JP2003103122A - Filtering method - Google Patents

Filtering method

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Publication number
JP2003103122A
JP2003103122A JP2001298864A JP2001298864A JP2003103122A JP 2003103122 A JP2003103122 A JP 2003103122A JP 2001298864 A JP2001298864 A JP 2001298864A JP 2001298864 A JP2001298864 A JP 2001298864A JP 2003103122 A JP2003103122 A JP 2003103122A
Authority
JP
Japan
Prior art keywords
filtration
liquid
tank
solid
supernatant
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
JP2001298864A
Other languages
Japanese (ja)
Inventor
Kazuhisa Kumami
和久 熊見
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.)
Daicel Corp
Daicen Membrane Systems Ltd
Original Assignee
Daicel Chemical Industries Ltd
Daicen Membrane Systems Ltd
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 Daicel Chemical Industries Ltd, Daicen Membrane Systems Ltd filed Critical Daicel Chemical Industries Ltd
Priority to JP2001298864A priority Critical patent/JP2003103122A/en
Publication of JP2003103122A publication Critical patent/JP2003103122A/en
Pending legal-status Critical Current

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  • Filtration Of Liquid (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for filtering suspension colloid at a high removal rate. SOLUTION: This filtering method comprises a step to obtain a supernatant liquid by settling the suspension colloid-containing liquid to be treated, a step to filter dynamically the supernatant liquid obtained at the preceding step by a filter medium having substantially uniform pores and a step to store the permeated liquid obtained at the preceding step in a water storage tank.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、ダイナミック濾過
を利用した濾過処理方法に関する。
TECHNICAL FIELD The present invention relates to a filtration treatment method using dynamic filtration.

【0002】[0002]

【従来の技術及び発明が解決しようとする課題】活性汚
泥法等を適用して処理された生物処理液は、未だ多量の
懸濁質を含んでおり、そのまま河川等に放流すると水質
汚染を引き起こすため、不織布等を用いた濾過によって
懸濁質の除去処理がなされている。
2. Description of the Related Art The biological treatment liquid treated by applying the activated sludge method and the like still contains a large amount of suspended solids, which causes water pollution when discharged directly to rivers. Therefore, the suspended matter is removed by filtration using a non-woven fabric or the like.

【0003】このような不織布を用いた濾過の場合、ミ
クロフィルター等に比べると目開きが大きいので、所謂
ダイナミック濾過により、懸濁質の除去率を高めること
が行われている。このダイナミック濾過は、不織布やネ
ットの孔に懸濁質乃至はフロック(活性汚泥等の懸濁質
の凝集塊)を沈積させ、ダイナミック膜を形成させて行
う濾過法であるため、安定した濾過能力を維持するに
は、好適なダイナミック膜の速やかな形成と厚みの制御
が重要となる。
In the case of filtration using such a non-woven fabric, since the mesh size is larger than that of a micro filter or the like, so-called dynamic filtration is used to increase the removal rate of suspended matter. This dynamic filtration is a filtration method that deposits suspended solids or flocs (aggregates of suspended solids such as activated sludge) in the pores of non-woven fabrics and nets to form a dynamic membrane, and therefore has a stable filtration capability. In order to maintain the above, rapid formation of a suitable dynamic film and control of the thickness are important.

【0004】本発明は、生物処理された懸濁質を含む被
処理液から懸濁質を除去する方法として適した濾過処理
方法を提供することを課題とする。
An object of the present invention is to provide a filtration treatment method suitable as a method for removing suspended matter from a liquid to be treated containing the biologically treated suspended matter.

