JP3790857B2 - Filtration apparatus and filtration method using floating filter medium - Google Patents

Filtration apparatus and filtration method using floating filter medium Download PDF

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Publication number
JP3790857B2
JP3790857B2 JP2002159203A JP2002159203A JP3790857B2 JP 3790857 B2 JP3790857 B2 JP 3790857B2 JP 2002159203 A JP2002159203 A JP 2002159203A JP 2002159203 A JP2002159203 A JP 2002159203A JP 3790857 B2 JP3790857 B2 JP 3790857B2
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Prior art keywords
filter medium
filtration
floating
floating filter
flow rate
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JP2002159203A
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JP2004000831A (en
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克之 片岡
和彰 島村
俊博 田中
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Ebara Corp
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Ebara Corp
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Description

【0001】
【発明の属する技術分野】
本発明は、工場排水、下水など懸濁粒子、リン酸イオン、フッ素イオン、金属イオン、色度成分、COD成分などの除去対象物質を含有する水(本明細書ではこれを「原水」という)のろ過装置及びろ過方法に関する。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と略称される)、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連続的に実施できる好適な技術である。
【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。合流式下水道の雨天時越流水(CSO)は、短時間に膨大な水量が発生するため、非常にコンパクトな装置でCSOの汚濁物質を除去できる装置が切望されている。
【0003】
また下水処理施設に流入する下水は、まず最初沈殿池で沈殿分離されたのち、活性汚泥処理されるが、最初沈殿池のSSの除去率が悪いため、凝集剤を添加して凝集沈殿処理する例が北欧で普及している。しかし、凝集沈殿速度が小さく、大きな沈殿池を必要とする欠点がある。そのためCSOおよび下水を高速度で固液分離できる新技術が待望されている。
【0004】
先行技術の「浮上ろ材を用いた連続ろ過機におけるろ材の洗浄装置」には、図2に示すように、浮上ろ材22を充填したろ過槽21の下部に、ろ材と汚水との分離槽31を設け、そのろ過槽21との連通部を開閉自在にするとともに、一方、ろ過槽21の頂部と前記分離槽31との間にろ材の洗浄管29を形成して、この洗浄管29を開閉自在とし、さらに、前記分離槽31には、汚水の引き抜きポンプ33を設けてなる、浮上ろ材を用いたろ過機におけるろ材の洗浄装置が記載されている。
【0005】
【発明が解決しようとする課題】
しかし、この従来技術の追試を行った結果、次の欠点があった。
1)間欠的にろ材を洗浄するので連続ろ過が行えない。
2)多数のバルブ(30,32,34など)が必要で、バルブの開閉操作が煩雑である。バルブ開閉制御設備も必要である。
3)最上部がコーン状になっていないため、浮上ろ材は装置上部のカバーに浮力で強く押し付けられ、固定層状態になっているので、浮上ろ材を管路29で非常に吸引しにくく、水だけが吸い込まれてしまう。
4)ろ過装置の下部に、2重コーン状の複雑な形の分離槽31を設けなけれぱならないので、装置製作が面倒で、制作費も高い。
【0006】
本発明は、非常に簡単な構成の装置によって、上記従来技術を改善したもので、河川水、湖沼水、排水、下水など各種原水中の懸濁粒子、リン酸イオン、フッ素イオン、金属イオン、色度成分、COD成分などの除去対象物質を高速度でろ過分離できる技術を提供することを課題とする。
【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することができた。
