JPH05137906A - Method and device for upflow filtration - Google Patents

Method and device for upflow filtration

Info

Publication number
JPH05137906A
JPH05137906A JP32668791A JP32668791A JPH05137906A JP H05137906 A JPH05137906 A JP H05137906A JP 32668791 A JP32668791 A JP 32668791A JP 32668791 A JP32668791 A JP 32668791A JP H05137906 A JPH05137906 A JP H05137906A
Authority
JP
Japan
Prior art keywords
packed bed
cleaning
filtration
water
packed
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.)
Granted
Application number
JP32668791A
Other languages
Japanese (ja)
Other versions
JPH0677650B2 (en
Inventor
Katsuyuki Kataoka
克之 片岡
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.)
Ebara Corp
Ebara Research Co Ltd
Original Assignee
Ebara Research Co Ltd
Ebara Infilco Co 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 Ebara Research Co Ltd, Ebara Infilco Co Ltd filed Critical Ebara Research Co Ltd
Priority to JP32668791A priority Critical patent/JPH0677650B2/en
Publication of JPH05137906A publication Critical patent/JPH05137906A/en
Publication of JPH0677650B2 publication Critical patent/JPH0677650B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Abstract

PURPOSE:To suppress an increase in the filtration resistance of a packed bed and to easily clean a filter medium by carrying out treatment without preventing the floating of a packing due to the clogging of a packed bed, cleaning the packed bed with an upflow and a cleaning gas and discharging the water from a waste cleaning water outlet provided above a treated water outlet. CONSTITUTION:A space B is formed between the boundary surface A of a packed bed 3 and a net. When the filtration resistance is increased, the whole packed bed 3 is raised by the pressure, hence the packed bed 3 is not compressed, and the elastic porous granular material constituting the packed bed 3 is loosely packed. This packed state is maintained until the SS is leaked into the treated water. At this time, the supply of raw water is stopped, and the packed bed 3 is cleaned. Namely, cleaning water from a cleaning water feed pipe 11 and the air from a cleaning air feed pipe 12 are supplied from below the packed bed 3, the SS collected on the granular material surface and in the gap between the grains is removed, and the waste cleaning water contg. a large amt. of SS is discharged from a waste cleaning water outlet 8.

Description

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

【0001】[0001]

【産業上の利用分野】本発明はSSを含有する懸濁液を
ろ過により清澄化する方法及び装置に関するものであ
る。
TECHNICAL FIELD The present invention relates to a method and an apparatus for clarifying a suspension containing SS by filtration.

【0002】[0002]

【従来の技術】スポンジ状の立体的網目構造をもつ弾性
多孔性粒状物をろ材とし、ろ過槽内にろ材を充填材とす
る充填層を設け、該充填層に上向流で原水を供給する上
向流ろ過装置は、既に特開昭60−147207号公報
に開示されている。
2. Description of the Related Art A sponge-like elastic porous granular material having a three-dimensional network structure is used as a filter medium, and a packing layer containing the filter medium as a packing material is provided in a filtration tank, and raw water is supplied to the packing layer in an upward flow. The upflow filtration device has already been disclosed in JP-A-60-147207.

【0003】この従来技術の上向流ろ過装置は図3に示
すように、弾性多孔性粒状物(以下スポンジ状粒状物と
もいう)からなる充填材24を充填した充填層の上部に
網26を設け、網26の下面で充填材24の浮上を阻止
し、充填材24を圧縮し、スポンジ状粒状物からなるろ
材の空隙率を意図的に小さくして原水供給管21からの
原水を上向流ろ過し、処理水流出管27から処理水(ろ
過水とも呼ぶ)を得る装置である。また、充填材24を
充填した充填層がろ過物により閉塞しろ過抵抗が上昇し
た時、充填層を再生するためには充填層に洗浄用水供給
管25からの洗浄用水、洗浄用空気供給管23からの洗
浄用空気を供給してろ材の洗浄を行う装置である。
As shown in FIG. 3, this prior art upflow filtration apparatus has a net 26 on the top of a packing layer filled with a filler 24 made of elastic porous particles (hereinafter also referred to as sponge particles). It is provided to prevent the filler 24 from floating on the lower surface of the net 26, compress the filler 24, and intentionally reduce the porosity of the filter medium composed of sponge-like particles to direct the raw water from the raw water supply pipe 21 upward. This is a device for performing flow filtration to obtain treated water (also referred to as filtered water) from the treated water outflow pipe 27. Further, when the packed bed filled with the packing material 24 is blocked by the filtered material and the filtration resistance is increased, in order to regenerate the packed bed, the cleaning water from the cleaning water supply pipe 25 and the cleaning air supply pipe 23 are added to the packed bed. It is a device for cleaning the filter medium by supplying cleaning air from the.

【0004】しかし、本発明者はこの従来装置を使用し
て、原水ろ過の従来技術の追試を実施した結果、次のよ
うな欠点があることを見出した。 スポンジ粒状物を圧縮して空隙率を小さくした状態
でSSをろ過除去しているため、ろ過開始後、短時間で
スポンジ粒状物を充填した充填層がSSによって激しく
目詰まりし、ろ過抵抗が急激に増加する。 スポンジ粒状物を充填した充填層の洗浄を充填層の
下部から空気と洗浄用水を上向流を供給して行うが、こ
の際、従来のろ過槽の充填層の上部にその断面を覆うよ
うに張られていた(ろ材の浮上及び流出を阻止するため
の)多孔性部材、ここでは単に網と呼ぶ、その網の下面
にスポンジ状粒状物がますます強く押しつけられてしま
い、ろ材が流動化しないため、ろ材洗浄が非常に難し
い。
However, as a result of carrying out a supplementary test of the conventional technique of raw water filtration using this conventional device, the present inventor has found out the following drawbacks. Since the SS is filtered off while the sponge granules are compressed to reduce the porosity, the packed bed filled with sponge granules is severely clogged with SS in a short time after the start of filtration, and the filtration resistance rapidly increases. Increase to. Cleaning of the packed bed filled with sponge granules is performed by supplying air and washing water upward from the lower part of the packed bed, and at this time, the cross section is covered on the upper part of the packed bed of the conventional filtration tank. The stretched porous material (to prevent the floating and outflow of the filter medium), which is simply called a mesh here, the sponge-like particles are pressed against the lower surface of the mesh even more strongly, and the filter medium does not fluidize. Therefore, cleaning the filter medium is extremely difficult.