【0005】[0005]

【課題を解決するための手段】本発明は、上記課題の解
決手段として、懸濁質を含む被処理液を沈降処理させて
上澄み液を得る工程と、前記工程で得られた上澄み液を
実質的に均一な孔を有する濾過体でダイナミック濾過す
る工程と、前記工程で得られた透過液を貯水槽に貯水す
る工程を具備する濾過処理方法を提供する。
Means for Solving the Problems As a means for solving the above problems, the present invention substantially comprises a step of obtaining a supernatant by subjecting a liquid to be treated containing a suspension to a sedimentation treatment, and a supernatant obtained in the above step. Provided is a filtration treatment method comprising: a step of dynamically filtering with a filter having uniform pores; and a step of storing the permeated liquid obtained in the step in a water storage tank.

【0006】本発明における「沈降処理」は、重力沈降
処理と凝集剤の添加による沈降処理のいずれか一方又は
両方の併用を含む。
The "sedimentation treatment" in the present invention includes either one or both of gravity sedimentation treatment and sedimentation treatment by addition of a flocculant.

【0007】[0007]

【発明の実施の形態】以下、図面により本発明の濾過処
理方法を説明する。図1は濾過処理方法の処理フローを
示す概念図、図2は図1で用いる固液分離装置の概念図
である。本発明は図1に示す処理フローに限定されるも
のではなく、必要に応じて当業者において通常なされる
他の処理工程を付加することができる。
BEST MODE FOR CARRYING OUT THE INVENTION The filtration method of the present invention will be described below with reference to the drawings. FIG. 1 is a conceptual diagram showing a processing flow of a filtration treatment method, and FIG. 2 is a conceptual diagram of a solid-liquid separation device used in FIG. The present invention is not limited to the processing flow shown in FIG. 1, and other processing steps usually performed by those skilled in the art can be added if necessary.

【0008】活性汚泥法で処理された生物処理水(被処
理水)は、沈降処理槽1の沈降槽2に入れる。この沈降
槽2では、重力沈降処理又は凝集剤添加によりフロック
を形成させる沈降処理により、懸濁質(SS)を底部に
沈降させる。沈降処理の方法は、被処理水中のSS濃
度、SSの粒径等を考慮して選択する。
Biologically treated water (water to be treated) treated by the activated sludge method is put in the settling tank 2 of the settling tank 1. In the settling tank 2, the suspension material (SS) is settled to the bottom by gravity settling processing or settling processing of forming flocs by adding a flocculant. The method of sedimentation treatment is selected in consideration of the SS concentration in the water to be treated, the particle size of SS and the like.

【0009】沈降槽2の上澄み部分は、仕切り板4を越
えて溢れさせることにより、上澄み液槽3に流入させ
る。この上澄み液槽3内の上澄み液中のSS濃度は、後
工程におけるダイナミック濾過を好適に行うため、5〜
100mg/Lが好ましく、10〜50mg/Lがより
好ましい。16は汚泥引き抜きラインである。
The supernatant portion of the settling tank 2 is caused to overflow the partition plate 4 and overflow into the supernatant liquid tank 3. The SS concentration in the supernatant liquid in the supernatant liquid tank 3 is 5 to 5 in order to suitably perform the dynamic filtration in the subsequent step.
100 mg / L is preferable, and 10-50 mg / L is more preferable. 16 is a sludge drawing line.

【0010】次に、ポンプ31を作動させ、上澄み液槽
3の上澄み液を上澄み液ライン11から固液分離装置5
に送り、実質的に均一な孔を有する濾過体でダイナミッ
ク濾過する。この工程で用いる固液分離装置5として
は、図2に示すものを用いることができる。
Next, the pump 31 is actuated, and the supernatant liquid of the supernatant liquid tank 3 is separated from the supernatant liquid line 11 by the solid-liquid separation device 5.
And is subjected to dynamic filtration with a filter body having substantially uniform pores. As the solid-liquid separation device 5 used in this step, the one shown in FIG. 2 can be used.

