JP2004130164A - Method and apparatus for filtering aqueous suspension - Google Patents

Method and apparatus for filtering aqueous suspension Download PDF

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Publication number
JP2004130164A
JP2004130164A JP2002294922A JP2002294922A JP2004130164A JP 2004130164 A JP2004130164 A JP 2004130164A JP 2002294922 A JP2002294922 A JP 2002294922A JP 2002294922 A JP2002294922 A JP 2002294922A JP 2004130164 A JP2004130164 A JP 2004130164A
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Japan
Prior art keywords
filter medium
filtration
suction
water flow
water
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JP2002294922A
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Japanese (ja)
Inventor
Katsuyuki Kataoka
片岡 克之
Toshihiro Tanaka
田中 俊博
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Ebara Corp
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Ebara Corp
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a filtering method for filtering suspended particles in raw water of every kind such as sewage or the like at a high speed by a simple and compact filter apparatus while markedly reducing a rise in loss head, and the filter apparatus using the same. <P>SOLUTION: A sucked water stream forming pipe is rotatably provided in close vicinity to the surface layer of the filter medium packed bed provided in the filter apparatus to form sucked water streams while performing the filtering treatment of water to be treated and rotating the sucked water stream forming pipe, and the filtered matter on the surface layer of the filter medium packed bed is excluded while discharging the washing wastewater containing the excluded filtered matter. It is preferable to make the rotary speed of the sucked water stream forming pipe variable and to use a floatable filter medium as the filter medium. <P>COPYRIGHT: (C)2004,JPO

Description

【0001】
【発明の属する技術分野】
本発明は下水、工場排水などの懸濁粒子を含有する懸濁水(以下「原水」ともいう)の高速ろ過方法及び装置に関し、原水中の懸濁粒子を低い損失水頭で、高速ろ過できる技術に関する。
また、本発明は、特に有機性の懸濁粒子を含有する合流式下水道の雨天時越流水(CSOと略される)又は下水処理施設に流入する下水の高速固液分離技術として極めて好適な革新技術である。
【0002】
【従来の技術】
最近合流式下水道における雨天時越流水(CSO)の公共用水域への汚濁負荷が大きな問題になっている。CSOを極力コンパクトな設備で固液分離できる新技術が待望されている。
従来、懸濁液からSSをろ過除去する技術は、砂、アンスラサイトなどの粒状物をろ材とする深層ろ過(Deep Bed Fi1tration)が公知であるが、下水などの有機性SSを大きなろ過速度で除去しようとすると、目詰まり進行が激しく、実用的でなかった。
【0003】
