JPH0244880Y2 - - Google Patents

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Publication number
JPH0244880Y2
JPH0244880Y2 JP1984053526U JP5352684U JPH0244880Y2 JP H0244880 Y2 JPH0244880 Y2 JP H0244880Y2 JP 1984053526 U JP1984053526 U JP 1984053526U JP 5352684 U JP5352684 U JP 5352684U JP H0244880 Y2 JPH0244880 Y2 JP H0244880Y2
Authority
JP
Japan
Prior art keywords
water
treated water
storage tank
tank
aeration
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.)
Expired
Application number
JP1984053526U
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Japanese (ja)
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JPS60165098U (en
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Priority to JP1984053526U priority Critical patent/JPS60165098U/en
Publication of JPS60165098U publication Critical patent/JPS60165098U/en
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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

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  • Biological Treatment Of Waste Water (AREA)
  • Activated Sludge Processes (AREA)

Description

【考案の詳細な説明】 (産業上の利用分野) この考案は活性汚泥等の好気性微生物を利用す
る排水処理装置の構造に係る。
[Detailed description of the invention] (Field of industrial application) This invention relates to the structure of a wastewater treatment device that utilizes aerobic microorganisms such as activated sludge.

(従来の技術) 従来活性汚泥等、好気性微生物を利用する排水
処理には、活性汚泥法、散水床法、回転円盤
法、接触酸化法等があり、何れも排水中の有機物
等を栄養源とする好気性微生物を繁殖させて有機
物を除去するものであるが、有機物の除去された
水と、繁殖した微生物等を完全に分離しなければ
充分な処理は達成されたといえない。
(Prior technology) Conventional wastewater treatment using activated sludge and other aerobic microorganisms includes the activated sludge method, sprinkled bed method, rotating disk method, and contact oxidation method, all of which use organic matter in wastewater as a nutrient source. This method removes organic matter by breeding aerobic microorganisms, but it cannot be said that sufficient treatment has been achieved unless the water from which organic matter has been removed is completely separated from the grown microorganisms.

通常分離の方法としては好気性微生物の凝集沈
降性による沈降分離が採られ、上澄水と汚泥に分
別される。沈降した汚泥は、曝気槽内の微生物濃
度を一定に保持するため、大部分は曝気槽に返送
され、余剰分は適当な方法で処分し、上澄水は処
理水としてそのまゝ又は更に過して放流され
る。
The usual separation method is sedimentation separation using the coagulation-sedimentation properties of aerobic microorganisms, and the water is separated into supernatant water and sludge. In order to maintain a constant microbial concentration in the aeration tank, most of the settled sludge is returned to the aeration tank, the surplus is disposed of in an appropriate manner, and the supernatant water is used as treated water or can be further filtered. It is released into the river.

しかしこれ等の方法は好気性微生物の凝集沈降
分離性が処理水の水質を大きく左右するため、こ
れらに管理の重点がおかれ、それを満足させるた
めに曝気量、汚泥濃度、微生物の種類等の適用範
囲が厳選され、工業的操作面では管理が困難で、
しかもなほ安定した高度の処理が得難い等の欠点
がある。
However, in these methods, the coagulation and sedimentation separation properties of aerobic microorganisms greatly affect the water quality of the treated water, so management is focused on these factors, and in order to satisfy this, the amount of aeration, sludge concentration, type of microorganisms, etc. The scope of application is carefully selected, and it is difficult to manage in terms of industrial operation.
Moreover, it has drawbacks such as difficulty in achieving stable and high-level processing.

これらの欠点を解消するため、水と汚泥との分
離を沈降によらず、過による方式が考えられて
いる。この方式は曝気槽底部に比較的粒度の小さ
い材を層状に充填した床を設け、この床の
底部に集水部を設け、曝気槽に連続供給された排
水は槽内に設けられた散気管から噴出する空気泡
の曝気と活性汚泥中の好気性微生物の働きで排水
中の有機物等は吸着分解処理される。処理された
水は床で過され、汚泥と分離された後、集水
部に集められ、槽外に排出される。槽外に排出さ
れた水は立上り管によつて処理水貯槽の上部に送
られ、ここに貯留されるが、一定量以上の処理水
は貯槽上部の溢流管から放出される。時間の経過
と共に床上面に汚泥がち密な層をなし、床内
部でも微生物の増殖があつて次第に空隙が失なわ
れ、処理水の通過が著しく困難になる。そのとき
は、曝気槽への原水供給及び貯槽への処理水移送
を止め、処理水貯槽から逆洗用の水をポンプによ
つて上記集水部から床上部に向けて水を噴出さ
せ、床表面に付着している汚泥を離脱させ、か
つ床内の汚泥を押出して空隙を復活させその後
は上記と同様の排水処理を繰返すのである。
In order to overcome these drawbacks, methods have been proposed in which water and sludge are separated by filtration instead of by sedimentation. In this method, a bed filled with a layer of material with relatively small particle size is installed at the bottom of the aeration tank, a water collection section is installed at the bottom of this bed, and the wastewater continuously supplied to the aeration tank is passed through an aeration pipe installed in the tank. The organic matter in the wastewater is adsorbed and decomposed by the aeration of air bubbles ejected from the sludge and the action of aerobic microorganisms in the activated sludge. The treated water is filtered through the bed, separated from sludge, collected in a water collection area, and discharged outside the tank. The water discharged outside the tank is sent to the upper part of the treated water storage tank by a riser pipe and is stored there, but treated water exceeding a certain amount is discharged from an overflow pipe at the upper part of the storage tank. As time passes, a dense layer of sludge forms on the upper surface of the floor, and microorganisms proliferate inside the floor, gradually eliminating voids and making it extremely difficult for treated water to pass through. In that case, stop the supply of raw water to the aeration tank and transfer of treated water to the storage tank, and use a pump to squirt water for backwashing from the treated water storage tank from the water collection section to the upper part of the floor. The sludge adhering to the surface is removed, the sludge in the bed is pushed out, the voids are restored, and the same wastewater treatment as above is repeated.