(1)上部の浮上ろ材の流動部を形成するテーパ部と、前記流動部の下部に続く浮上ろ材の充填層からなるろ過層を形成する直胴部を有する槽からなり、前記テーパ部の頂部に配備した原水流入部と、テーパ部の浮上ろ材流動部から浮上ろ材を吸引するろ材吸引管、前記吸引管から吸引ポンプを経由して送られた浮上ろ材を導入する、前記ろ過層の下方に配設した上部開口のろ材洗浄チャンバと、前記槽の底部に配備したろ過水排出部、及び前記ろ材洗浄チャンバの下部に設置した洗浄排水排出管を有することを特徴とする浮上ろ材を用いたろ過装置。
(2)原水流量をQ、ろ材吸引水量をQ1、洗浄排水排出流量をQ2とするとき、Q1<Q2<<Qに設定したことを特徴とする前記(1)記載のろ過装置。
【0008】
(3)上部のテーパ部に浮上ろ材の流動部を形成し、前記流動部の下方に続いて浮上ろ材の充填層からなるろ過部が形成されたろ過槽のテーパ部の頂部から原水を導入して、前記流動部及びろ過部をへて下方に流下させ、テーパ部の中間位置から浮上ろ材を吸引して外部に取り出し、取り出した浮上ろ材をろ過部の下方に設けた上方開口のろ材洗浄チャンバへ導入して洗浄後、ろ過部下方に浮上させ、ろ材洗浄チャンバから洗浄排水を排出させ、ろ過槽下部から処理水を取り出し、原水流量をQ、ろ材吸引水流量をQ1、洗浄排水排出流量をQ2とするとき、Q1<Q2<<Qに設定したことを特徴とするろ過方法。
【0009】
【発明の実施の形態】
以下に、本発明を図面に基づいて詳細に説明する。
図1は、本発明の連続ろ過装置主要部の一実施態様を示す図である。
本発明装置の主要構造を説明する。
ろ過装置1は中央部が円筒状で直胴部3を形成しており、上部がテーパ状(コーン状)でテーパ部2を形成している。テーパ部2の頂部に原水流入部8が接続されており、そこから原水7が入って下方に流下するようになっている。
【0010】
ろ過装置内1には、ろ材として比重が水より小さい浮上性粒子(発泡プラスチック粒子など)4が充填されている。テーパ部2においては原水の下降流速が大きく、それも頂部に近いほど流速が大きいため浮上ろ材4が流動化しており、流動部5を形成する。
その下部の槽直胴部3は原水の下降流速がテーパ部2より小さいため、浮上ろ材4が、固定層に近い状態の充填層6を構成している。これがろ過層6を形成している(これは、状態をいうときには「充填層」といい、作用の点でいうときには「ろ過層」という)。ただ、その流動部に接している部分では流動化している原水の力で膨張率が小さい膨張層を形成する場合がある。ろ過層6の下方には、ろ過水流出部15が設置されている。
【0011】
テーパ部2に、ろ材吸引管9が設置され、ポンプ機構10と接続されている。なお、ろ材吸引管9の開口は図1に示すように流動部5の中心近くに設けることができる。ポンプ機構10に接続するろ材移送管11は、浮上ろ材充填層6の下のろ材洗浄チャンバ12に接続されている。このチャンバ12は上部が開口し、下部に洗浄排水管13が取り付けられている。ろ材移送管11からチャンバ12内に送り込まれた浮上ろ材4は比重が小さいためにその上部開口からろ過槽内を上昇して浮上ろ材充填層6の下に供給される。
排水管13には排水ポンプ14が接続されている。
以上が本発明連続ろ過装置1の骨子構成である。
【0012】
次に作用原理を説明する。
処理対象原水7が、本発明ろ過装置1の上部のテーパ部2に流入する。
装置の直胴部3における原水7の下降流速は、浮上ろ材4の浮上速度よりも小さくし、浮上ろ材4の充填層(膨張層もしくは固定層)6が形成されるように設定する。直胴部3におけるろ過層6の充填高さは、通常1〜2m程度で充分である。
【0013】
原水7が、流動部5を経由したのち、浮上ろ材充填層(ろ過層)6を下降流で流過し、その際懸濁粒子がろ過除去されて、清澄なろ過水16がろ過層6下部から流出する。
なお、原水7に凝集剤17を添加する場合もある。この場合は、凝集フロックがろ過除去される。
【0014】
しかして、テーパ部2に接続されたろ材吸引管9から任意のポンプ機構10によって浮上ろ材4を吸引し、ろ材移送管11を経てろ過層6下方のろ材洗浄チャンバ12に導入する。
ろ材吸引管9の上端は、装置直胴部3の充填層部(浮上粒子が膨張層又は固定層を形成している部分)に位置するのではなく、テーパ部2内に位置することが重要である。なぜなら、テーパ部2では原水の下降流速が浮上性粒子(浮上ろ材)4の浮上速度よりも大きいために浮上性粒子4が流動しているので、浮上性粒子4をろ材吸引管路9内に容易に吸引出来るからである。
【0015】
ろ材吸引管9から入った後、浮上性粒子4に付着したSSは、ポンプ10などのせん断力によって剥離する。チャンバ12に吐き出された浮上性粒子4とSS分のうち、浮上性粒子4はチャンバ12の上部開口部から上方に浮上してゆき、ろ材充填層6の下界面に達して停止する。その際、後述する洗浄排水管13から排水に伴ってろ過層6から流下するろ過水の一部がチャンバ12の上部に入り、丁度浮上する浮上性粒子4と向流する状態となり、浮上性粒子4がろ過水で洗浄される作用が得られる。そして、チャンバ12内に入ったSS分はチャンバ12の底部に沈殿するか浮遊状態にある。