アンスラサイト、砂以外の各種粒状固体(例えば粒状プラスチック)をろ材とするろ過法も検討されているが、ろ材粒径を大きくして目詰まりを少なくすると、SSの除去率が悪化してしまうなどの矛盾点が生じた(特許文献1、特許文献2)。特に、下水などが含む有機性SSは粘着力が強いので、これら下水などを対象としてSS除去率が高く、かつ目詰まりが少なく、ろ過抵抗の増加が少ないという相反する要求を満足できる技術は実用化されていなかった。
【0004】
【特許文献1】
特開平4−187294号公報
【0005】
【特許文献2】
特開平4−363105号公報
【0006】
【発明が解決しようとする課題】
本発明は、簡単かつコンパクトな装置によって、下水など各種原水中の懸濁粒子を損失水頭の上昇を著しく少なくしながら高速ろ過できる新技術を提供する。
【0007】
【課題を解決するための手段】
本発明は、下記の手段により上記の課題を解決した。
(1)ろ過装置内に設けたろ材充填層の表層面に近接して、吸引水流生起管を回転可能に設け、被処理水のろ過処理を行いながら、該吸引水流生起管を回転させつつ吸引水流を起こし、ろ材充填層の表層面上のろ過物を排除し、排除したろ過物を含む洗浄排水を排出することを特徴とする懸濁水のろ過方法。
(2)ろ過装置内に、ろ材充填層を設け、該充填層表層面に近接して、吸引口を有する吸引水流生起管を回転可能に設け、被処理水のろ過処理を行いながら、該吸引水流生起管を回転させつつ吸引水流を起こし、該吸引口から該充填層表層面上の濾過物を含む洗浄排水を排出することを特徴とする懸濁水のろ過装置。
(3)前記吸引水流生起管の回転速度を可変としたことを特徴とする前記(2)のろ過装置。
(4)前記ろ材が浮上性ろ材であることを特徴とする前記(2)又は(3)のろ過装置。
【0008】
【発明の実施の形態】
図1は、本発明の高速ろ過装置の一実施態様を示す構成図である。図中、1はろ過装置、2は原水、3は原水流入部、4はろ材充填層、5はろ過水、6はろ過水流出部、7は吸引水流生起管、8はスリット、9はモータ、10は吸引ポンプ、12及び14は網である。
図1に示す本発明の高速ろ過装置は、下部に原水流入部を備え、上部にろ過水流出部を備えたろ過塔の内部に、たとえば比重が1に近い(自力で浮上するか、又は上向水流によって上方に押し上げられる比重が0.9〜1.1程度が好適)プラスチック(ポリプロピレンなど)粒状物を充填する。粒状物の形状は任意であり、小板、星型粒、中空筒などが、充填空隙率が大きくなるので好適である。ろ材粒径は5〜20mm程度が適している。充填層厚は1〜2m程度が好適である。
【0009】
この充填層に対して、原水又は原水に凝集剤(高分子凝集剤単独又は無機凝集剤と高分子凝集剤の併用)を添加したものを、上向流又は下向流で流通させ、原水中の懸濁粒子を充填材の空隙に捕捉させてろ過除去する。図1に示した例は上向流ろ過の場合である。本発明では下向きろ過で行うこともできる。
従来のろ過装置では、このような充填層に原水を通水する運転を続けると、充填層の表層部Aに最もSSが捕捉されるので、表層部Aから目詰まりが進み、その後徐々に充填層全体にSS捕捉が進み、最終的にSS捕捉容量が限界に達し、処理水のSSが急増するか又はろ過抵抗が所定値に達する。この時点で原水流入を止め、ろ材を洗浄するようにしていた。
【0010】
これに対し本発明は、充填層の表層部Aの水平面に近接して、槽の半径方向に吸引口を有する吸引水流生起管(単に「吸引水流管」ともいう)を回転可能に設ける。吸引水流生起管は充填層に近接する部分に設けられて、吸引ポンプによって、流速が数m/秒の吸引水流が吸引口に生起する。吸引口の形状としては種々の形状を取ることができるが、表層部に広く接することができる点から、スリット部とすることが好ましい。
スリット幅は、ろ材粒径より小さくし、ろ材が吸引管内に流入しないようにする。スリットに網を張る方法もあるが、網が目詰まりしやすいのであまり推奨できない。スリットに代えて多孔状パイプにしても良い。スリットの長さは、吸引水流生起管を充填層の中心に設けた場合、充填層の直径あるいは半径とすることが好適である。
吸引水流生起管は、モータによって回転可能で、回転数は可変とする。回転数は数〜数十RPMが適当である。
【0011】
このような本発明のろ過装置の、上向流ろ過の場合の運転態様を説明する。
原水2は上向流でろ過装置1に流入する。原水SSは主としてろ材充填層4の下部の表層部Aに捕捉され、表層部AのSS捕捉量が増加し、ろ過抵抗が増加する。しかし、原水2のろ過処理を行いながら、間歇的に吸引ポンプ10を稼動すると、吸引水流生起管7のスリット8に強い吸引水流が起きる。
【0012】
この結果、充填層4の表層部のろ材は比重が小さいので容易に下方に引かれて展開し、充填層4に捕捉されていたSSも同時に吸引され、前記スリット8から吸引水流生起管7に吸引され、そのパイプ内を経由して、表層部洗浄排水11が槽外に排出される。吸引ポンプ10の運転は、間歇的に行うのが通常であるが、常時運転しても良い。
このようなメカニズムによって、本発明では、ろ過工程中に、表層部Aに捕捉されたSSの大部分が系外に排出され、表層部AのSS捕捉量がほとんど増加しないので、表層部Aのろ過抵抗の上昇が非常に少なくなる。この結果、充填層全体のろ過抵抗の上昇が少なくなり、大きなろ過速度、高い原水SS濃度でも、長時問のろ過が行える。
【0013】
しかし、長時間ろ過を続けると、表層部より高い位置(深い位置)のSS捕捉量が増加するため、ろ過抵抗が徐々に増加し、所定値に達するので、この時点で原水の流入を止め、ろ過を中止し、充填層全体を洗浄する。