【0011】固液分離槽21には所要数の濾過エレメン
ト22が配置されている。18は濃縮液排出ライン、2
3は濾過エレメント22の表面を洗浄するための散気装
置、24は固液分離槽21のオーバーフローラインであ
る。図2の装置は、濾過エレメント22が上澄み液の中
に浸漬された直接浸漬型であるが、濾過エレメント22
をハウジング等に収容したモジュールとして、固液分離
槽21の外部に置く外部設置型にすることもできる。
A required number of filter elements 22 are arranged in the solid-liquid separation tank 21. 18 is a concentrate discharge line, 2
3 is an air diffuser for cleaning the surface of the filtration element 22, and 24 is an overflow line of the solid-liquid separation tank 21. The apparatus of FIG. 2 is a direct immersion type in which the filtration element 22 is immersed in the supernatant liquid.
It is also possible to use an externally installed type in which the module is housed in a housing or the like and is placed outside the solid-liquid separation tank 21.

【0012】濾過エレメント22は、1以上の所要数の
集水管を備えた枠体の両面に、濾過体を張り付けた袋状
のものであり、図2では、一つの集水管が透過液ノズル
となっている。複数の濾過エレメント22におけるそれ
ぞれの透過液ノズルは、透過液ライン12に接続されて
いる。
The filter element 22 is a bag-like member in which a filter body is attached to both sides of a frame body having one or more required number of water collecting pipes. In FIG. 2, one water collecting pipe is a permeate nozzle. Has become. Each permeate nozzle of the plurality of filtration elements 22 is connected to the permeate line 12.

【0013】濾過体は、ダイナミック膜の形成を容易に
し、高い透過流束を維持するため、実質的に均一な孔径
の孔を有するものを使用し、例えばネットが好ましい。
なお、実質的に均一な孔径とは、全ての孔の径が完全に
均一である場合と、本発明の目的を損なわない範囲内
で、製造上の誤差や継続使用に伴う経日的変化による誤
差(例えば、±数%程度の誤差)がある場合を含むもの
である。このように濾過体としてネットのようなものを
使用した場合、全ての孔の孔径は実質的に同一であるの
で、本発明でいう濾過体の平均孔径は、そのまま全ての
孔の孔径とほぼ同一となる。
In order to facilitate the formation of a dynamic membrane and maintain a high permeation flux, the filter body should be one having pores having a substantially uniform pore size, for example, a net is preferable.
In addition, the substantially uniform pore diameter means a case where all the pore diameters are completely uniform, and within a range not impairing the object of the present invention, due to a manufacturing error or a change with time due to continuous use. This includes the case where there is an error (for example, an error of about ± several%). Thus, when a net-like material is used as the filter body, since the pore diameters of all the pores are substantially the same, the average pore diameter of the filter body in the present invention is almost the same as the pore diameter of all the pores. Becomes

【0014】濾過エレメント22の濾過体として用いる
ネットは、平均孔径が10〜50μmのものが好まし
く、10〜30μmのものがより好ましい。
The net used as the filter body of the filter element 22 preferably has an average pore size of 10 to 50 μm, more preferably 10 to 30 μm.

【0015】ネットは金属繊維又はプラスチック繊維か
らなるものであり、金属繊維としては、鉄、銀、銅、銅
合金、チタン、ステンレス、基材となる金属に銀や銅を
メッキしたものからなるものが挙げられるが、銅、ステ
ンレスが好ましい。プラスチック繊維としては、ポリエ
ステル、ポリスチレン、ポリ塩化ビニル、ポリ塩化ビニ
リデン、ポリテトラフルオロエチレン、ポリ(メタ)ア
クリル酸エステル、ビスコースレーヨン、酢酸セルロー
ス、ポリエチレン、ポリプロピレン等のポリオレフィ
ン、ポリエーテル、ポリエーテルエステル、更にこれら
の共重合体、ブレンド物や架橋物等が挙げられるが、ポ
リ塩化ビニリデン、ポリエステル、ポリエチレン、ポリ
プロピレンが好ましく、ポリエステル、ポリエチレンが
より好ましい。
The net is made of metal fiber or plastic fiber, and the metal fiber is made of iron, silver, copper, copper alloy, titanium, stainless steel, or a base metal plated with silver or copper. However, copper and stainless steel are preferable. Examples of plastic fibers include polyester, polystyrene, polyvinyl chloride, polyvinylidene chloride, polytetrafluoroethylene, poly (meth) acrylic acid ester, viscose rayon, cellulose acetate, polyethylene, polypropylene and other polyolefins, polyethers, polyether esters. Further, these copolymers, blends, crosslinked products and the like can be mentioned, but polyvinylidene chloride, polyester, polyethylene and polypropylene are preferable, and polyester and polyethylene are more preferable.