【0005】上記従来技術において、このような欠点が
発生する原因を追求した結果、図2のように、スポンジ
のような圧縮されやすい弾性多孔性粒状物が充填してあ
る充填層の上部に接して、浮上防止用の網を設けている
ため、原水の上向流の圧力によってスポンジ粒状物が網
の下面に強く圧縮されてしまい、スポンジ粒状物にSS
が目詰まりし易くなり、充填層のろ過抵抗の急激な増加
をもたらすことを突き止めた。充填層内にSSが捕捉さ
れると充填層のろ過抵抗が増加するので、ますますスポ
ンジ状粒状物は圧縮されてしまうという悪循環が発生す
ることも確認できた。
In the above prior art, as a result of pursuing the cause of such a defect, as shown in FIG. 2, the upper surface of the packing layer filled with elastic porous granular material such as sponge which is easily compressed is contacted. Since the net for preventing floating is provided, the sponge granules are strongly compressed to the lower surface of the net by the upward flow pressure of the raw water, and the sponge granules are SS
Have been found to be easily clogged, resulting in a rapid increase in the filtration resistance of the packed bed. It was also confirmed that when SS is trapped in the packed bed, the filtration resistance of the packed bed increases, so that a vicious cycle occurs in which the sponge-like granular material is more and more compressed.

【0006】すなわち、従来技術はその根本思想がスポ
ンジ状粒状物からなるろ材を充填した充填層に原水を供
給して、ろ材を圧縮した状態で原水のSSをろ過すると
いう点に存在しているのであるが、このような技術思想
そのものの中に大きな問題点を内在しているのである。
従って、従来技術は到底実用的な優れたろ過技術にはな
り得ないことを本発明者は確認した。
That is, the basic idea of the prior art exists in the point that raw water is supplied to a packed bed filled with a filter medium composed of sponge-like particles, and SS of the raw water is filtered while the filter medium is compressed. However, there are major problems inherent in such technical ideas themselves.
Therefore, the present inventor has confirmed that the conventional technique cannot be a practically excellent filtration technique.

【0007】[0007]

【発明が解決しようとする課題】本発明は、上記従来方
法及び装置の欠点を解決することを目的とするもので、
ろ材を充填材とする充填層を有するろ過槽において、S
Sの捕捉容量が大きい立体的網目構造をもつ弾性多孔性
粒状物をろ材とし、充填層に上向流で原水を供給して、
充填層でSSをろ過した時その充填層のろ過抵抗の上昇
が少なく、かつ充填層のろ材の洗浄が容易な上向流ろ過
方法および装置を提供することを課題としている。
SUMMARY OF THE INVENTION The present invention aims to solve the above-mentioned drawbacks of the conventional method and apparatus.
In a filtration tank having a packed bed containing a filter material as a packing material, S
An elastic porous granular material having a three-dimensional network structure with a large S trapping capacity is used as a filter medium, and raw water is supplied to the packed bed in an upward flow,
An object of the present invention is to provide an upflow filtration method and device in which an increase in filtration resistance of the packed bed when the SS is filtered in the packed bed is small and the filter material of the packed bed is easily washed.

【0008】[0008]

【課題を解決するための手段】上記課題は、以下に示し
た本発明の上向流ろ過方法および装置によって達成され
る。 1)立体的網目構造をもつ弾性多孔性粒状物の充填材か
らなる充填層に上向流で原水を供給し原水を充填層でろ
過し処理水を得るに際し、充填層の閉塞に伴う充填材の
浮上を阻止せず処理を行うと共に、随時上向流ならびに
洗浄用気体をもって該充填層を洗浄し、その排水を処理
水流出口より上部に設けた洗浄排水流出口より流出させ
ることを特徴とする上向流ろ過方法。 2)ろ過槽の下部の多孔性支持床上に立体的網目構造を
もつ弾性多孔性粒状物の充填材からなる充填層を形成
し、上記多孔性支持床の下に少なくとも原水供給管と、
空気洗浄用手段と、要すれば水洗浄用手段を設け、該充
填層の上方界面の近傍で、その界面より下方に処理水流
出口を設け、該充填層の上方界面の上方に空間部を置い
て洗浄排水流出口を設けて成る上向流ろ過装置。 3)好ましくは該ろ過槽内に、さらに微生物養生用散気
装置を設けた上記2)に記載の上向流ろ過装置。特に好
ましくは上記水洗浄手段に用いる洗浄用水が原水である
上記1)に記載の上向流ろ過方法によって達成される。
The above object can be achieved by the upflow filtration method and apparatus of the present invention described below. 1) When the raw water is supplied in an upward flow to a packed bed made of a packing material of an elastic porous granular material having a three-dimensional network structure and the raw water is filtered through the packed bed to obtain treated water, the packing material caused by clogging of the packed bed. The treatment is carried out without blocking the floating of the water, the packed bed is washed with an upflow and a cleaning gas at any time, and the drainage thereof is caused to flow out from the washing drainage outlet provided above the treated water outlet. Upflow filtration method. 2) A packing layer formed of a packing material of elastic porous particles having a three-dimensional network structure is formed on the porous support bed below the filtration tank, and at least a raw water supply pipe is provided under the porous support bed.
An air cleaning means and, if necessary, a water cleaning means are provided, a treated water outlet is provided in the vicinity of the upper interface of the packed bed and below the interface, and a space is placed above the upper interface of the packed bed. An upflow filtration device that is equipped with a washing drain outlet. 3) Preferably, the upflow filtration device according to 2) above, further comprising an air diffuser for microbial curing in the filtration tank. Particularly preferably, it is achieved by the upflow filtration method described in 1) above, wherein the washing water used in the water washing means is raw water.