充填層4全体のろ材洗浄は、たとえば次のように行う。すなわち、散気部材、例えば散気装置13から空気17を数分問散気しながら、吸引水流管7を数十RPMで回転させると吸引水流管7が攪拌翼の作用を示し、ろ材を強くかく乱するので、ろ材に付着している濁質が剥離する。その後、洗浄排水管16から槽内の水を急速に排出し、洗浄排水15として取り出す。この結果充填材に捕捉されていた濁質は排出され、充填層4は清浄になる。
以上のようなメカニズムでろ材充填層が簡単に洗浄されるので、再度原水を供給し上向流ろ過を開始する。
【0014】
【実施例】
以下に実施例を挙げて本発明を更に詳細に説明するが。本発明の範囲はこれらに限定されるものではない。
【0015】
実施例1(合流式下水道の雨天時越流水のろ過処理試験)
図1の本発明装置を使って、下水のろ過試験を行った。ろ過槽は内径30cmの円筒形容器に比重0.91のポリプロピレン製正方形ろ材(寸法4×4×2mm)を厚2mに充填した層(充填層空隙率94%)である。このろ過槽にSSが130mg/リットルである下水をろ過速度1440m/dで通水した。
吸引水流管は、パイプ径15mm、スリット長さ15cm、スリット幅1.8mmである。スリット部は充填層の下面から25mmの位置にあるように配置した。スリット部の吸引水流の流速は0.5m/秒とした。回転数は10rpmである。吸引水流は、槽外に設置した吸引ポンプを稼動することによって生起させた。原水のろ過をろ過速度1440m/dで行いながら、5分間隔で1分間吸引水流を発生させて表層部の洗浄を行った。
【0016】
このような運転を行った結果、2時問経過後においてもろ過抵抗は0.6m水頭であり、ろ過抵抗が2m水頭に上昇するまでの時問は、7時問25分後であった。ろ過水SSの平均値は26mg/リットルであった。
【0017】
比較例1
比較試験として、吸引水流生起管を使わずに、実施例1と同じろ材充填層で、通常の上向流ろ過を行った。
下水(SS130mg/リットル)にろ過速度1440m/dで上向流で通水した。この結果、運転開始後2時間までのろ過水SSの平均値は23mg/リットルである、2時問20分後にろ過抵抗が2m水頭に増加し、ろ過水SSが85mg/リットルに悪化した。
【0018】
【発明の効果】
本発明によれば、次のような効果が得られる。
(1)最も目詰まりの進行が速い充填層表層部を、原水のろ過処理を行いながら、効果的に洗浄できるので、充填層全体のろ過抵抗の増加率が従来装置よりも非常に少なくなり、「原水流入を止めて行う充填層全体の洗浄」の頻度が少なくなるので、ろ過装置の稼働率が大きく向上する。
(2)ろ過速度を非常に大きくとっても、ろ過抵抗の増加が少ないので、下水CSOのようなSSが多い原水を高速度でろ過できる。
【図面の簡単な説明】
【図1】本発明の高速ろ過装置の一実施態様を示す構成図である。
【符号の説明】
1 ろ過装置
2 原水
3 原水流入部
4 ろ材充填層
5 ろ過水
6 ろ過水流出部網
7 吸引水流生起管モータ
8 スリット
9 モータ
10 吸引ポンプ
11 表層部洗浄排水
12 網
13 散気装置
14 網
15 洗浄排水
16 洗浄排水管
17 空気
A 表層部
[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a method and an apparatus for high-speed filtration of suspended water (hereinafter also referred to as “raw water”) containing suspended particles such as sewage and industrial effluent, and relates to a technique capable of high-speed filtration of suspended particles in raw water with a low head loss. .
Further, the present invention is an innovation which is particularly suitable as a high-speed solid-liquid separation technology for rainwater overflow (abbreviated as CSO) of a combined sewer system containing organic suspended particles or sewage flowing into a sewage treatment facility. Technology.
[0002]
[Prior art]
Recently, the pollution load of public water bodies due to rainfall overflow (CSO) in a combined sewer has become a major problem. There is a long-awaited demand for a new technology that can separate solid-liquid CSOs with as compact equipment as possible.