チャンバ12の底部付近に設けた洗浄排水管13から水を系外に排出すると、ろ過水16の一部がチャンバ12内に流入するので、浮上ろ材4から剥離したSSは系外に排出する水に随伴されて効果的に系外に排出される。この排出された水を洗浄排水という。したがって、剥離SSがろ過水16に混入してろ過水SSを増加させるようなトラブルが起きない。洗浄排水の排出は連続的に行なっても、また間欠的に行なってもかまわない。
【0016】
この場合、ろ材吸引水量をQ1、洗浄排水流量をQ2とするとき、Q2>Q1に設定すると、確実に剥離SSを系外に排除できる。特に、原水流量をQとするとき、Q1<Q2<<Qに設定したとき、一層確実に剥離SSを系外に排除することができる。なお、Q1は5〜6m/min以下が好ましい。
このようなメカニズムで、浮上ろ材ろ過層6を構成する浮上ろ材4がろ過層6の上面から下面に循環するので、充填層全体が、下から上へ徐々に移動する状態となる。
【0017】
したがって、浮上ろ材充填層は移動層となり、移動層によるろ過処理が、簡単な構成できわめて合理的に実現される。したがって、ろ過層上部でろ材に捕捉されたSSは、ろ材吸引管路を経由して、浮上ろ材から剥離されて洗浄排水で系外に排出され、また浮上ろ材は洗浄されたのち、洗浄粒子が再びろ過層を形成するため、ろ過層が絶えず更新されたものとなるので、ろ過抵抗が大きく増加することなく、一定のろ過抵抗を維持しながら、連続ろ過が行える。
【0018】
本発明の連続ろ過に適用するために最適な浮上性粒子4を種々検討した結果、浮上性粒子4の比重として極力小さいものを使用することが、大きなろ過速度を得るために重要で、比重が0.2以下のものが適していることが判明した。特に発泡スチロールなどの発泡プラスチック微粒子、中でも発泡スチロールは比重が極めて小さくでき、極めて浮上力が大きいこと、低価格で、入手も容易であるので最適である。
【0019】
浮上ろ材4の粒径も重要因子であり、過度に大きいとSSがリークされやすく、一方、過度に小さいとろ過抵抗が大きくなるので、粒径0.5〜5mm程度が好ましい。
ろ過層の下から上への最適移動速度は、諸条件で大きく変るため一概には言えないが、原則として、原水SSが多い場合は、浮上ろ材4の下降流生起管路への吸引量Q1を多くし、原水SSが少ない場合は、吸引量Q1を少なくする。原水SSが多いときには、原水を最初にろ過するろ過層の上面が早く詰まるので、その上面部分の浮上ろ材4を早く更新する必要があるからである。
【0020】
【発明の効果】
本発明によれば、以下の効果が得られる。
1)従来技術のような多数のバルブが一切不要で、かつ非常にシンプルな装置形状、構成によって、ろ過層を移動層にしながら高ろ過速度の連続ろ過が行える。
2)合流式下水道の雨天時越流水(CSO)のように、短時間に膨大な水量が発生する原水に極めて好適であり、非常にコンパクトな装置で、必ずしも凝集剤を使用しなくても懸濁粒子を効果的に除去できる。
【図面の簡単な説明】
【図1】本発明の浮上ろ材を用いたろ過装置の一実施例を示す構成概略説明図である。
【図2】従来の浮上ろ材を用いた連続ろ過機の一例の構成概略説明図である。
【符号の説明】
1 ろ過装置
2 テーパ(コーン)部
3 直胴部
4 浮上ろ材
5 ろ材流動部
6 分離槽
7 原水
8 原水流入部
9 ろ材吸引管
10 引抜きポンプ
11 ろ材移送管
12 ろ材洗浄チャンバ
13 洗浄排水管
14 ポンプ
15 ろ過水流出部
16 ろ過水
17 凝集剤
21 ろ過槽
22 浮上ろ材
23 ろ過層
24 原水
25 原水供給管
26 噴水口
27 ろ過水
28 浮上ろ材(浮上性粒子)
29 洗浄管
29a 洗浄室
30 バルブ
31 分離槽
32 バルブ
33 ポンプ
34 バルブ
35 洗浄排水
Q 原水流量
1 ろ材吸引水流量
2 洗浄排水排出流量
[0001]
BACKGROUND OF THE INVENTION
In the present invention, water containing substances to be removed such as suspended particles such as industrial waste water and sewage, phosphate ions, fluorine ions, metal ions, chromaticity components, and COD components (this is referred to as “raw water” in this specification). The present invention relates to a filtration device and a filtration method. INDUSTRIAL APPLICABILITY The present invention can be continuously implemented as a high-speed solid-liquid separation technology for sewage that flows into a sewage treatment facility, particularly, rainwater overflow (abbreviated as CSO) in a combined sewer that contains organic suspended particles. This is a preferred technique.
