use a mesh sheet having a lower intersection portion than the reverse osmosis membrane device when blocking the membrane device.

また、縦糸49aや横糸49bとなる繊維の直径Dは、それぞれ直径0.1〜0.6m
mが好ましく、さらに好ましくは0.1〜0.4mm程度である。被処理水の濁度や処理
量にもよるが、被処理水を略縦断できるようにするためには、ある程度の太さの繊維で被
処理水が通過させる空孔を形成する必要があり、また、太すぎると形成される空孔が大き
くなりすぎて、濁質を除去できなくなるためである。
Moreover, the diameter D of the fiber used as the warp 49a or the weft 49b is 0.1-0.6 m in diameter, respectively.
m is preferable, and more preferably about 0.1 to 0.4 mm. Depending on the turbidity and the amount of water to be treated, in order to be able to cut the water to be treated substantially vertically, it is necessary to form holes through which the water to be treated passes with fibers of a certain thickness, Moreover, if the thickness is too large, the formed pores become too large, and the suspended matter cannot be removed.

メッシュシート45を構成する糸等の材質としては、例えば、ポリオレフィン、ポリエ
ステル、ナイロン、ポリフッ化ビニリデン(PVDF)などの合成樹脂や、金属繊維等が
挙げられるが、耐薬品性や経済性の観点から、ポレオレフィンが好ましい。なお、図5に
おいては、織物を例示したが、繊維で形成された比較的大きな空孔を有する不織布でもよ
い。
Examples of the material constituting the mesh sheet 45 include synthetic resins such as polyolefin, polyester, nylon, and polyvinylidene fluoride (PVDF), and metal fibers. From the viewpoint of chemical resistance and economy. Polyolefins are preferred. In addition, although the woven fabric was illustrated in FIG. 5, the nonwoven fabric which has a comparatively big void | hole formed with the fiber may be sufficient.

また、スペーサー46は、メッシュシート45に比べて被処理水が通過し難いシート状
のものであれば特に限定されず、例えば、空孔を全く有さず被処理水を通過させない水不
透過シートや、直径0.1〜100μm、好ましくは0.5〜30μm程度の繊維で形成
された不織布等、又は、これらを貼り合わせたり熱融着で一体成型する等により重ねられ
たものとしてもよい。なお、スペーサー46が被処理水を通過させない水不透過シートで
あれば、被処理水をメッシュシート45に均一に接触させることができるので、スペーサ
ー46は水不透過シートを有するものであることが好ましい。そして、不織布をスペーサ
ー46として用いると、不織布表面の毛羽立ち部位で被処理水の濁質を捕捉することがで
き濾過装置12の濁質捕捉性を向上させることができるため、不織布と水不透過シートと
からなるスペーサーとすることが好ましい。
The spacer 46 is not particularly limited as long as the water to be treated is less likely to pass through than the mesh sheet 45. For example, the water impervious sheet does not have any holes and does not allow the water to be treated to pass through. Or it may be a non-woven fabric formed of fibers having a diameter of 0.1 to 100 [mu] m, preferably about 0.5 to 30 [mu] m, or the like, or those laminated by integrally bonding them by heat fusion or the like. In addition, since the to-be-processed water can be made to contact the mesh sheet 45 uniformly if the spacer 46 is a water-impermeable sheet which does not allow the to-be-processed water to pass through, the spacer 46 may have a water-impermeable sheet. preferable. And if a nonwoven fabric is used as the spacer 46, the turbidity of the to-be-processed water can be captured at the fluffing part of the nonwoven fabric surface, and the turbidity capture property of the filtration apparatus 12 can be improved. It is preferable to use a spacer consisting of

スペーサー46の材質としては、例えば、ポリオレフィン、ポリエステル、ナイロン、
ポリフッ化ビニリデン(PVDF)、金属繊維、活性炭繊維等が挙げられる。耐薬品性や
経済性の観点からは、ポレオレフィンが好ましい。また、被処理水中に含まれるNaCl
O等の還元処理をすることができ、活性炭塔などの装置を不要にすることができるという
観点からは、活性炭繊維が好ましい。
Examples of the material of the spacer 46 include polyolefin, polyester, nylon,
Examples thereof include polyvinylidene fluoride (PVDF), metal fibers, activated carbon fibers, and the like. Polyolefins are preferred from the viewpoint of chemical resistance and economy. NaCl contained in the water to be treated
From the viewpoint that reduction treatment of O or the like can be performed and an apparatus such as an activated carbon tower can be eliminated, activated carbon fibers are preferable.