Conventionally, as a technique for filtering and removing SS from a suspension, deep bed filtration using granular materials such as sand and anthracite as a filter material is known, but organic SS such as sewage is removed at a large filtration rate. Attempts to remove it were severely clogged and impractical.
[0003]
Filtration methods using various granular solids (eg, granular plastic) other than anthracite and sand as filter media are also being studied. However, if the filter media size is increased to reduce clogging, the SS removal rate will deteriorate. (Patent Documents 1 and 2). In particular, since organic SS contained in sewage and the like has a strong adhesive force, a technology capable of satisfying the conflicting demands of high sewage removal rate, low clogging, and small increase in filtration resistance for such sewage is practical. Had not been converted.
[0004]
[Patent Document 1]
JP-A-4-187294 [0005]
[Patent Document 2]
JP-A-4-363105
[Problems to be solved by the invention]
The present invention provides a new technology that enables high-speed filtration of suspended particles in various raw waters such as sewage by using a simple and compact device while significantly reducing the rise in the head loss.
[0007]
[Means for Solving the Problems]
The present invention has solved the above problems by the following means.
(1) A suction water flow generating tube is rotatably provided near the surface of the filter medium packed layer provided in the filtration device, and suction is performed while rotating the suction water flow generating tube while filtering the water to be treated. A method for filtering suspended water, comprising: causing a water flow to remove a filtrate on a surface layer of a filter medium-packed layer; and discharging washing wastewater containing the removed filtrate.
(2) A filter medium filling layer is provided in the filtration device, and a suction water flow generating pipe having a suction port is rotatably provided near the surface of the packing layer, and the suction is performed while performing the filtration of the water to be treated. A device for filtering suspended water, wherein a suction water flow is generated while rotating a water flow generating tube, and washing wastewater containing a filtrate on the surface of the packed bed is discharged from the suction port.
(3) The filtration device according to (2), wherein a rotation speed of the suction water flow generating tube is variable.
(4) The filtering device according to (2) or (3), wherein the filter medium is a floating filter medium.
[0008]
BEST MODE FOR CARRYING OUT THE INVENTION
FIG. 1 is a configuration diagram showing one embodiment of the high-speed filtration device of the present invention. In the figure, 1 is a filtration device, 2 is raw water, 3 is raw water inflow section, 4 is filter medium packed layer, 5 is filtered water, 6 is filtered water outflow section, 7 is suction water flow generating pipe, 8 is slit, and 9 is motor Reference numeral 10 is a suction pump, and 12 and 14 are nets.
The high-speed filtration device of the present invention shown in FIG. 1 has, for example, a specific gravity close to 1 (or floats on its own or rises above) inside a filtration tower provided with a raw water inflow portion at a lower portion and a filtered water outflow portion at an upper portion. The specific gravity pushed up by the countercurrent is preferably about 0.9 to 1.1.) Plastic (such as polypropylene) granules are filled. The shape of the granular material is arbitrary, and platelets, star-shaped particles, hollow cylinders, and the like are preferable because the filling porosity increases. A filter media particle size of about 5 to 20 mm is suitable. The thickness of the filling layer is preferably about 1 to 2 m.
[0009]
The raw water or raw water to which a flocculant (a polymer flocculant alone or a combination of an inorganic flocculant and a polymer flocculant) has been added is flown upward or downward in the raw water. Are trapped in the voids of the filler and removed by filtration. The example shown in FIG. 1 is for upflow filtration. In the present invention, the filtration can be performed by downward filtration.
In a conventional filtration device, if the operation of passing raw water through such a packed bed is continued, SS is most caught in the surface layer A of the packed bed. SS trapping progresses to the whole layer, and finally SS trapping capacity reaches the limit, SS of treated water increases rapidly or filtration resistance reaches a predetermined value. At this point, the inflow of raw water was stopped and the filter medium was washed.
[0010]
On the other hand, in the present invention, a suction water flow generating pipe (simply referred to as “suction water flow pipe”) having a suction port in the radial direction of the tank is rotatably provided near the horizontal plane of the surface layer portion A of the packed bed. The suction water flow generating pipe is provided at a portion close to the packed bed, and a suction pump generates a suction water flow having a flow velocity of several meters / second at the suction port. The shape of the suction port can take various shapes, but is preferably a slit portion because it can widely contact the surface layer portion.