[0002]
[Prior art]
Recently, the pollution load on the public water area of rainwater overflow (CSO) in the combined sewer has become a big problem. Since rainwater overflow (CSO) in a combined sewer generates a huge amount of water in a short time, a device that can remove CSO contaminants with a very compact device is eagerly desired.
[0003]
In addition, the sewage flowing into the sewage treatment facility is first precipitated and separated in the settling basin and then treated with activated sludge. However, since the SS removal rate of the first settling basin is poor, a coagulant is added to perform coagulation sedimentation treatment. Examples are prevalent in Scandinavia. However, there is a drawback that the coagulation sedimentation rate is small and a large sedimentation basin is required. Therefore, a new technology capable of solid-liquid separation of CSO and sewage at high speed is desired.
[0004]
As shown in FIG. 2, in the prior art “filtering device for filter media in a continuous filter using floating filter medium”, a separation tank 31 for separating the filter medium and sewage is provided below the filter tank 21 filled with the floating filter medium 22. Provided, and the communication portion with the filtration tank 21 can be freely opened and closed. On the other hand, a filter cleaning pipe 29 is formed between the top of the filtration tank 21 and the separation tank 31, and the cleaning pipe 29 can be opened and closed. In addition, the separation tank 31 is provided with a filter medium cleaning device in a filter using a floating filter medium, which is provided with a sewage extraction pump 33.
[0005]
[Problems to be solved by the invention]
However, as a result of conducting an additional test of this prior art, there were the following drawbacks.
1) Since the filter medium is washed intermittently, continuous filtration cannot be performed.
2) A large number of valves (30, 32, 34, etc.) are required, and the opening and closing operation of the valves is complicated. Valve opening / closing control equipment is also required.
3) Since the uppermost part is not cone-shaped, the floating filter medium is strongly pressed against the cover at the top of the apparatus by a buoyant force and is in a fixed layer state. Only will be inhaled.
4) Since a complicated separation tank 31 having a double cone shape must be provided at the lower part of the filtration device, the device production is troublesome and the production cost is high.
[0006]
The present invention is an improvement of the above-described prior art by a device with a very simple configuration, and suspended particles in various raw water such as river water, lake water, drainage, sewage, phosphate ions, fluorine ions, metal ions, It is an object of the present invention to provide a technology capable of filtering and separating substances to be removed such as chromaticity components and COD components at high speed.
[0007]
[Means for Solving the Problems]
The present invention has solved the above-described problems by the following means.
(1) It comprises a tank having a taper part that forms a fluidized part of the upper floating filter medium and a straight body part that forms a filtration layer comprising a packed bed of the floated filter medium following the lower part of the fluidized part, and the top part of the taper part The raw water inflow section arranged in the filter section, a filter medium suction pipe for sucking the floating filter medium from the floating filter medium flow section of the tapered section, and a floating filter medium sent from the suction pipe via a suction pump are introduced below the filtration layer. Filtration using a floating filter medium, characterized by having a filter medium cleaning chamber with an upper opening disposed, a filtrate drainage provided at the bottom of the tank, and a cleaning drainage pipe installed at the bottom of the filter medium cleaning chamber apparatus.
(2) the raw water flow rate Q, Q 1 a filter material suction water, when the washing waste water discharge flow rate Q 2, above, wherein the set to Q 1 <Q 2 << Q ( 1) filtration device as claimed .