【0016】ダイナミック濾過条件は、ダイナミック膜
を形成できる条件であれば特に制限されるものではない
が、膜間差圧が0.1〜5kPa程度で濾過運転するこ
とが望ましい。
The dynamic filtration condition is not particularly limited as long as it can form a dynamic membrane, but it is desirable to carry out the filtration operation at a transmembrane pressure difference of about 0.1 to 5 kPa.

【0017】次に、固液分離装置5で濾過処理された透
過液は、透過液ライン12から貯水槽6に送られて貯水
される。
Next, the permeated liquid filtered by the solid-liquid separation device 5 is sent from the permeated liquid line 12 to the water storage tank 6 and is stored therein.

【0018】このような濾過運転を継続して行った場
合、濾過体表面に過剰のSS乃至はフロック(活性汚泥
等のSSの凝集塊)が付着して濾過能力が低下するた
め、適宜逆圧洗浄を行って過剰なSS乃至はフロックを
取り除く。濾過運転時間が余り長すぎると、逆圧洗浄に
よる洗浄性が低下するため、本発明では1回の濾過時間
を5〜20分間とし、濾過の間に逆圧洗浄を行うことが
望ましい。
When such a filtration operation is continuously performed, excessive SS or flocs (aggregates of SS such as activated sludge) are attached to the surface of the filter body to reduce the filtration ability, so that the back pressure is appropriately adjusted. Wash to remove excess SS or flocs. If the filtration operation time is too long, the detergency of the back pressure cleaning is deteriorated. Therefore, in the present invention, it is desirable to set the filtration time for one time to 5 to 20 minutes and perform the back pressure cleaning during the filtration.

【0019】この逆圧洗浄は、循環ポンプ32を作動さ
せて貯水槽6内の透過液を逆圧洗浄ライン14から逆圧
洗浄槽7に送った後、濾過体内部に透過液を供給するこ
とにより行う。透過液には、洗浄性を高めるため、酸及
び/又は次亜塩素酸ナトリウムを添加することができ
る。また、固液分離槽21の底面から、散気装置23で
空気を曝気することで濾過体表面のSSを除去する方法
を、逆圧洗浄と組み合わせてもよい。
In this back pressure cleaning, the permeate in the water storage tank 6 is sent from the back pressure cleaning line 14 to the back pressure cleaning tank 7 by operating the circulation pump 32, and then the permeate is supplied to the inside of the filter body. By. An acid and / or sodium hypochlorite can be added to the permeated liquid in order to enhance the cleaning property. Further, the method of removing SS on the surface of the filter body by aerating air from the bottom surface of the solid-liquid separation tank 21 with the air diffuser 23 may be combined with back pressure cleaning.