The slit width is made smaller than the filter medium particle size so that the filter medium does not flow into the suction pipe. There is a method of setting a net in the slit, but it is not recommended because the net is easily clogged. A porous pipe may be used instead of the slit. When the suction water flow generating tube is provided at the center of the packed bed, the length of the slit is preferably the diameter or radius of the packed bed.
The suction water flow generating tube can be rotated by a motor, and the rotation speed is variable. An appropriate rotation speed is several to several tens of RPM.
[0011]
An operation mode of such a filtration device of the present invention in the case of upward flow filtration will be described.
The raw water 2 flows into the filtration device 1 in an upward flow. The raw water SS is mainly captured in the surface layer portion A below the filter medium packed layer 4, and the amount of trapped SS in the surface layer portion A increases, and the filtration resistance increases. However, if the suction pump 10 is operated intermittently while the raw water 2 is being filtered, a strong suction water flow is generated in the slit 8 of the suction water flow generation pipe 7.
[0012]
As a result, the filter medium at the surface layer portion of the packed bed 4 has a small specific gravity, so it is easily pulled downward and developed, and the SS trapped in the packed bed 4 is also sucked at the same time. The water is sucked, and the surface washing water 11 is discharged out of the tank via the pipe. The operation of the suction pump 10 is usually performed intermittently, but may be always performed.
By such a mechanism, in the present invention, most of the SS trapped in the surface layer A is discharged out of the system during the filtration step, and the amount of SS trapped in the surface layer A hardly increases. The rise in filtration resistance is very small. As a result, the increase in filtration resistance of the entire packed bed is reduced, and long-time filtration can be performed even at a high filtration rate and a high raw water SS concentration.
[0013]
However, if filtration is continued for a long time, the amount of trapped SS at a higher position (deeper position) than the surface layer increases, so that the filtration resistance gradually increases and reaches a predetermined value. Stop the filtration and wash the entire packed bed.
The filter medium washing of the entire packed bed 4 is performed, for example, as follows. That is, when the suction water flow pipe 7 is rotated at several tens of RPM while diffusing the air 17 from the air diffusion member, for example, the air diffusion device 13 for several minutes, the suction water flow pipe 7 shows an action of a stirring blade, and the filter medium is strongly strengthened. Because of the disturbance, the turbidity adhering to the filter medium is peeled off. Thereafter, the water in the tank is quickly drained from the washing drainage pipe 16 and taken out as the washing drainage 15. As a result, the suspended matter trapped in the filler is discharged, and the packed layer 4 is cleaned.
Since the filter medium packed bed is easily washed by the mechanism as described above, the raw water is supplied again and the upward flow filtration is started.
[0014]
【Example】
Hereinafter, the present invention will be described in more detail with reference to Examples. The scope of the present invention is not limited to these.
[0015]
Example 1 (Filtration test of combined sewage sewer stormwater overflow)
A sewage filtration test was performed using the apparatus of the present invention shown in FIG. The filtration tank is a layer (filled layer porosity of 94%) in which a cylindrical container having an inner diameter of 30 cm is filled with a polypropylene square filter medium (size: 4 × 4 × 2 mm) having a specific gravity of 0.91 to a thickness of 2 m. Sewage having an SS of 130 mg / liter was passed through the filtration tank at a filtration speed of 1440 m / d.
The suction water flow pipe has a pipe diameter of 15 mm, a slit length of 15 cm, and a slit width of 1.8 mm. The slit portion was arranged so as to be located 25 mm from the lower surface of the filling layer. The flow rate of the suction water flow at the slit was 0.5 m / sec. The rotation speed is 10 rpm. The suction water flow was generated by operating a suction pump installed outside the tank. While filtering the raw water at a filtration speed of 1440 m / d, a suction water flow was generated at intervals of 5 minutes for 1 minute to wash the surface layer portion.
[0016]
As a result of performing such an operation, the filtration resistance was 0.6 m head even after the elapse of 2:00, and the time required for the filtration resistance to rise to the 2 m head was 7:00 and 25 minutes later. The average value of the filtered water SS was 26 mg / liter.