[0008]
(3) A floating portion of the floating filter medium is formed in the upper tapered portion, and raw water is introduced from the top of the tapered portion of the filtration tank in which a filtration portion composed of a packed bed of the floating filter material is formed below the flowing portion. Then, the flow part and the filtration part are allowed to flow downward, the floating filter medium is sucked out from the intermediate position of the taper part and taken out to the outside, and the filtered medium washing chamber having an upper opening provided with the removed floating filter medium below the filtration part After washing and floating to the bottom of the filtration unit, the washing waste water is discharged from the filter material washing chamber, the treated water is taken out from the lower part of the filtration tank, the raw water flow rate is Q, the filter material suction water flow rate is Q 1 , and the washing waste water discharge flow rate. when to the Q 2, filtration wherein the set to Q 1 <Q 2 << Q.
[0009]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, the present invention will be described in detail with reference to the drawings.
FIG. 1 is a diagram showing an embodiment of the main part of the continuous filtration device of the present invention.
The main structure of the device of the present invention will be described.
The filtering device 1 has a cylindrical shape with a central portion forming a straight body portion 3, and an upper portion with a tapered shape (conical shape) to form a tapered portion 2. A raw water inflow portion 8 is connected to the top of the taper portion 2, and raw water 7 enters from there and flows downward.
[0010]
The filtration apparatus 1 is filled with floating particles (foamed plastic particles or the like) 4 having a specific gravity smaller than that of water as a filter medium. In the taper part 2, the descending flow rate of the raw water is large, and the flow rate is larger as it is closer to the top part. Therefore, the floating filter medium 4 is fluidized to form the fluidized part 5.
Since the lower tank straight body portion 3 has a lower flow rate of the raw water than the tapered portion 2, the floating filter medium 4 constitutes the packed bed 6 in a state close to the fixed bed. This forms the filtration layer 6 (this is referred to as a “filled layer” when referring to a state, and is referred to as a “filtration layer” when referred to in terms of action). However, in the portion in contact with the fluidized portion, an expanded layer having a small expansion rate may be formed by the force of the raw water fluidized. A filtered water outflow portion 15 is installed below the filtration layer 6.
[0011]
A filter medium suction pipe 9 is installed in the tapered portion 2 and connected to the pump mechanism 10. In addition, the opening of the filter medium suction pipe 9 can be provided near the center of the fluidized part 5 as shown in FIG. A filter medium transfer pipe 11 connected to the pump mechanism 10 is connected to a filter medium cleaning chamber 12 below the floating filter medium packed bed 6. The chamber 12 is open at the top and a cleaning drain pipe 13 is attached to the bottom. Since the floating filter medium 4 fed into the chamber 12 from the filter medium transfer pipe 11 has a small specific gravity, it rises in the filter tank from its upper opening and is supplied under the floating filter medium packed bed 6.
A drain pump 14 is connected to the drain pipe 13.
The above is the basic configuration of the continuous filtration device 1 of the present invention.
[0012]
Next, the principle of operation will be described.
The raw water 7 to be treated flows into the upper tapered portion 2 of the filtration device 1 of the present invention.
The descending flow rate of the raw water 7 in the straight body part 3 of the apparatus is set to be smaller than the rising speed of the floating filter medium 4 so that a packed layer (expanded layer or fixed layer) 6 of the floating filter medium 4 is formed. The filling height of the filtration layer 6 in the straight body part 3 is usually about 1 to 2 m.
[0013]
After the raw water 7 passes through the fluidized part 5, it flows through the floating filter medium packed bed (filtered layer) 6 in a downward flow. At that time, suspended particles are filtered and removed, and the clear filtered water 16 becomes the lower part of the filtered layer 6. Spill from.
Note that the flocculant 17 may be added to the raw water 7. In this case, the aggregated floc is removed by filtration.
[0014]
Thus, the floating filter medium 4 is sucked from the filter medium suction pipe 9 connected to the taper portion 2 by an arbitrary pump mechanism 10 and introduced into the filter medium cleaning chamber 12 below the filter layer 6 through the filter medium transfer pipe 11.
It is important that the upper end of the filter medium suction pipe 9 is positioned not in the packed layer portion (portion where the floating particles form the expanded layer or the fixed layer) of the apparatus body 3 but in the tapered portion 2. It is. This is because the buoyant particles 4 flow because the descending flow rate of the raw water is higher than the levitating speed of the levitating particles (floating filter material) 4 in the taper portion 2. This is because it can be sucked easily.