そして、メッシュシート45及びスペーサー46を重ね合わせる形態に特に限定はなく
、シート面同士を貼り合わせてもよく熱融着で一体成型してもよい。なお、メッシュシー
ト45とスペーサー46の大きさは同一でなくてもよいが、均一に被処理水を処理するた
めには、ほぼ同一であることが好ましい。メッシュシート45やスペーサー46の通水方
向の長さは、被処理水の濁度、処理量や求める処理水の濁度にもよるが、例えば、200
〜1000mm程度とすればよい。
The form in which the mesh sheet 45 and the spacer 46 are overlapped is not particularly limited, and the sheet surfaces may be bonded together or integrally formed by heat fusion. In addition, although the magnitude | size of the mesh sheet 45 and the spacer 46 does not need to be the same, in order to process a to-be-processed water uniformly, it is preferable that it is substantially the same. The length of the mesh sheet 45 and the spacer 46 in the water flow direction depends on the turbidity of the water to be treated, the amount of treatment, and the turbidity of the treated water to be obtained.
What is necessary is just about -1000 mm.

このメッシュシート45及びスペーサー46を重ね合わせたシート状部材を巻きつける
芯材43の材質は特に限定されず、プラスチックや金属などを用いることができるが、経
済性の観点からは塩化ビニル配管(CVP配管)とすることが好ましい。また、芯材43
の形状も特に限定されず、例えば円柱状でも角柱状でもよい。なお、シート状部材を芯材
43に巻きつける方法も特に限定は無く、例えばシート状部材の端部を接着剤等で芯材4
3に固定し、該芯材43を中心として、シート状部材をのり巻き状に巻き込み、被処理水
の処理量や濁度等に応じて、任意の径となるように巻きつければよい。
The material of the core member 43 around which the sheet member on which the mesh sheet 45 and the spacer 46 are superimposed is wound is not particularly limited, and plastic, metal, or the like can be used, but from the viewpoint of economy, vinyl chloride piping (CVP) Piping). Also, the core material 43
The shape is not particularly limited, and may be, for example, cylindrical or prismatic. The method for winding the sheet-like member around the core member 43 is not particularly limited. For example, the end of the sheet-like member is bonded to the core member 4 with an adhesive or the like.
3, the sheet member is wound around the core member 43 in a roll shape, and wound to have an arbitrary diameter according to the amount of water to be treated, turbidity, and the like.

そして、濾過槽41に限定はなく、例えば材質はステンレス製や繊維強化プラスチック
(FRP)製とすることができ、また、大きさは中空の円柱状(筒状)であれば、直径1
00〜1000mm、高さ200〜1000mmとすることができる。また、図2では、
筒状の濾過槽41としたが、筒状でなくてもよく、通水できる形状、すなわち、中空であ
ればよく、例えば角柱に空洞を設けた形状でもよい。
The filter tank 41 is not limited. For example, the material can be made of stainless steel or fiber reinforced plastic (FRP), and if the size is a hollow cylindrical shape (tubular shape), the diameter is 1
It can be set to 00 to 1000 mm and a height of 200 to 1000 mm. In FIG.
Although it was set as the cylindrical filtration tank 41, it does not need to be a cylinder and what is necessary is just the shape which can permeate | transmit water, ie, a hollow, for example, the shape which provided the cavity in the prism.