[0017]
Comparative Example 1
As a comparative test, ordinary upward flow filtration was performed using the same filter medium packed bed as in Example 1 without using a suction water flow generating tube.
Water was passed through the sewage (130 mg / liter) in an upward flow at a filtration speed of 1440 m / d. As a result, the average value of the filtered water SS up to 2 hours after the start of the operation was 23 mg / liter, and the filtration resistance increased to 2 m head after 2 hours and 20 minutes, and the filtered water SS deteriorated to 85 mg / liter.
[0018]
【The invention's effect】
According to the present invention, the following effects can be obtained.
(1) Since the surface layer portion of the packed bed where clogging progresses fastest can be effectively washed while filtering the raw water, the rate of increase of the filtration resistance of the entire packed bed is much smaller than that of the conventional apparatus. Since the frequency of “washing the entire packed bed by stopping the inflow of raw water” is reduced, the operation rate of the filtration device is greatly improved.
(2) Even if the filtration speed is very high, the increase in filtration resistance is small, so that raw water having a large amount of SS such as sewage CSO can be filtered at a high speed.
[Brief description of the drawings]
FIG. 1 is a configuration diagram showing one embodiment of a high-speed filtration device of the present invention.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Filtration apparatus 2 Raw water 3 Raw water inflow part 4 Filter material packed bed 5 Filtration water 6 Filtration water outflow part network 7 Suction water flow generating tube motor 8 Slit 9 Motor 10 Suction pump 11 Surface part washing drainage 12 Net 13 Air diffuser 14 Net 15 Cleaning Drainage 16 Cleaning drainage pipe 17 Air A Surface layer

Claims (4)

ろ過装置内に設けたろ材充填層の表層面に近接して、吸引水流生起管を回転可能に設け、被処理水のろ過処理を行いながら、該吸引水流生起管を回転させつつ吸引水流を起こし、ろ材充填層の表層面上のろ過物を排除し、排除したろ過物を含む洗浄排水を排出することを特徴とする懸濁水のろ過方法。A suction water flow generating pipe is rotatably provided in the vicinity of the surface of the filter medium packed layer provided in the filtration device, and a suction water flow is generated while rotating the suction water flow generating pipe while filtering the water to be treated. A method of filtering suspended water, comprising: removing a filtrate on the surface of the filter medium-filled layer; and discharging washing wastewater containing the removed filtrate. ろ過装置内に、ろ材充填層を設け、該充填層表層面に近接して、吸引口を有する吸引水流生起管を回転可能に設け、被処理水のろ過処理を行いながら、該吸引水流生起管を回転させつつ吸引水流を起こし、該吸引口から該充填層表層面上の濾過物を含む洗浄排水を排出することを特徴とする懸濁水のろ過装置。In the filtration device, a filter medium-filled layer is provided, and a suction water flow generating pipe having a suction port is rotatably provided near the surface of the packed layer, and the suction water flow generating pipe is provided while performing a filtration treatment of the water to be treated. A suspension water filtration device characterized by causing a suction water flow while rotating the water, and discharging washing wastewater containing a filtrate on the surface of the packed layer from the suction port. 前記吸引水流生起管の回転速度を可変としたことを特徴とする請求項2のろ過装置。3. The filtering device according to claim 2, wherein a rotation speed of the suction water flow generating tube is variable. 前記ろ材が浮上性ろ材であることを特徴とする請求項2又は請求項3のろ過装置。The filtering device according to claim 2 or 3, wherein the filter medium is a floating filter medium.
JP2002294922A 2002-10-08 2002-10-08 Method and apparatus for filtering aqueous suspension Pending JP2004130164A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100978070B1 (en) 2010-06-18 2010-08-26 미라클워터 주식회사 Filtraion apparatus having ss filtering type and backwash-water discharge type
KR100978071B1 (en) 2010-06-18 2010-08-26 미라클워터 주식회사 Filtraion apparatus having ss filtering type and backwash-water discharge type

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100978070B1 (en) 2010-06-18 2010-08-26 미라클워터 주식회사 Filtraion apparatus having ss filtering type and backwash-water discharge type
KR100978071B1 (en) 2010-06-18 2010-08-26 미라클워터 주식회사 Filtraion apparatus having ss filtering type and backwash-water discharge type

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