【0009】本発明の技術思想の骨子は、スポンジなど
の立体的網目構造をもつ弾性多孔性粒状物からなる充填
材、すなわちろ材による上向流ろ過の理想的構成方法を
見出した点にある。
The essence of the technical idea of the present invention lies in the finding of an ideal method of constructing an upflow filtration by a filler made of elastic porous particles having a three-dimensional network structure such as sponge, that is, a filter medium.

【0010】より詳しくは、弾性多孔性粒状物からなる
ろ材の充填層の上部に接して設置されていた不動な網を
廃し、原理的にスポンジ状ろ材が網の下面に圧縮されな
いようにすることで充填層での円滑な上向流ろ過が行え
るようにした点にある。このため、弾性多孔性粒状物の
系外への流出を阻止するために、新しい工夫を施ごした
ろ過水の取り出し手段を採用した。また、ろ材の閉塞に
よって充填層のろ過抵抗が上昇した時、随時上向流なら
びに洗浄用気体を用いて、充填層のろ材の洗浄が効果的
に行えるように、充填層の表面上に空間部を設けるなど
本発明の洗浄方法に適した、独自に新しく工夫した洗浄
排水取り出し手段を採用した点にある。
More specifically, it is necessary to eliminate the immovable net which was placed in contact with the upper part of the packed layer of the filter material made of elastic porous particles so that the sponge-like filter material is not compressed on the lower surface of the net in principle. The point is that smooth upflow filtration can be performed in the packed bed. Therefore, in order to prevent the outflow of the elastic porous particles to the outside of the system, a newly devised means for taking out filtered water was adopted. Also, when the filtration resistance of the packed bed increases due to the blockage of the filter medium, a space is formed on the surface of the packed bed so that the filter medium of the packed bed can be effectively washed by using upward flow and a cleaning gas as needed. This is because the newly adopted cleaning drainage means that is unique and suitable for the cleaning method of the present invention is provided.

【0011】本発明では、処理水の取り出し口の位置
は、弾性多孔性粒状物の圧縮をなくし、処理水質を良好
に維持し、スペースを効率よく使用する上で、充填層上
端もしくはその近傍に設けることが好ましい。従って本
発明の装置では、弾性多孔性粒状物の圧縮に伴うろ過抵
抗増加を防止し得ると共に、弾性多孔性粒状物の処理水
流出口から系外への流出を阻止し得るような機能とする
ため、例えばネットなど透水部材は充填層の上部界面近
傍(処理水流出口を覆う位置)の槽壁に設ける。ここ
で、充填層の上部界面近傍とは、充填層上端面をも包含
できる意味である。従って、充填層上端面は、透水部材
の直下にも透水部材の上側にも存在し得る。
In the present invention, the treated water outlet is located at or near the upper end of the packed bed in order to eliminate compression of the elastic porous granular material, maintain good treated water quality, and use the space efficiently. It is preferable to provide. Therefore, in the device of the present invention, it is possible to prevent an increase in filtration resistance due to compression of the elastic porous particles and to prevent the elastic porous particles from flowing out of the system from the treated water outlet. A water-permeable member such as a net is provided on the tank wall near the upper interface of the packed bed (position covering the treated water outlet). Here, the vicinity of the upper interface of the filling layer means that the upper end surface of the filling layer can be included. Therefore, the upper end surface of the packed bed can exist immediately below the water permeable member or above the water permeable member.

【0012】すなわち、透水部材の上方には、充填層と
同じ弾性多孔性粒状物が大気に露出して設けてある。ま
た、本発明の装置の充填層ないし露出層の上に空間部を
配備することが弾性多孔性粒状物の洗浄効果を挙げる上
で重要である。
That is, above the water-permeable member, the same elastic porous granular material as the filling layer is provided exposed to the atmosphere. Further, it is important to provide a space portion on the filling layer or the exposed layer of the device of the present invention in order to enhance the cleaning effect of the elastic porous particulate matter.

【0013】本発明は、SSの物理的除去のみに限定さ
れることはなく、該充填層に酸素含有気泡を供給して好
気的条件を保持させることにより、微生物を付着繁殖さ
せてそのろ材表面に生物膜を形成させ、少なくとも好気
性生物ろ過可能な汚水成分、例えばBOD、NH3 −N
などの成分の生物学的除去と物理学的除去を行うことが
でき、そのための酸素含有気泡供給装置(散気装置)を
充填層の下方部などに適宜配置することができる。
The present invention is not limited to the physical removal of SS, but by supplying oxygen-containing bubbles to the packed bed to maintain aerobic conditions, microorganisms are allowed to adhere and propagate to the filter medium. A biofilm is formed on the surface, and at least aerobic biofilterable sewage components such as BOD, NH 3 -N
It is possible to perform biological removal and physical removal of components such as, and an oxygen-containing bubble supply device (aeration device) for that purpose can be appropriately arranged in the lower part of the packed bed or the like.

【0014】あるいは、槽内を嫌気性条件に維持して嫌
気性生物ろ過装置とすることも可能である。さらに、単
一槽内に好気性生物ろ過層と嫌気性生物ろ過層とが共存
したろ過装置を該充填層により構成してもよい。また、
弾性多孔性粒状物からなる充填層の所望の位置に所望に
応じて弾性多孔性粒状物以外にその他の粒状固体からな
る充填層もしくは弾性多孔性粒状物とそれら粒状固体の
併用層を設けてもよい。
Alternatively, the inside of the tank may be maintained under anaerobic conditions to provide an anaerobic biological filtration device. Further, a filtration device in which an aerobic biological filtration layer and an anaerobic biological filtration layer coexist in a single tank may be constituted by the packed bed. Also,
At the desired position of the packed layer made of elastic porous granules, a packed layer made of other granular solids or a combination layer of the elastic porous granules and those granular solids may be provided in addition to the elastic porous granules as desired. Good.