[0015]
After entering from the filter medium suction tube 9, the SS attached to the floating particles 4 is peeled off by a shearing force of the pump 10 or the like. Of the levitating particles 4 and SS discharged into the chamber 12, the levitating particles 4 rise upward from the upper opening of the chamber 12, reach the lower interface of the filter medium packed layer 6 and stop. At that time, a part of the filtered water flowing down from the filtration layer 6 along with drainage from a washing drain pipe 13 to be described later enters the upper portion of the chamber 12 and becomes counterflowing with the levitation particles 4 that just float up. 4 is washed with filtered water. Then, the SS component that has entered the chamber 12 settles at the bottom of the chamber 12 or is in a floating state.
When water is discharged out of the system from the washing drain pipe 13 provided near the bottom of the chamber 12, a part of the filtered water 16 flows into the chamber 12, so the SS separated from the floating filter medium 4 is discharged out of the system. Is effectively discharged outside the system. This discharged water is called washing waste water. Therefore, the trouble that exfoliation SS mixes with filtrate 16 and filtrate water SS increases does not occur. The drainage of the cleaning wastewater may be performed continuously or intermittently.
[0016]
In this case, when the filter medium suction water amount is Q 1 and the washing drainage flow rate is Q 2 , the separation SS can be surely excluded from the system by setting Q 2 > Q 1 . In particular, when the raw water flow rate is Q, and when Q 1 << Q 2 << Q is set, the separation SS can be more reliably excluded from the system. Q 1 is preferably 5 to 6 m / min or less.
With such a mechanism, the floating filter medium 4 constituting the floating filter medium filtration layer 6 circulates from the upper surface to the lower surface of the filtration layer 6, so that the entire packed bed gradually moves from the bottom to the top.
[0017]
Therefore, the floating filter medium packed bed becomes a moving bed, and the filtration treatment by the moving bed can be realized extremely simply with a simple configuration. Therefore, the SS trapped by the filter medium at the upper part of the filtration layer is separated from the floating filter medium via the filter medium suction pipe and discharged out of the system by washing wastewater. Since the filtration layer is formed again, the filtration layer is constantly renewed, so that continuous filtration can be performed while maintaining a constant filtration resistance without greatly increasing the filtration resistance.
[0018]
As a result of various investigations on the optimum floating particles 4 to be applied to the continuous filtration of the present invention, it is important to use the one having the smallest possible specific gravity of the floating particles 4 in order to obtain a large filtration rate. A value of 0.2 or less was found to be suitable. In particular, expanded plastic fine particles such as expanded polystyrene, especially expanded polystyrene, can be extremely small in specific gravity, have extremely high levitation force, are inexpensive and are easily available, and are optimal.
[0019]
The particle size of the floating filter medium 4 is also an important factor. If the particle size is excessively large, SS is likely to leak. On the other hand, if the particle size is excessively small, the filtration resistance increases, so a particle size of about 0.5 to 5 mm is preferable.
The optimum moving speed from the bottom to the top of the filtration layer varies greatly depending on various conditions. However, in principle, when the raw water SS is large, the suction amount Q of the floating filter medium 4 to the downflow generation conduit is Q. increasing the 1, when the raw water SS is small, reducing the suction amount Q 1. This is because when the amount of the raw water SS is large, the upper surface of the filtration layer that first filters the raw water is clogged quickly, so that the floating filter medium 4 on the upper surface portion needs to be updated quickly.
[0020]
【The invention's effect】
According to the present invention, the following effects can be obtained.
1) A large number of valves as in the prior art are not required at all, and a very simple apparatus shape and configuration enables continuous filtration at a high filtration rate while using a filtration layer as a moving bed.
2) It is extremely suitable for raw water that generates a huge amount of water in a short time, such as rainwater overflow (CSO) in confluent sewers, and is a very compact device that does not necessarily require the use of flocculants. Cloudy particles can be removed effectively.
[Brief description of the drawings]
FIG. 1 is a schematic explanatory drawing showing an embodiment of a filtration apparatus using a floating filter medium of the present invention.