【0020】更に濾過運転を長期間継続した場合、上澄
み液ライン11、透過液ライン12及び貯水槽6のそれ
ぞれの管壁や内壁にスケールが付着蓄積されるため、酸
水溶液及び/又は次亜塩素酸ナトリウム水溶液を流して
洗浄することが望ましい。このスケールの洗浄は、上澄
み液槽3内に酸等を添加し、上澄み液ライン11、固液
分離装置5(固液分離槽21)、濃縮液排出ライン18
の順による循環経路(循環経路A)による洗浄と、固液
分離槽21、透過液ライン12、貯水槽6、逆圧洗浄ラ
イン14、固液分離槽21の順による循環経路(循環経
路B)による洗浄を行う。
Further, when the filtration operation is continued for a long period of time, scale is adhered and accumulated on the respective pipe walls and inner walls of the supernatant liquid line 11, the permeate liquid line 12 and the water storage tank 6, so that the acid aqueous solution and / or hypochlorous acid It is desirable to wash by flushing with an aqueous sodium acid solution. To wash the scale, an acid or the like is added to the supernatant liquid tank 3, the supernatant liquid line 11, the solid-liquid separation device 5 (solid-liquid separation tank 21), and the concentrated liquid discharge line 18 are added.
Cleaning by the circulation path (circulation path A) in the order of, and the circulation path (circulation path B) by the solid-liquid separation tank 21, the permeate line 12, the water storage tank 6, the back pressure cleaning line 14, and the solid-liquid separation tank 21 in this order. Wash with.

【0021】逆圧洗浄及びスケールの洗浄に用いる酸と
しては、クエン酸等のキレート作用のある有機酸、硝酸
等の無機酸を用いることができる。
As the acid used for back pressure cleaning and scale cleaning, an organic acid having a chelating action such as citric acid or an inorganic acid such as nitric acid can be used.

【0022】本発明の濾過処理方法を適用すれば、50
〜95%の除去率で上澄み液中のSSを除去することが
できる。
If the filtration method of the present invention is applied, 50
SS in the supernatant can be removed with a removal rate of ~ 95%.

【0023】本発明の濾過処理方法は、汚水処理場等に
おける活性汚泥等を含む排水、各種施設の排水及び家庭
排水の処理、その他懸濁物を含む排水、更には河川、湖
沼等の浄化処理等に適用することができる。
The filtration treatment method of the present invention is a treatment of wastewater containing activated sludge, etc. in wastewater treatment plants, etc., treatment of wastewater of various facilities and domestic wastewater, wastewater containing other suspended matter, and purification treatment of rivers, lakes and marshes. Etc. can be applied.

【0024】[0024]

【実施例】以下に、実施例に基づいて本発明をより詳細
に説明するが、本発明はこれらの実施例によって限定さ
れるものではない。
The present invention will be described in more detail based on the following examples, but the invention is not intended to be limited by these examples.

【0025】実施例1 図1に示すような処理フローにより、次の条件で濾過運
転した。
Example 1 According to the process flow shown in FIG. 1, the filtration operation was carried out under the following conditions.

【0026】被処理水(沈降槽2内):MLSSが10
00mg/Lの活性汚泥液 上澄み液(上澄み液槽3内):MLSSが50mg/L 固液分離装置:図2に示すように、ハウジング内に間隔
20mmで鉛直方向に5枚並べた平板状濾過体(平織ス
テンレス製ネット、有効濾過面積500cm2/枚、目
開き37μm、線径35μm、開口率27%)が収容さ
れているもの 透水速度:10m/日(膜間差圧1kPa)の定透過量
濾過運転 このような条件で濾過運転を行い、10分ごとに0.5
分間、20m/日で透過液(有効塩素濃度5mg/Lの
次亜塩素酸ナトリウム溶液)による濾過体の逆圧洗浄を
行った。24時間経過後の透水速度は10m/日であ
り、MLSS濃度は5mg/Lであった。また、30日
ごとに、硝酸を用いて、循環経路A、Bのスケール除去
を行った。但し、水(上澄み液又は透過液)1Lに対し
て、1N硝酸水溶液を100ml添加した。
Water to be treated (in the settling tank 2): MLSS is 10
00 mg / L of activated sludge liquid supernatant (in the supernatant liquid tank 3): MLSS is 50 mg / L Solid-liquid separation device: As shown in FIG. 2, five plates are vertically arranged in the housing at intervals of 20 mm. A body (a net made of plain woven stainless steel, an effective filtration area of 500 cm 2 / sheet, an opening of 37 μm, a wire diameter of 35 μm, an aperture ratio of 27%) is stored. Permeation rate: 10 m / day (transmembrane pressure difference of 1 kPa) Volume filtration operation Filtration operation is performed under such conditions and 0.5 is performed every 10 minutes.
The filter body was back-pressure washed with a permeated liquid (sodium hypochlorite solution having an effective chlorine concentration of 5 mg / L) at 20 m / day for minutes. The water permeation rate after 24 hours was 10 m / day, and the MLSS concentration was 5 mg / L. In addition, every 30 days, the scales of circulation routes A and B were removed using nitric acid. However, 100 ml of 1N nitric acid aqueous solution was added to 1 L of water (supernatant or permeate).