【0015】本発明は、ろ過継続可能な時間を過ぎると
充填層の洗浄を行うが、その手段は特に制限はなく、公
知の手段が適用できる。この場合、上記散気装置を洗浄
用として兼用してもよく、また別途専用手段、例えば、
空気洗浄用空気供給装置、水洗浄用水供給装置などを配
備することができる。この場合、通常洗浄用としては本
発明の装置による処理水が使用されるが、所望により原
水を使用してもよい。
In the present invention, the packed bed is washed after a lapse of time for which filtration can be continued, but the means therefor is not particularly limited, and known means can be applied. In this case, the air diffusing device may also be used for cleaning, or a separate dedicated means, for example,
An air supply device for cleaning air, a water supply device for cleaning water, and the like can be provided. In this case, the treated water by the apparatus of the present invention is usually used for washing, but raw water may be used if desired.

【0016】また、洗浄用空気に代えて任意の酸素を含
有しない不活性な気体、例えば窒素ガスなどを使用して
もよく、特にこのようなガスは嫌気性充填層を設けた場
合、特に好適であり、好気性充填層を併用した場合はこ
れらも共通に洗浄し得る位置に該洗浄ガス供給装置を配
備するとよい。
Instead of the cleaning air, an inert gas containing no oxygen, such as nitrogen gas, may be used, and such gas is particularly preferable when an anaerobic packing layer is provided. When the aerobic filling layer is also used, the cleaning gas supply device may be arranged at a position where they can be commonly cleaned.

【0017】また、洗浄時などに、弾性多孔性粒状物か
らなるろ材が槽外に流出しないように流出防止装置(9
および10)を配備することが重要である。該流出防止
装置(9および10)としては、ネットなどの多孔性透
水部材が使用できる。上記洗浄装置により充填層を洗浄
して発生したSSなどを含む洗浄排水は、処理水流出口
6よりも上部に設けられる洗浄排水流出口8から排出さ
れる。
Further, an outflow prevention device (9) is provided so that the filter material made of elastic porous particles does not flow out of the tank during washing or the like.
And it is important to deploy 10). As the outflow prevention device (9 and 10), a porous water permeable member such as a net can be used. The cleaning waste water containing SS and the like generated by cleaning the packed bed by the cleaning device is discharged from the cleaning waste water outlet 8 provided above the treated water outlet 6.

【0018】本発明に使用される弾性多孔性粒状物は、
大気圧下で圧縮すると内部空気を排除して収縮し、圧縮
を止めると空気を内部に吸収して元の状態に復元される
弾性を有する多孔性の小体であって、吸水性を有するも
のならいかなる形状、素材、孔構造などのものでも適用
できる。
The elastic porous granules used in the present invention are:
It is a porous small body that has elasticity when it is compressed under atmospheric pressure and contracts by removing the internal air, and when compression is stopped it absorbs air inside and restores to its original state. Any shape, material, hole structure, etc. can be applied.

【0019】該弾性多孔性粒状物は、表面から内部にか
けて連続した穴を持つように形成され、公知の発泡方法
などにより製造できる。該弾性多孔性粒状物の素材とし
ては、上記性質を有するものであるならば、特に制限さ
れず、有機高分子、無機化合物など公知のものを使用で
きるが、中でも素材自体に適度な弾性と強度とを有する
素材が好ましく、特にウレタン樹脂が好ましい。
The elastic porous granular material is formed so as to have continuous holes from the surface to the inside, and can be produced by a known foaming method or the like. The material of the elastic porous granular material is not particularly limited as long as it has the above properties, and known materials such as organic polymers and inorganic compounds can be used. Among them, the material itself has appropriate elasticity and strength. Materials having and are preferable, and urethane resin is particularly preferable.

【0020】例えば、ポリウレタンフォームなどの弾性
多孔性粒状物は、ウレタン樹脂などのプラスチックスを
連続気泡を製造する発泡方法で発泡して作製され、その
まま使用するか、所望する形状、サイズに切断して使用
する。弾性多孔性粒状物のサイズは、10〜30mm、
好ましくは15〜20mmであり、その形状は角形、球
状、その他種々の形状がとれるが、角形が好ましい。そ
の比重は通常0.8〜1.2程度が好ましい。弾性多孔
性粒状物の空隙率は、90%以上が好ましい。また、気
孔径、すなわち、穴径は0.1〜6mm、好ましくは2
〜4mmの範囲から選択することが望ましい。また、1
cmの長さ当たりの穴の数は5〜20個が好ましい。
For example, an elastic porous granular material such as polyurethane foam is produced by foaming plastics such as urethane resin by a foaming method for producing open cells, and is used as it is or cut into a desired shape and size. To use. The size of the elastic porous granular material is 10 to 30 mm,
It is preferably 15 to 20 mm, and its shape can be square, spherical, or various other shapes, but the square is preferable. Its specific gravity is usually preferably about 0.8 to 1.2. The porosity of the elastic porous granular material is preferably 90% or more. Further, the pore diameter, that is, the hole diameter is 0.1 to 6 mm, preferably 2
It is desirable to select from the range of up to 4 mm. Also, 1
The number of holes per cm length is preferably 5 to 20.