上記の過方式による排水処理作業において、
処理時間の経過に伴つて生ずる床部分の処理水
通過の阻害現象について仔細に調べたところ次の
ようなことがわかつた。即ち、曝気槽内の排水中
に空気泡を放出する散気管は床の表面付近に設
けられるため、床表面付近の水には放出された
微細な気泡が含まれており、このような水が床
内に吸引され、吸引された気泡は集合して空気層
となつて床に封じこめられ、これが水の通過を
阻害し、終には処理水の流出を不可能にする原因
の一つになる。この床内における空気層の生起
は床の上面を境にして外側(曝気ゾーン側)の
圧力より床内側が減圧になる程、著しく、減圧
となる原因としては床表層の目詰まりによる
過抵抗の増加等のため流入水が流出水より量的に
大きくなり、曝気槽の水位が処理水貯槽の水位よ
り高くなることで必然的に発生する。そして床
内の空気層の生起により、この現象は更に加速さ
れ、水処理継続も困難なる。
In wastewater treatment work using the above method,
A detailed investigation into the phenomenon of obstruction to the passage of treated water through the bed as the treatment time progressed revealed the following. In other words, the aeration pipe that releases air bubbles during drainage in the aeration tank is installed near the floor surface, so the water near the floor surface contains the released fine air bubbles. The air bubbles that are sucked into the floor gather together to form an air layer and become trapped in the floor, which obstructs the passage of water and is one of the reasons why it is eventually impossible for treated water to flow out. Become. The formation of this air layer within the bed is so remarkable that the pressure inside the bed becomes lower than the pressure outside (aeration zone side) with the upper surface of the bed as a boundary. This inevitably occurs when the inflow water becomes larger than the outflow water due to increase in volume, and the water level in the aeration tank becomes higher than the water level in the treated water storage tank. This phenomenon is further accelerated by the formation of an air layer within the bed, making it difficult to continue water treatment.

更に、上記過方式において、床底部に設け
られた集水部に集められた水は導出され、処理水
貯槽に送給されるが、この送給のための配管は曝
気槽の液面を一定以上に保持させる必要上、その
高さまで立上がらせて処理水貯槽に連結される。
床に空気槽がない間は支障ないが、一旦床内
に空気層が発生した場合、空気は集水部を経て水
と一諸になつて処理水貯槽への処理水送給管内に
押出され、この送給管の立上り部でエヤーリフト
を構成し、このため床内を減圧にし、更に気泡
の吸込みを増大することがわかつた。
Furthermore, in the above-mentioned filtration system, the water collected in the water collection section provided at the bottom of the floor is led out and sent to the treated water storage tank, but the piping for this delivery keeps the liquid level in the aeration tank constant. Because it is necessary to maintain the water above that level, it is raised to that height and connected to the treated water storage tank.
There is no problem as long as there is no air tank on the floor, but once an air layer forms in the floor, the air passes through the water collection section, combines with water, and is pushed out into the treated water supply pipe to the treated water storage tank. It was found that the rising part of this feed pipe constitutes an air lift, which reduces the pressure in the bed and further increases the suction of air bubbles.

(本考案の目的) 本考案は上述の、活性汚泥を使用して、過方
式によつて汚泥を分離する装置における欠点を解
消し、更に構造的に簡素にした排水処理装置を提
供することを目的とするものである。
(Purpose of the present invention) The present invention aims to eliminate the drawbacks of the above-mentioned apparatus for separating sludge by a filtration method using activated sludge, and to provide a wastewater treatment apparatus which is further simplified in structure. This is the purpose.

(図面の説明) 第1図は本考案装置の一例の縦断正面略図であ
る。
(Description of the Drawings) FIG. 1 is a schematic longitudinal sectional front view of an example of the device of the present invention.