【0027】[0027]

【発明の効果】本発明の濾過処理方法によれば、下水処
理場等で生じる生物処理後の上澄み液から、河川に放流
できる程度までSSを除去することができる。
EFFECTS OF THE INVENTION According to the filtration method of the present invention, SS can be removed from the supernatant liquid after biological treatment generated in a sewage treatment plant or the like to the extent that it can be discharged into a river.

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

【図1】 本発明の濾過処理方法を説明するための処理
フローの概念図。
FIG. 1 is a conceptual diagram of a processing flow for explaining a filtration processing method of the present invention.

【図2】 図1で用いる固液分離装置の概念図。FIG. 2 is a conceptual diagram of a solid-liquid separation device used in FIG.

【符号の説明】[Explanation of symbols]

1 沈降処理槽 2 沈降槽 3 上澄み液槽 4 仕切り板 5 固液分離槽 6 貯水槽 7 逆圧洗浄槽 1 sedimentation tank 2 settling tank 3 supernatant liquid tank 4 partition boards 5 Solid-liquid separation tank 6 water tank 7 Back pressure cleaning tank

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D015 BA19 BB01 BB05 CA02 EA32 FA01 FA02 FA16 FA26 4D066 BA01 BB12 FA02    ─────────────────────────────────────────────────── ─── Continued front page    F term (reference) 4D015 BA19 BB01 BB05 CA02 EA32                       FA01 FA02 FA16 FA26                 4D066 BA01 BB12 FA02

Claims (7)