【0021】[0021]

【作用】図1を参照しながら本発明の作用と1実施態様
を述べる。1は、上向流ろ過槽であり、2は、弁13を
備えた原水供給管、3は、弾性多孔性粒状物(ポリウレ
タンフォームの角状片)からなるろ材が充填された充填
層(固定層)である。弾性多孔性粒状物は粒径が1〜3
cmのもので、連続気泡でその穴の大きさが、1〜4m
mとかなり大きな穴を持つものが適している。9は、ろ
材の流出を阻止する網ないし多孔板である。また、4は
充填層を支持する多孔性支持床である。
The operation and one embodiment of the present invention will be described with reference to FIG. Reference numeral 1 is an upward flow filtration tank, 2 is a raw water supply pipe equipped with a valve 13, and 3 is a packed bed (fixed layer) filled with a filter medium made of elastic porous granular material (polygonal polyurethane foam). Layer). The elastic porous granular material has a particle size of 1 to 3
cm, open cells with a hole size of 1 to 4 m
It is suitable to have a very large hole of m. Reference numeral 9 is a mesh or a perforated plate that prevents the filter medium from flowing out. Further, 4 is a porous support bed for supporting the packed bed.

【0022】本発明は充填層3の表面界面Aが従来法の
(図3で示した)ようなろ材の浮上を阻止する網に接し
ないようにしてあることが重要である。11は、充填層
3を洗浄するための弁14を備えた洗浄用水を供給する
洗浄用水供給管である。12は、空気洗浄用の空気を供
給する弁15を備えた空気供給管である。6は、SSが
ろ過除去された処理水の流出口であり、弁17を備えた
処理水流出管5が配備されている。槽内の水位は処理水
の流出レベルと同じ位置にある。
In the present invention, it is important that the surface interface A of the filling layer 3 does not come into contact with the mesh for preventing the floating of the filter medium as in the conventional method (shown in FIG. 3). Reference numeral 11 denotes a cleaning water supply pipe for supplying cleaning water, which is provided with a valve 14 for cleaning the packed bed 3. Reference numeral 12 is an air supply pipe provided with a valve 15 for supplying air for air cleaning. 6 is an outlet for treated water from which SS has been filtered out, and a treated water outflow pipe 5 equipped with a valve 17 is provided. The water level in the tank is at the same level as the outflow level of treated water.

【0023】また、10は、充填層3を洗浄する場合、
洗浄排水流出口8から流出する洗浄排水中へろ材が流出
するのを阻止する網である。この洗浄排水流出口8には
処理水流出管7が配備されている。Bは、充填層3の上
部に設けた空間部であり、本発明において重要な役割を
果たす。しかして、本発明の作用を説明すればSSを含
有する懸濁液(すなわち、原水)をウレタンフォームな
どの弾性多孔性粒状物の充填層3に対して上向流で通水
すると、原水のSSが充填層3の無数の空隙部に捕捉さ
れ、特に弾性多孔性粒状物の内部の空隙部にも効果的に
捕捉される。
[0023] Further, 10 is for cleaning the packed bed 3
It is a net that prevents the filter medium from flowing out into the cleaning drainage flowing out from the cleaning drainage outlet 8. A treated water outflow pipe 7 is provided at the washing drainage outlet 8. B is a space provided above the filling layer 3 and plays an important role in the present invention. To explain the operation of the present invention, when an SS-containing suspension (that is, raw water) is passed through the packed layer 3 of elastic porous granular material such as urethane foam in an upward flow, the raw water is SS is trapped in the innumerable voids of the filling layer 3, and particularly effectively in the voids inside the elastic porous granular material.

【0024】このような方法でろ過を継続し続けるにつ
れて、充填層3のSS捕捉量が増加するためろ過抵抗が
増加して行く。図3の従来装置では、このようなろ過抵
抗の増加につれ充填層3に加わる圧力も増えるので、充
填層3が網に押しつけられ、ますます空隙率が減少し、
その結果さらにろ過抵抗が増加するという悪循環を招い
ていた。
As the filtration is continued by such a method, the SS trap amount of the packed bed 3 increases and the filtration resistance increases. In the conventional device of FIG. 3, since the pressure applied to the packed bed 3 increases as the filtration resistance increases, the packed bed 3 is pressed against the net, and the porosity further decreases.
As a result, a vicious circle in which the filtration resistance is further increased is caused.

【0025】しかし、図1の本発明では充填層3の上面
の界面Aが網に接していず、空間部Bが存在するように
したため、ろ過抵抗が増加すると、その圧力によって充
填層3全体が上方に移動することができ(言い換えれば
充填層に充填されたろ材が浮上することができ)、充填
層3が圧縮されない。つまり、充填層3の界面Aの位置
がろ過抵抗の増加につれて上方に移動し、移動した分だ
け空間部Bに露出した状態になるので、露出部のろ材の
自重によってろ過抵抗と丁度バランスした状態を維持す
ることができるのである。
However, in the present invention shown in FIG. 1, since the interface A on the upper surface of the packing layer 3 is not in contact with the net and the space B exists, when the filtration resistance increases, the entire packing layer 3 is caused by the pressure. It can move upward (in other words, the filter medium filled in the packed bed can float), and the packed bed 3 is not compressed. In other words, the position of the interface A of the filling layer 3 moves upward as the filtration resistance increases, and is exposed to the space B by the amount of the movement, so that the filtration resistance is just balanced by the weight of the filter medium at the exposed portion. Can be maintained.