図2においては、濾過体42として、芯材43に3回巻回された濾過体本体44を有す
るものを用いたが、巻回す回数に制限はなく、被処理水の処理量及び濁度等により適宜調
節すればよい。したがって、濾過体本体44が1回のみ巻回された濾過体42としてもよ
いが、巻回す回数が多いほどスペーサー46によりメッシュシート45の形状が保持しや
すくなり、被処理水が均一にメッシュシート45を縦断できるようになって、水処理が安
定するため好ましい。
In FIG. 2, the filter body 42 having the filter body main body 44 wound three times around the core material 43 is used. However, the number of windings is not limited, and the treatment amount, turbidity, etc. of the water to be treated May be adjusted as appropriate. Therefore, the filter body 42 may be the filter body 42 wound only once, but the shape of the mesh sheet 45 is more easily held by the spacer 46 as the number of times of winding is increased, and the water to be treated is uniformly distributed in the mesh sheet. 45 can be cut longitudinally, and the water treatment is stable, which is preferable.

また、図2においては、濾過体42として、芯材43に濾過体本体44が巻回された物
を用いたが、芯材43はなくてもよく、例えばスペーサー46等でメッシュシート45の
通水時の形状を保持し、被処理水がメッシュシート45を面方向に通過(縦断)すること
ができれば、濾過体本体44のみからなる濾過体42としてもよい。
In FIG. 2, a filter body 42 in which a filter body main body 44 is wound around a core material 43 is used as the filter body 42, but the core material 43 may be omitted. For example, the mesh sheet 45 may be passed by a spacer 46 or the like. The filter body 42 including only the filter body main body 44 may be used as long as the water shape is maintained and the water to be treated can pass (vertically cut) the mesh sheet 45 in the surface direction.

また、図2においては、中空の円柱状の濾過槽41に濾過体42を充填した濾過装置1
2としたが、濾過体42にFRPなどのシートを巻きつけて被処理水が漏れないように接
合したものとしてもよい。また、スペーサー46を水不透過の材質とし、被処理水が漏れ
ないようにすることにより、スペーサー46が濾過槽41を兼ねるようにしてもよい。
Moreover, in FIG. 2, the filtration apparatus 1 which filled the filter body 42 in the hollow cylindrical filtration tank 41 is shown.
However, the filter 42 may be wound around a sheet of FRP or the like so that the water to be treated does not leak. Moreover, the spacer 46 may be made to serve as the filtration tank 41 by making the spacer 46 a water-impermeable material so that the water to be treated does not leak.

また、濾過装置12の後段に設ける逆浸透膜装置13は、メッシュシート45の被処理
水通水方向の断面積よりも被処理水の通水路の断面積が大きい、例えば、スパイラル型の
ものではメッシュシート45の交点部の高さよりも原水流路の幅が大きいものが好ましい
。逆浸透膜装置13の形態に特に限定はないが、例えば、袋とじにした逆浸透膜を側面に
通水孔を有する中空の芯材に巻き回した形状のいわゆるスパイラル型のものが、大型化に
対応し易いため好ましい。特に、濾過装置12と同一の直径を有するスパイラル型の逆浸
透膜装置とすることが好ましい。なお、スパイラル型の逆浸透膜装置13を用いると、逆
浸透膜で不純物を膜分離処理された処理水(透過水)が、中空の芯材から排出され、芯材
以外からは逆浸透膜で膜分離処理されていない不純物を多く含んだいわゆる濃縮水が排出
される。
Further, the reverse osmosis membrane device 13 provided at the subsequent stage of the filtration device 12 has a cross-sectional area of the water passage of the treated water larger than the cross-sectional area of the mesh sheet 45 in the water passage direction of the treated water. What has the width | variety of a raw | natural water flow path larger than the height of the intersection part of the mesh sheet 45 is preferable. The form of the reverse osmosis membrane device 13 is not particularly limited. For example, a so-called spiral-type device in which a reverse osmosis membrane bound in a bag is wound around a hollow core member having a water passage hole on its side surface is increased in size. Since it is easy to respond to, it is preferable. In particular, a spiral type reverse osmosis membrane device having the same diameter as the filtration device 12 is preferable. When the spiral type reverse osmosis membrane device 13 is used, treated water (permeated water) obtained by separation of impurities by the reverse osmosis membrane is discharged from the hollow core material, and the reverse osmosis membrane is used from other than the core material. So-called concentrated water containing a large amount of impurities not subjected to membrane separation is discharged.