【特許請求の範囲】[Claims] 【請求項1】 懸濁質を含む被処理液を沈降処理させて
上澄み液を得る工程と、前記工程で得られた上澄み液を
実質的に均一な孔を有する濾過体でダイナミック濾過す
る工程と、前記工程で得られた透過液を貯水槽に貯水す
る工程を具備する濾過処理方法。
1. A step of obtaining a supernatant by subjecting a liquid to be treated containing a suspension to a sedimentation treatment, and a step of dynamically filtering the supernatant obtained in the above step with a filter having substantially uniform pores. A filtration method comprising the step of storing the permeated liquid obtained in the above step in a water storage tank.
【請求項2】 上澄み液中の懸濁質濃度が5〜100m
g/Lである請求項1記載の濾過処理方法。
2. The concentration of suspended matter in the supernatant liquid is 5 to 100 m.
The filtration treatment method according to claim 1, wherein the filtration treatment is g / L.
【請求項3】 濾過体が平均孔径10〜50μmのネッ
トである請求項1又は2記載の濾過処理方法。
3. The filtration treatment method according to claim 1, wherein the filter body is a net having an average pore size of 10 to 50 μm.
【請求項4】 濾過時間が5〜20分間で、濾過の間に
逆圧洗浄を行う請求項1〜3のいずれか1記載の濾過処
理方法。
4. The filtration treatment method according to claim 1, wherein the filtration time is 5 to 20 minutes, and the back pressure washing is performed during the filtration.
【請求項5】 逆圧洗浄時に濾過体の下方から曝気して
濾過体表面を洗浄する請求項4記載の濾過処理方法。
5. The filtration treatment method according to claim 4, wherein the surface of the filter is washed by aerating from below the filter during the back pressure cleaning.
【請求項6】 逆圧洗浄時の洗浄水として、透過液中に
酸及び/又は次亜塩素酸ナトリウムを添加したものを用
いる請求項4又は5記載の濾過処理方法。
6. The filtration treatment method according to claim 4 or 5, wherein as the washing water for the back pressure washing, one in which an acid and / or sodium hypochlorite is added to the permeate is used.
【請求項7】 懸濁質を含む被処理液を沈降処理させて
上澄み液を得る工程が沈降処理槽で行われ、前記工程で
得られた上澄み液を実質的に均一な孔を有する濾過体で
ダイナミック濾過する工程が固液分離槽内で行われるも
のであり、沈降処理槽と固液分離槽とが管で連結され、
固液分離槽と貯水槽が管で連結されており、沈降処理槽
と固液分離槽とを連結する管、固液分離槽と貯水槽を連
結する管及び貯水槽内部を、酸水溶液及び/又は次亜塩
素酸ナトリウム水溶液で洗浄する請求項1〜6のいずれ
か1記載の濾過処理方法。
7. A filter body having substantially uniform pores, wherein a step of settling a liquid to be treated containing a suspension to obtain a supernatant liquid is carried out in a sedimentation treatment tank, and the supernatant liquid obtained in the above step is provided with substantially uniform pores. The process of dynamic filtration is performed in the solid-liquid separation tank, and the sedimentation treatment tank and the solid-liquid separation tank are connected by a pipe,
The solid-liquid separation tank and the water storage tank are connected by a pipe, and a pipe connecting the sedimentation treatment tank and the solid-liquid separation tank, a pipe connecting the solid-liquid separation tank and the water storage tank, and Alternatively, the filtration treatment method according to any one of claims 1 to 6, which is washed with an aqueous solution of sodium hypochlorite.
JP2001298864A 2001-09-28 2001-09-28 Filtering method Pending JP2003103122A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101212710B1 (en) 2012-04-25 2012-12-14 주식회사 시노펙스 A system for purifying discharging water of wastewater treatment plant

Citations (6)

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Publication number Priority date Publication date Assignee Title
JPH1157739A (en) * 1997-08-25 1999-03-02 Hitachi Ltd Water purifying method
JP2000070685A (en) * 1998-08-27 2000-03-07 Daicel Chem Ind Ltd Metbod for washing solid-liquid separation membrane
JP2001038176A (en) * 1999-07-28 2001-02-13 Hitoshi Daido Washing method for medicinal liquid in dynamic filter body
JP2001149761A (en) * 1999-12-01 2001-06-05 Ebara Corp Solid/liquid separation method and solid/liquid separation device
JP2001224935A (en) * 2000-02-17 2001-08-21 Hitoshi Daido Chemical washing method for dynamic filtration body and dynamic filtration device
JP2001259318A (en) * 2000-03-16 2001-09-25 Japan Organo Co Ltd Filter

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH1157739A (en) * 1997-08-25 1999-03-02 Hitachi Ltd Water purifying method
JP2000070685A (en) * 1998-08-27 2000-03-07 Daicel Chem Ind Ltd Metbod for washing solid-liquid separation membrane
JP2001038176A (en) * 1999-07-28 2001-02-13 Hitoshi Daido Washing method for medicinal liquid in dynamic filter body
JP2001149761A (en) * 1999-12-01 2001-06-05 Ebara Corp Solid/liquid separation method and solid/liquid separation device
JP2001224935A (en) * 2000-02-17 2001-08-21 Hitoshi Daido Chemical washing method for dynamic filtration body and dynamic filtration device
JP2001259318A (en) * 2000-03-16 2001-09-25 Japan Organo Co Ltd Filter

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101212710B1 (en) 2012-04-25 2012-12-14 주식회사 시노펙스 A system for purifying discharging water of wastewater treatment plant

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