【0026】こうして、ろ過抵抗の増加につれて、充填
層全体が上方に少しづつ移動して行くので、充填層3を
構成する弾性多孔性粒状物を粗な充填状態に維持でき、
この状態は処理水にSSのリークが始まるまで続く。こ
の時点で原水の供給を止め、充填層3の洗浄を行う。洗
浄は次のように行う。すなわち、原水供給管2に取り付
けられている弁13と処理水(ろ過水)流出管5の弁1
7を閉じ、洗浄用水供給管11の弁14を開け、洗浄用
空気供給管12の弁15を開け、洗浄用水供給管11か
らの洗浄用水と洗浄用空気供給管12からの空気とを充
填層3の下部から供給する。すると、充填層3内が、激
しい気液混相乱流によって流動攪拌され、弾性多孔性粒
状物ろ材表面と内部および相互の空隙部に捕捉されてい
たSSが洗浄され、洗浄排水流出口8から多量のSSを
含む洗浄排水が流出する。
In this way, as the filtration resistance increases, the whole packed bed gradually moves upward, so that the elastic porous particles constituting the packed bed 3 can be maintained in a coarse packed state,
This state continues until SS leaks into the treated water. At this point, the supply of raw water is stopped and the packed bed 3 is washed. The cleaning is performed as follows. That is, the valve 13 attached to the raw water supply pipe 2 and the valve 1 of the treated water (filtered water) outflow pipe 5
7 is closed, the valve 14 of the cleaning water supply pipe 11 is opened, the valve 15 of the cleaning air supply pipe 12 is opened, and the cleaning water from the cleaning water supply pipe 11 and the air from the cleaning air supply pipe 12 are packed in a bed. Supply from the bottom of 3. Then, the inside of the packed bed 3 is agitated by a violent gas-liquid mixed phase turbulent flow, and the SS trapped in the surface of the elastic porous granular material filter medium and in the mutual voids are washed and a large amount is discharged from the washing drainage outlet 8. Washing wastewater containing SS is discharged.

【0027】図2はろ材を洗浄している状態のろ過槽の
様子を示したものである。網10はろ材洗浄時にろ材の
流出を防止するためのものである。また、洗浄用水とし
ては、ろ過処理水を貯留しておき、これを使えばよい。
また、原水によって洗浄しても構わない。さて、所要時
間(通常10〜20分位)、上記のような洗浄を続ける
とろ材が洗浄され、清浄な状態に戻るので、弁14およ
び弁15を閉じ、洗浄用水供給管11からの洗浄用水と
洗浄用空気供給管12からの空気の供給を止める。その
後ドレーン管18の弁16を開け、槽内水位をろ過水流
出レベルまで下げる。そして、弁13と弁17を開け、
再びろ過を開始する。
FIG. 2 shows the state of the filtration tank in the state where the filter medium is being washed. The net 10 is for preventing the filter medium from flowing out when the filter medium is washed. Further, as the cleaning water, filtered water may be stored and used.
Further, it may be washed with raw water. By continuing the above washing for the required time (usually about 10 to 20 minutes), the filter medium is washed and returns to a clean state. Therefore, the valves 14 and 15 are closed, and the washing water from the washing water supply pipe 11 is closed. The supply of air from the cleaning air supply pipe 12 is stopped. After that, the valve 16 of the drain pipe 18 is opened to lower the water level in the tank to the filtered water outflow level. Then open valves 13 and 17,
Start filtration again.

【0028】以上のように本発明は弾性多孔性粒状物を
ろ材として使用するろ過方法のポイントが、従来法とは
逆に弾性多孔性粒状物を極力圧縮させないように工夫す
ることにあることを突き止めて完成された。(従来法
は、弾性多孔性粒状物をできるだけ圧縮された状態でろ
過することを根本思想としている。)
As described above, according to the present invention, the point of the filtration method using the elastic porous granular material as the filter medium is to devise so as not to compress the elastic porous granular material as much as possible contrary to the conventional method. It was found and completed. (The conventional method is based on filtering the elastic porous granular material in a state of being compressed as much as possible.)

【0029】[0029]

【実施例】以下、本発明の具体的実施例を示すが、本発
明はこれに限定されるものではない。図1に示した本発
明の上向流ろ過装置(透明塩ビ製、カラム直径200m
mφ、カラム高さ3000mm)を用いて、藤沢市の団
地の下水(SS98〜186mg/リットル、BOD8
6〜178mg/リットル)を対象にして下水からのS
S除去を行った。処理条件と処理結果を表1に示す。
EXAMPLES Specific examples of the present invention will be shown below, but the present invention is not limited thereto. The upflow filtration apparatus of the present invention shown in FIG. 1 (made of transparent PVC, column diameter 200 m
sewage (SS98-186 mg / liter, BOD8) of Fujisawa housing complex using mφ and column height of 3000 mm)
6 to 178 mg / liter) from the sewage
S was removed. Table 1 shows the processing conditions and the processing results.

【0030】[0030]

【表1】 [Table 1]

【0031】表1から次の事実が明らかである。 1.従来の装置よりも、本発明の装置ではろ過継続時間
が約5倍長くとれ、洗浄排水発生率も1/10に減少し
た。(本発明−1と従来装置との比較) 2.本発明−2は、従来の装置に用いられているろ材と
同一物性のポリウレタンフォームを用いたが、やはり従
来装置におけるよりも長時間のろ過が継続でき、洗浄排
水発生率も減少する。 3.本発明−1では、本発明−2のろ材と多孔率、気孔
径を変えてろ過を行った結果、本発明−2の場合に比べ
ろ材は高能率を発揮している。すなわち、本発明の装置
ではろ材の多孔率、気孔径はかなり重要な因子であるこ
とを示している。
The following facts are clear from Table 1. 1. With the device of the present invention, the duration of filtration was about 5 times longer than with the conventional device, and the generation rate of cleaning wastewater was reduced to 1/10. (Comparison between Present Invention-1 and Conventional Device) The present invention-2 uses the polyurethane foam having the same physical properties as the filter medium used in the conventional apparatus, but the filtration can be continued for a longer time than in the conventional apparatus, and the generation rate of cleaning waste water is reduced. 3. In the present invention-1, as a result of performing filtration while changing the porosity and the pore diameter with the filter medium of the present invention-2, the filter medium exhibits high efficiency as compared with the case of the present invention-2. That is, in the apparatus of the present invention, it is shown that the porosity and the pore diameter of the filter medium are very important factors.