また、濾過処理の前段で、被処理水に無機凝集剤や高分子凝集剤等の凝集剤を添加する
凝集処理をするようにしてもよい。凝集処理により、被処理水中に含まれる濁質とでフロ
ック(凝集物)が形成されるため、後段の濾過処理により、濁質が捕捉されやすくなって
より清澄な被処理水を得ることができる。なお、凝集処理を行う場合、水処理装置10は
、原水槽11と濾過処理手段12Aとの間や、原水槽11と濾過処理手段12Bとの間に
、凝集処理手段を設ければよい。凝集処理手段としては、被処理水が導入される反応槽と
、反応槽または反応槽の前段で凝集剤を導入するポンプ等からなる凝集剤導入手段と、必
要に応じて被処理水を撹拌する撹拌機を有するものとすればよい。
Moreover, you may make it perform the aggregation process which adds flocculants, such as an inorganic flocculant and a polymer flocculent, to a to-be-processed water before the filtration process. Since flocs (aggregates) are formed by the turbidity contained in the water to be treated by the flocculation treatment, the turbidity is easily captured by the subsequent filtration treatment, and a clearer water to be treated can be obtained. . In addition, when performing a flocculation process, the water treatment apparatus 10 should just provide a flocculation process means between the raw | natural water tank 11 and the filtration process means 12A, or between the raw | natural water tank 11 and the filtration process means 12B. As the coagulation treatment means, a reaction tank into which the water to be treated is introduced, a coagulant introduction means comprising a pump or the like for introducing the coagulant in the reaction tank or the previous stage of the reaction tank, and the water to be treated are stirred if necessary. What is necessary is just to have a stirrer.

以下に、後段に逆浸透膜処理手段(逆浸透膜装置)13を有し上記所定の濾過体を有す
る濾過処理手段(濾過装置)12の効果を示す参考例を示す。
(参考実施例1)
被処理水(原水)として、濁度2.0〜3.0度、残留塩素(as.Cl):0.0
5ppm未満、水温:24.5〜25.5℃の工業用水を、濾過装置12の後段に逆浸透
膜装置13を設けた水処理装置を用い、逆浸透膜装置の入り口圧力:0.75MPa、逆
浸透膜装置から排出される濃縮水量:1.35m/h、処理水量:0.25m/hと
なる水量で、被処理水を通水して処理した。なお、濾過装置12や、逆浸透膜装置13の
構成は以下の通りである。
Below, the reference example which shows the effect of the filtration process means (filter apparatus) 12 which has the reverse osmosis membrane process means (reverse osmosis membrane apparatus) 13 in the back | latter stage and has the said predetermined filter body is shown.
(Reference Example 1)
As water to be treated (raw water), turbidity 2.0-3.0 degrees, residual chlorine (as.Cl 2): 0.0
Less than 5 ppm, water temperature: 24.5 to 25.5 ° C. industrial water using a water treatment device provided with a reverse osmosis membrane device 13 at the subsequent stage of the filtration device 12, an inlet pressure of the reverse osmosis membrane device: 0.75 MPa, The water to be treated was passed through and treated with the amount of concentrated water discharged from the reverse osmosis membrane device: 1.35 m 3 / h and the amount of treated water: 0.25 m 3 / h. The configurations of the filtration device 12 and the reverse osmosis membrane device 13 are as follows.