FIG. 2 is a schematic explanatory view of a configuration of an example of a continuous filter using a conventional floating filter medium.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Filtration apparatus 2 Tapered (cone) part 3 Straight body part 4 Floating filter material 5 Filter material flow part 6 Separation tank 7 Raw water 8 Raw water inflow part 9 Filter medium suction pipe 10 Extraction pump 11 Filter medium transfer pipe 12 Filter medium washing chamber 13 Washing drain pipe 14 Pump 15 Filtration water outflow part 16 Filtration water 17 Flocculant 21 Filtration tank 22 Floating filter medium 23 Filtration layer 24 Raw water 25 Raw water supply pipe 26 Fountain port 27 Filtration water 28 Floating filter medium (floating particle)
29 Cleaning pipe 29a Cleaning chamber 30 Valve 31 Separation tank 32 Valve 33 Pump 34 Valve 35 Cleaning drainage Q Raw water flow rate Q 1 Filter medium suction water flow rate Q 2 Cleaning drainage discharge flow rate

Claims (3)

上部の浮上ろ材の流動部を形成するテーパ部と、前記流動部の下部に続く浮上ろ材の充填層からなるろ過層を形成する直胴部を有する槽からなり、前記テーパ部の頂部に配備した原水流入部と、テーパ部の浮上ろ材流動部から浮上ろ材を吸引するろ材吸引管、前記吸引管から吸引ポンプを経由して送られた浮上ろ材を導入する、前記ろ過層の下方に配設した上部開口のろ材洗浄チャンバと、前記槽の底部に配備したろ過水排出部、及び前記ろ材洗浄チャンバの下部に設置した洗浄排水排出管を有することを特徴とする浮上ろ材を用いたろ過装置。It comprises a tank having a taper part that forms a fluidized part of the upper floating filter medium and a straight body part that forms a filtration layer comprising a packed bed of the floated filter medium following the lower part of the fluidized part, and is disposed at the top of the taper part. The raw water inflow section, the filter medium suction pipe for sucking the floating filter medium from the floating filter medium flow section of the tapered section, and the floating filter medium introduced from the suction pipe via the suction pump are introduced below the filtration layer. A filtration apparatus using a floating filter medium, comprising a filter medium cleaning chamber having an upper opening, a filtered water discharge unit disposed at a bottom of the tank, and a cleaning drainage pipe installed at a lower part of the filter medium cleaning chamber. 原水流量をQ、ろ材吸引水流量をQ1、洗浄排水排出流量をQ2とするとき、Q1<Q2<<Qに設定したことを特徴とする請求項1記載のろ過装置。The raw water flow rate Q, filter media suction water flow rate Q 1, when the washing wastewater discharge flow rate Q 2, the filtration apparatus of claim 1, wherein the set to Q 1 <Q 2 << Q. 上部のテーパ部に浮上ろ材の流動部を形成し、前記流動部の下方に続いて浮上ろ材の充填層からなるろ過部が形成されたろ過槽のテーパ部の頂部から原水を導入して、前記流動部及びろ過部をへて下方に流下させ、テーパ部の中間位置から浮上ろ材を吸引して外部に取り出し、取り出した浮上ろ材をろ過部の下方に設けた上方開口のろ材洗浄チャンバへ導入して洗浄後、ろ過部下方に浮上させ、ろ材洗浄チャンバから洗浄排水を排出させ、ろ過槽下部から処理水を取り出し、原水流量をQ、ろ材吸引水流量をQ1、洗浄排水排出流量をQ2とするとき、Q1<Q2<<Qに設定したことを特徴とするろ過方法。Forming a floating part of the floating filter medium in the upper taper part, introducing raw water from the top of the taper part of the filtration tank in which a filtration part composed of a packed bed of floating filter medium is formed below the fluid part, The fluidized part and the filtering part are allowed to flow downward, the floating filter medium is sucked out from the intermediate position of the taper part and taken out to the outside, and the extracted floating filter medium is introduced into a filter medium cleaning chamber having an upper opening provided below the filtering part. After washing, float up below the filtration unit, discharge the washing wastewater from the filter media washing chamber, take out the treated water from the lower part of the filtration tank, feed the raw water flow rate Q, filter material suction water flow rate Q 1 , wash wastewater discharge flow rate Q 2 In this case, the filtration method is characterized in that Q 1 << Q 2 << Q is set.
JP2002159203A 2002-05-31 2002-05-31 Filtration apparatus and filtration method using floating filter medium Expired - Fee Related JP3790857B2 (en)

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