【0032】本発明においては、ろ過槽の構成が第1の
重要構成因子であり、第2の重要構成因子は弾性多孔性
粒状物の物性、すなわち、多孔率や気孔径の選定であ
る。従って、多孔率が小さな値で気孔径の大きな弾性多
孔性粒状物を用いて、このようなろ材を図1に示したよ
うな充填層構成とすることにより、最良のろ過が行え
る。
In the present invention, the structure of the filtration tank is the first important constituent factor, and the second important constituent factor is the selection of the physical properties of the elastic porous granular material, that is, the porosity and the pore diameter. Therefore, the best filtration can be performed by using such an elastic porous granular material having a small porosity and a large pore diameter and having such a packing material as shown in FIG.

【0033】[0033]

【発明の効果】立体的網目構造の弾性粒状固体を充填し
た充填層を有するろ過槽において、原水を充填層下部よ
り上向流で供給してろ過を行い、ろ過の処理水を流出す
る処理水流出口を、洗浄排水を流出させる洗浄排水流出
口よりも下方に設ける構造とし、この構造によってろ過
の継続と共に充填層の閉塞により充填材が浮上すること
を阻止せず、また充填層の洗浄時は随時上向流ならびに
洗浄用気体をもって該充填層を洗浄し、洗浄排水流出口
より洗浄排水を流出させることにより、従来の同じ弾性
粒状固体を充填した充填層を有するろ過槽におけるより
も、ろ過継続時間を長くすることができ、かつ洗浄排水
発生率も減少する最良のろ過が行える。
EFFECTS OF THE INVENTION In a filtration tank having a packed bed filled with elastic granular solids having a three-dimensional network structure, raw water is supplied from the lower part of the packed bed in an upward flow to perform filtration, and the treated water for filtration is discharged. The structure is such that the outlet is provided below the cleaning drainage outlet that discharges the cleaning drainage.This structure does not prevent the packing material from floating due to the blockage of the packing layer as the filtration continues, and when cleaning the packing layer. By continuing to wash the packed bed with an upward flow and a cleaning gas at any time and letting the washing waste water flow out from the washing waste water outlet, the filtration is continued more than in the conventional filtration tank having a packed bed filled with the same elastic granular solid. The best filtration can be performed which can prolong the time and reduce the generation rate of washing wastewater.

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

【図1】図1は本発明の上向流ろ過装置の構造を示す断
面図である。
FIG. 1 is a cross-sectional view showing the structure of an upflow filtration device of the present invention.

【図2】図2はろ材を洗浄している状態の本発明の上向
流ろ過装置の様子を示す断面図である。
FIG. 2 is a cross-sectional view showing a state of the upflow filtration device of the present invention in a state where the filter medium is being washed.

【図3】図3は従来の上向流ろ過装置の構造を示す断面
図である。
FIG. 3 is a cross-sectional view showing the structure of a conventional upflow filtration device.

【符号の説明】[Explanation of symbols]

1 ろ過槽 5 処理水流出管 2 原水供給管 6 処理水流出口 3 充填層 7 洗浄排水流出
管 4 多孔性支持床 8 洗浄排水流出
口 9 網(ろ過水流出口用) 23 洗浄用空気供
給管 10 網(洗浄排水流出口用) 24 充填材 11 洗浄用水供給管 25 洗浄用水供
給管 12 洗浄用空気供給管 26 網(充填材
流出防止用) 13〜17 弁 27 処理水流出
管 18 ドレイン管 28 洗浄排水流
出口 20 ろ過槽 29 洗浄排水流
出管 21 原水供給管 30〜35 弁 22 多孔性支持床 36 ドレイン管
1 Filtration Tank 5 Treated Water Outflow Pipe 2 Raw Water Supply Pipe 6 Treated Water Outlet 3 Packed Bed 7 Washing Drainage Outflow Pipe 4 Porous Support Floor 8 Washing Drainage Outlet 9 Net (For Filtered Water Outlet) 23 Washing Air Supply Pipe 10 Net (For cleaning drainage outlet) 24 Filling material 11 Cleaning water supply pipe 25 Cleaning water supply pipe 12 Cleaning air supply pipe 26 Net (for preventing packing material outflow) 13 to 17 valve 27 Treated water outflow pipe 18 Drain pipe 28 Cleaning drainage Outlet 20 Filtration tank 29 Washing drainage outflow pipe 21 Raw water supply pipe 30-35 Valve 22 Porous support bed 36 Drain pipe

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.5 識別記号 庁内整理番号 FI 技術表示箇所 C02F 3/06 6647−4D 3/10 A 6647−4D 3/20 C 3/28 B 7158−4D 7824−4D B01D 23/24 A 7824−4D Z 7112−4D 29/38 Z ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 5 Identification code Internal reference number FI Technical indication C02F 3/06 6647-4D 3/10 A 6647-4D 3/20 C 3/28 B 7158-4D 7824-4D B01D 23/24 A 7824-4D Z 7112-4D 29/38 Z

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 立体的網目構造をもつ弾性多孔性粒状物
の充填材からなる充填層に上向流で原水を供給し原水を
充填層でろ過し処理水を得るに際し、充填層の閉塞に伴
う充填材の浮上を阻止せず処理を行うと共に、随時上向
流ならびに洗浄用気体をもって該充填層を洗浄し、その
排水を処理水流出口より上部に設けた洗浄排水流出口よ
り流出させることを特徴とする上向流ろ過方法。
1. When the raw water is supplied in an upward flow to a packed bed made of a packing material of an elastic porous granular material having a three-dimensional network structure and the raw water is filtered through the packed bed to obtain treated water, the packed bed is blocked. It is possible to perform the treatment without blocking the accompanying floating of the packing material, wash the packed bed with an upflow and a cleaning gas at any time, and let the drainage flow out from the washing drainage outlet provided above the treated water outlet. Characteristic upward flow filtration method.
【請求項2】 ろ過槽の下部の多孔性支持床上に立体的
網目構造をもつ弾性多孔性粒状物の充填材からなる充填
層を形成し、上記多孔性支持床の下に少なくとも原水供
給管と、空気洗浄用手段と、要すれば水洗浄用手段を設
け、該充填層の上方界面の近傍で、その界面より下方に
処理水流出口を設け、該充填層の上方界面の上方に空間
部を置いて洗浄排水流出口を設けて成る上向流ろ過装
置。
2. A packing layer made of a packing material of elastic porous particles having a three-dimensional network structure is formed on the porous support bed below the filtration tank, and at least a raw water supply pipe is provided under the porous support bed. A means for air cleaning and optionally a means for water cleaning are provided, a treated water outlet is provided in the vicinity of the upper interface of the packed bed and below the interface, and a space is provided above the upper interface of the packed bed. An upflow filtration device that is installed and provided with a wash drain outlet.
【請求項3】 ろ過槽内に、さらに微生物養生用散気装
置を設けたことを特徴とする請求項2に記載の上向流ろ
過装置。
3. The upflow filtration apparatus according to claim 2, further comprising an air diffuser for microbial curing provided in the filtration tank.
JP32668791A 1991-11-15 1991-11-15 Upflow filtration method and device Expired - Lifetime JPH0677650B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP32668791A JPH0677650B2 (en) 1991-11-15 1991-11-15 Upflow filtration method and device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP32668791A JPH0677650B2 (en) 1991-11-15 1991-11-15 Upflow filtration method and device