<濾過装置>
濾過槽・・・内径100mmの円筒状容器(ベッセル)
濾過体・・・メッシュシートをポリエチレン製の直径0.3mmの繊維からなる縦糸及
び横糸で形成された図5に示す1m×10mで交点部の高さTが0.85mm、オープニ
ング3000μm、オープニングエリア82%の織物とし、スペーサーをPET(ポリエ
チレンテレフタラート)製の1m×10m×厚さ0.1mmのフィルム(水不透過フィル
ム)とし、これらを重ね合わせて四隅を熱融着したシート状部材を作成し、このシート状
部材を水不透過フィルムが外側になるようにして直径20mmの塩化ビニル製のパイプ(
芯材)に10m巻きつけて形成した、直径100mmの濾過体
水不透過部材:濾過槽の内壁と濾過体本体の外周との隙間や、芯材付近の隙間を、被処
理水を通過させない接着剤で充填した
濾過装置の通水量:1.6m/h(LV=200m/h)
<Filtration device>
Filtration tank ... Cylindrical container (vessel) with an inner diameter of 100 mm
Filter body: mesh sheet made of warp and weft made of polyethylene fibers with a diameter of 0.3 mm, 1 m × 10 m shown in FIG. 5, intersection point height T is 0.85 mm, opening is 3000 μm, opening area A sheet-like member made of 82% woven fabric, a spacer made of PET (polyethylene terephthalate), 1 m × 10 m × 0.1 mm thick film (water impervious film), and the four corners are laminated and heat-sealed. A pipe made of vinyl chloride having a diameter of 20 mm (with a water-impermeable film facing outside)
Filter body with a diameter of 100 mm, water-impermeable member formed by wrapping 10 m around the core material): Adhesion that does not allow the water to be treated to pass through the gap between the inner wall of the filtration tank and the outer periphery of the filter body, or the gap near the core material Flow rate of the filtration device filled with the agent: 1.6 m 3 / h (LV = 200 m / h)

<逆浸透膜装置>
逆浸透膜・・・ザ・ダウ・ケミカル・カンパニー製FILMTEC LE−4040(
原水流路スペーサーの交点部の高さ:0.85mm)を用いたスパイラル型のもの(直径
100mm)
処理時における逆浸透膜の差圧を、図6に示すように、逆浸透膜装置の入口の圧力P1
と濃縮水出口の圧力P2の差(P1−P2(MPa))として求めたところ、72時間通
水してもほぼ一定で安定しており、閉塞が防止されることが確認された。なお、その後、
0.2MPaに上昇し通水が不能となった。
<Reverse osmosis membrane device>
Reverse osmosis membrane: FILMTEC LE-4040 (The Dow Chemical Company)
Spiral type using raw water flow path spacer intersection height (0.85 mm) (diameter 100 mm)
The differential pressure of the reverse osmosis membrane at the time of processing is shown in FIG.
And the pressure P2 at the outlet of the concentrated water (P1−P2 (MPa)), it was confirmed that even when water was passed for 72 hours, the water was almost constant and stable, and blockage was prevented. After that,
The pressure increased to 0.2 MPa, and water passage became impossible.

また、濾過装置12に導入する被処理水(原水)、及び、被処理水の通水開始から72
時間経過時に逆浸透膜装置13から排出された処理水について、微粒子数をレーザー光遮
断方式の微粒子カウンターで測定し、また、濁度をカオリン標準液を用いた透過光測定方
法により求めたところ、表1に示す結果となった。表1に示すように、参考実施例1では
、200μm以上の濁質が除去されており、濾過装置12を用いなかった参考比較例1と
比べて顕著に濁質が除去されていたことから、参考実施例1では濾過装置12から排出さ
れる処理水が清澄で、その結果後段の逆浸透膜装置13での膜分離処理が好適に行われた
ことが確認された。
In addition, the water to be treated (raw water) to be introduced into the filtering device 12 and 72 from the start of water flow of the water to be treated
With respect to the treated water discharged from the reverse osmosis membrane device 13 over time, the number of fine particles was measured with a fine particle counter of a laser light blocking method, and the turbidity was determined by a transmitted light measurement method using a kaolin standard solution. The results shown in Table 1 were obtained. As shown in Table 1, in Reference Example 1, the turbidity of 200 μm or more was removed, and the turbidity was remarkably removed as compared with Reference Comparative Example 1 in which the filtration device 12 was not used. In Reference Example 1, it was confirmed that the treated water discharged from the filtration device 12 was clear, and as a result, the membrane separation treatment in the reverse osmosis membrane device 13 in the subsequent stage was suitably performed.

Figure 2011212542
Figure 2011212542

(参考比較例1)
濾過装置12を設けず、逆浸透膜装置のみとした以外は、参考実施例1と同様の操作を
行った。微粒子数及び濁度の測定結果を表1に示す。また、逆浸透膜の差圧は、通水直後
からが上昇し、24時間後には0.2MPaとなり、通水不能になった。
(Reference Comparative Example 1)
The same operation as in Reference Example 1 was performed except that the filtration device 12 was not provided and only the reverse osmosis membrane device was used. The measurement results of the number of fine particles and turbidity are shown in Table 1. Further, the differential pressure of the reverse osmosis membrane increased immediately after water flow, and after 24 hours became 0.2 MPa, making water flow impossible.

(参考実施例2)
スペーサーとして、直径17.5μmのポレオレフィン系繊維で形成された1m×10
m×厚さ0.22mmの不織布(日本バイリーン製 FT−330N)1枚と、PET(
ポリエチレンテレフタラート)製の1m×10m×厚さ0.1mmのフィルム(水不透過
フィルム)1枚とを重ね合わせて四隅を熱融着して固定したものを用いた以外は、参考実
施例1と同様の操作を行った。微粒子数及び濁度の測定結果を表1に示す。この結果、逆
浸透膜の差圧は、30日間通水してもほぼ一定で安定しており、閉塞が長期間防止される
ことが確認された。また、表1に示すように、参考実施例2では、50μm以上の濁質が
除去されており、濾過装置12を用いなかった参考比較例1や、参考実施例1と比べても
顕著に濁質が除去されていたことから、参考実施例2では濾過装置12から排出される処
理水が顕著に清澄で、その結果後段の逆浸透膜装置13での膜分離処理が好適に行われた
ことが確認された。
(Reference Example 2)
As a spacer, 1 m × 10 made of polyolefin fibers having a diameter of 17.5 μm
One non-woven fabric of mx thickness 0.22mm (FT-330N made by Nippon Vilene) and PET (
Reference Example 1 except that a 1 m × 10 m × 0.1 mm thick film (water impervious film) made of polyethylene terephthalate was superposed and fixed by heat-sealing the four corners. The same operation was performed. The measurement results of the number of fine particles and turbidity are shown in Table 1. As a result, it was confirmed that the differential pressure of the reverse osmosis membrane was almost constant and stable even when water was passed for 30 days, and occlusion was prevented for a long time. Moreover, as shown in Table 1, in Reference Example 2, turbidity of 50 μm or more was removed, and it was significantly more turbid than Reference Comparative Example 1 and Reference Example 1 in which the filtration device 12 was not used. Since the quality was removed, the treated water discharged from the filtration device 12 was remarkably clarified in Reference Example 2, and as a result, the membrane separation treatment in the reverse osmosis membrane device 13 in the subsequent stage was suitably performed. Was confirmed.

(参考実施例3)
スペーサーとして、直径15μmの活性炭繊維で形成された1m×10m×厚さ0.3
mmの不織布(ユニチカ製活性炭繊維 A−15)1枚と、PET(ポリエチレンテレフ
タラート)製の1m×10m×厚さ0.1mmのフィルム(水不透過フィルム)1枚とを
重ね合わせて四隅を熱融着して固定したものを用いた以外は、参考実施例1と同様の操作
を行った。微粒子数及び濁度の測定結果を表1に示す。この結果、逆浸透膜の差圧は、3
0日間通水してもほぼ一定で安定しており、閉塞が長期間防止されることが確認された。
また、表1に示すように、参考実施例3では、50μm以上の濁質が除去されており、参
考比較例1や、参考実施例1と比べても顕著に濁質が除去されていたことから、参考実施
例3では濾過装置12から排出される処理水が顕著に清澄で、その結果後段の逆浸透膜装
置13での膜分離処理が好適に行われたことが確認された。
(Reference Example 3)
As a spacer, 1 m × 10 m × thickness 0.3 made of activated carbon fiber with a diameter of 15 μm
1 mm × 10 mm non-woven fabric (Unitika activated carbon fiber A-15) and 1 mm × 10 m × 0.1 mm thick film (water impervious film) made of PET (polyethylene terephthalate) The same operation as in Reference Example 1 was performed, except that a material fixed by heat fusion was used. The measurement results of the number of fine particles and turbidity are shown in Table 1. As a result, the differential pressure of the reverse osmosis membrane is 3
It was confirmed that even if water was passed for 0 days, it was almost constant and stable, and occlusion was prevented for a long time.
Moreover, as shown in Table 1, in Reference Example 3, turbidity of 50 μm or more was removed, and turbidity was remarkably removed as compared with Reference Comparative Example 1 and Reference Example 1. Thus, in Reference Example 3, it was confirmed that the treated water discharged from the filtration device 12 was remarkably clarified, and as a result, the membrane separation treatment in the subsequent reverse osmosis membrane device 13 was suitably performed.