Publications (2)

Publication Number Publication Date
JPH05137906A true JPH05137906A (en) 1993-06-01
JPH0677650B2 JPH0677650B2 (en) 1994-10-05

Family

ID=18190539

Family Applications (1)

Application Number Title Priority Date Filing Date
JP32668791A Expired - Lifetime JPH0677650B2 (en) 1991-11-15 1991-11-15 Upflow filtration method and device

Country Status (1)

Country Link
JP (1) JPH0677650B2 (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0810530A (en) * 1994-06-30 1996-01-16 Masaru Taniguchi Water purifier
JP2012528716A (en) * 2009-06-03 2012-11-15 バイオウォーター テクノロジー エーエス Method and reactor for biological purification of wastewater
JP2013112943A (en) * 2011-11-25 2013-06-10 Hokukon Co Ltd Filter tank component and filter tank using the same
US8475653B2 (en) 2009-09-03 2013-07-02 Korea Institute Of Construction Technology Water treatment apparatus having meshed tubes provided with cilia and water treatment method using the same
CN103623626A (en) * 2013-12-10 2014-03-12 武汉市汉江石油物资技术开发有限责任公司 High-efficiency energy-saving granular filter
JP2016059912A (en) * 2014-09-22 2016-04-25 メタウォーター株式会社 Sedimentation basin
JP2018079441A (en) * 2016-11-17 2018-05-24 日立造船株式会社 Filter device and method for operating filter device
JP7130166B1 (en) * 2021-10-07 2022-09-02 三菱電機株式会社 Foreign matter removal device

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0810530A (en) * 1994-06-30 1996-01-16 Masaru Taniguchi Water purifier
JP2012528716A (en) * 2009-06-03 2012-11-15 バイオウォーター テクノロジー エーエス Method and reactor for biological purification of wastewater
JP2015145006A (en) * 2009-06-03 2015-08-13 バイオウォーター テクノロジー エーエス Method for biological purification of waste water and reactor
US9758402B2 (en) 2009-06-03 2017-09-12 Biowater Technology AS Method and reactor for biological purification of waste water
US8475653B2 (en) 2009-09-03 2013-07-02 Korea Institute Of Construction Technology Water treatment apparatus having meshed tubes provided with cilia and water treatment method using the same
JP2013112943A (en) * 2011-11-25 2013-06-10 Hokukon Co Ltd Filter tank component and filter tank using the same
CN103623626A (en) * 2013-12-10 2014-03-12 武汉市汉江石油物资技术开发有限责任公司 High-efficiency energy-saving granular filter
JP2016059912A (en) * 2014-09-22 2016-04-25 メタウォーター株式会社 Sedimentation basin
JP2018079441A (en) * 2016-11-17 2018-05-24 日立造船株式会社 Filter device and method for operating filter device
JP7130166B1 (en) * 2021-10-07 2022-09-02 三菱電機株式会社 Foreign matter removal device
WO2023058180A1 (en) * 2021-10-07 2023-04-13 三菱電機株式会社 Foreign matter removal device

Also Published As

Publication number Publication date
JPH0677650B2 (en) 1994-10-05

Similar Documents

Publication Publication Date Title
JPH05137906A (en) Method and device for upflow filtration
JP2695624B2 (en) How to clean floating filter media
JP3436947B2 (en) Suspension filtration equipment
JP2592356B2 (en) Organic sewage biological filtration equipment
JPH06285484A (en) Soil water purifying tank
JP3779634B2 (en) Long fiber filtration device
WO2010134175A1 (en) Contaminated water treatment device
JP2565427B2 (en) Organic sewage biological filtration equipment
JPH04341308A (en) Filtration of suspended liquid and device therefor
JPH0745038B2 (en) Downflow filtration method and device
JPH0736916B2 (en) Biofiltration device for organic wastewater
JPS59206022A (en) Liquid purifying method and apparatus
JPH0711836Y2 (en) Aerobic biological filtration equipment
JP2584384B2 (en) Method and apparatus for treating organic sewage
JPH07108361B2 (en) Clarification device for suspension and cleaning method thereof
JPH0745037B2 (en) Method and apparatus for biological treatment of organic wastewater
JPH0647526Y2 (en) Downflow clarification device
JPH0788305A (en) Upward current filter device
JP2002191908A (en) Filter and septic tank
JP3378628B2 (en) Filtration and denitrification equipment for sewage and filtration and denitrification method
JP2518743B2 (en) Downflow biofilter for organic wastewater
JPH04210202A (en) Method and equipment for downflow filtration
JPH0824895A (en) Biological filtration device and cleaning of floating filter medium for biological filtration
JPH0677651B2 (en) Upflow filter
JPH08294699A (en) Biological denitrification apparatus of waste water