そして、この参考実施例3と同様の水処理装置に、0.5ppm(as.Cl)の残
留塩素を有する栃木県野木町の水道水を100時間通水した結果、安定して残留塩素濃度
0.05ppm(as.Cl)未満の処理水が得られた。
And, as a result of passing tap water of Nogi-cho, Tochigi Prefecture having 0.5 ppm (as.Cl 2 ) residual chlorine through the water treatment apparatus similar to that of Reference Example 3 for 100 hours, the residual chlorine concentration was stable. A treated water of less than 0.05 ppm (as. Cl 2 ) was obtained.

10 水処理装置、 11 原水槽、 12 濾過装置(濾過処理手段)、 13 逆浸
透膜装置(逆浸透膜処理手段)、 17A〜17I 弁、 41 濾過槽、 42 濾過
体、 43 芯材、 44 濾過体本体、 45 メッシュシート、 46 スペーサー
、 47 プレート、 48 水不透過部材、 49a 縦糸、 49b 横糸
DESCRIPTION OF SYMBOLS 10 Water treatment apparatus, 11 Raw water tank, 12 Filtration apparatus (filtration treatment means), 13 Reverse osmosis membrane apparatus (reverse osmosis membrane treatment means), 17A-17I valve, 41 Filtration tank, 42 Filter body, 43 Core material, 44 Filtration Body body, 45 mesh sheet, 46 spacer, 47 plate, 48 water impervious member, 49a warp, 49b weft

Claims (3)

被処理水を逆浸透膜で処理する逆浸透膜処理の前に被処理水を並列に濾過処理する濾過
処理手段の逆洗方法であって、
前記濾過処理手段が、シート状部材が渦巻状に巻回される濾過体本体と、被処理水が通
水され、前記濾過体本体の軸芯が通水方向に沿うように前記濾過体本体が内部に充填され
る濾過槽とを有し、前記シート状部材は、被処理水が通過する空孔を有するシート状のメ
ッシュシートと、メッシュシートに比べて被処理水が通過し難いシート状のスペーサーの
シート面同士が重ねられたものであり、
前記逆浸透膜処理で排出される濃縮水を、被処理水が通水されていない前記濾過処理手
段に被処理水の通水方向とは逆の方向から通水することにより、前記濾過処理手段を逆洗
することを特徴とする濾過処理手段の逆洗方法。
A reverse washing method of a filtration means for filtering the treated water in parallel before the reverse osmosis membrane treatment for treating the treated water with a reverse osmosis membrane,
The filtration means includes a filter body having a sheet-like member wound in a spiral shape, water to be treated, and the filter body so that an axis of the filter body is along a water passage direction. The sheet-like member has a sheet-like mesh sheet having pores through which the water to be treated passes, and a sheet-like material through which the water to be treated is difficult to pass compared to the mesh sheet. The sheet surfaces of the spacer are overlapped,
By passing the concentrated water discharged in the reverse osmosis membrane treatment from the direction opposite to the water flow direction of the water to be treated, the filtration treatment means is passed through the filtration treatment means through which the water to be treated is not passed. A backwashing method of the filtration means characterized by backwashing.
前記逆浸透膜処理は、前記濾過処理手段から排出された被処理水を並列に逆浸透膜処理
するものであることを特徴とする請求項1に記載の濾過処理手段の逆洗方法。
The reverse washing method of the filtration processing means according to claim 1, wherein the reverse osmosis membrane treatment is a reverse osmosis membrane treatment of water to be treated discharged from the filtration treatment means in parallel.
シート状部材が渦巻状に巻回される濾過体本体と、被処理水が通水され、前記濾過体本
体の軸芯が通水方向に沿うように前記濾過体本体が内部に充填される濾過槽とを有し、前
記シート状部材は、被処理水が通過する空孔を有するシート状のメッシュシートと、メッ
シュシートに比べて被処理水が通過し難いシート状のスペーサーのシート面同士が重ねら
れたものである濾過処理手段であって、被処理水を濾過処理する並列に配置された複数の
濾過処理手段と、
前記濾過処理手段の後段に設けられ前記濾過処理手段から排出される被処理水を逆浸透
膜で逆浸透膜処理する逆浸透膜処理手段と、
前記逆浸透膜処理手段から排出される濃縮水を被処理水が通水されていない前記濾過処
理手段に被処理水の通水方向とは逆の方向から導入する濃縮水導入手段とを有することを
特徴とする水処理装置。
A filter body in which a sheet-like member is spirally wound, and a filter in which water to be treated is passed, and the filter body is filled in such a manner that the shaft core of the filter body is along the water passing direction. The sheet-like member has a sheet-like mesh sheet having pores through which the water to be treated passes, and sheet surfaces of the sheet-like spacer in which the water to be treated is difficult to pass compared to the mesh sheet. A plurality of filtration processing means arranged in parallel for filtering the water to be treated.
A reverse osmosis membrane treatment means which is provided at a subsequent stage of the filtration treatment means and performs a reverse osmosis membrane treatment with a reverse osmosis membrane on the water to be treated discharged from the filtration treatment means;
Concentrated water introduction means for introducing the concentrated water discharged from the reverse osmosis membrane treatment means into the filtration treatment means through which the water to be treated is not passed from the direction opposite to the water flow direction of the water to be treated. Water treatment device characterized by.
JP2010081550A 2010-03-31 2010-03-31 Method for backwashing filter treatment means and water treatment apparatus therefor Pending JP2011212542A (en)

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Country Link
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107381907A (en) * 2017-09-08 2017-11-24 浙江伊瑞尔净水设备有限公司 A kind of medical ultrapure water machine

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52109669A (en) * 1976-03-10 1977-09-14 Yuasa Battery Co Ltd Filter
JPH09313812A (en) * 1996-05-28 1997-12-09 Wako Sangyo Kk Spiral filter element
JPH10263539A (en) * 1997-03-28 1998-10-06 Japan Organo Co Ltd Member treating method of water to be treated and membrane treating device
JPH11244852A (en) * 1998-02-26 1999-09-14 Japan Organo Co Ltd Desalination device and back washing method of filter used for desalination device
JP2007014902A (en) * 2005-07-08 2007-01-25 Mitsubishi Heavy Ind Ltd Desalination apparatus and washing method of pretreatment membrane of desalination apparatus

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52109669A (en) * 1976-03-10 1977-09-14 Yuasa Battery Co Ltd Filter
JPH09313812A (en) * 1996-05-28 1997-12-09 Wako Sangyo Kk Spiral filter element
JPH10263539A (en) * 1997-03-28 1998-10-06 Japan Organo Co Ltd Member treating method of water to be treated and membrane treating device
JPH11244852A (en) * 1998-02-26 1999-09-14 Japan Organo Co Ltd Desalination device and back washing method of filter used for desalination device
JP2007014902A (en) * 2005-07-08 2007-01-25 Mitsubishi Heavy Ind Ltd Desalination apparatus and washing method of pretreatment membrane of desalination apparatus

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107381907A (en) * 2017-09-08 2017-11-24 浙江伊瑞尔净水设备有限公司 A kind of medical ultrapure water machine

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