図中、1は曝気槽、2は床であつて、例えば
珪石、珪砂、アンスラサイト等の比較的粒度の小
さい材を曝気槽1の底面上に、所要の高さに層
状に充填して形成される。3は集水部であつて、
床2の下部に設置される。その構造としては例
えば多数の細孔を穿つた管を多数本、中心となる
排水管の開口部位置から放射状に配置したもの、
又は、扁平な丸型、角型の室で、その上面、更に
必要に応じて側面に多数の細孔を穿つたものなど
が用いられる。4は散気管で、床2の上面より
も僅かに上位に位置させられ、その構造は例えば
上記集水部3と同様のものでもよく、その他曝気
槽1内に均一に空気泡が泡出されるものであれ
は、如何なる構造からなるものでもよい。5は散
気管4に空気を送るブロアー、6は原水を導入す
る配管、7は集水部3に集められた処理水を処理
水貯槽8に送給する導管であつて、処理水貯槽8
における連結部は該貯槽8の下部とする。即ちそ
の連結部は図示のように貯槽8の底面に開口して
いてもよく、また貯槽8の側壁の底面に近い下位
に開口していてもよい。また貯槽8は、図示のも
のでは側壁の一部を曝気槽1の側壁の一部と共用
しているが、貯槽8を独立させてもよい。その場
合でも導管7をなるべく短いものとするように、
近接して設けるのがよい。9は処理水貯槽8の比
較的上位に設けた処理水の溢流管、10は逆洗用
のポンプ、11は曝気槽1における液面、12は
処理水貯槽8における液面である。
In the figure, 1 is an aeration tank and 2 is a floor, which is formed by filling the bottom of the aeration tank 1 with relatively small-grained materials such as silica stone, silica sand, and anthracite in a layered manner to a desired height. be done. 3 is the water collection part,
It is installed at the bottom of floor 2. For example, the structure is one in which many pipes with many pores are arranged radially from the opening position of the central drainage pipe.
Alternatively, a flat round or rectangular chamber with a large number of pores bored in its upper surface and, if necessary, on its side surfaces, is used. Reference numeral 4 denotes an aeration pipe, which is positioned slightly above the upper surface of the floor 2, and its structure may be similar to the above-mentioned water collection section 3, for example, and air bubbles are uniformly bubbled into the aeration tank 1. It may have any structure. 5 is a blower that sends air to the aeration pipe 4; 6 is a pipe that introduces raw water; and 7 is a conduit that delivers the treated water collected in the water collection section 3 to the treated water storage tank 8.
The connecting portion in is the lower part of the storage tank 8. That is, the connecting portion may be opened at the bottom of the storage tank 8 as shown in the figure, or may be opened at a lower part of the side wall of the storage tank 8 near the bottom. Further, in the illustrated embodiment, the storage tank 8 shares a part of the side wall with a part of the side wall of the aeration tank 1, but the storage tank 8 may be made independent. Even in that case, the conduit 7 should be made as short as possible.
It is best to place them close together. 9 is a treated water overflow pipe provided relatively above the treated water storage tank 8; 10 is a pump for backwashing; 11 is a liquid level in the aeration tank 1; and 12 is a liquid level in the treated water storage tank 8.

この装置を運転するには、配管6から曝気槽1
に原水を一定量で連続供給し、同時に散気管4か
ら空気を泡出させる。曝気槽1内には活性汚泥を
存在させておき、この活性汚泥の好気性微生物の
働きで、原水中の有機物等は吸着、分解され、処
理された水は床2で過され、汚泥と分離、分
離された処理水は集水部3を経て導管7を矢印A
方向に通り、処理水貯槽8に送られ、溢流管9の
位置を越えた水は排出され、この水はそのまゝ放
流されるか、又は過器で再度過された後、放
流される。
To operate this device, the pipe 6 must be connected to the aeration tank 1.
A constant amount of raw water is continuously supplied to the tank, and at the same time, air is bubbled out from the air diffuser pipe 4. Activated sludge is kept in the aeration tank 1, and organic matter in the raw water is adsorbed and decomposed by the action of aerobic microorganisms in this activated sludge, and the treated water is passed through the bed 2 and separated from the sludge. , the separated treated water passes through the water collection section 3 and continues along the conduit 7 as shown by arrow A.
The water flowing in the direction of the treated water is sent to the treated water storage tank 8, and the water that exceeds the overflow pipe 9 is discharged, and this water is either discharged as is or is passed through the filter again and then discharged. .

集水部3から貯槽8への水の流れの際、導管7
に設けたポンプ10は作動させず、水圧のみによ
つて処理水を貯槽8に送給する。従つて転開始時
から暫くの間は、液面11と12とは同レベルに
ある。
When water flows from the water collection section 3 to the storage tank 8, the conduit 7
The pump 10 provided in the tank 8 is not operated, and the treated water is fed to the storage tank 8 only by water pressure. Therefore, for a while after the start of rotation, the liquid levels 11 and 12 are at the same level.

更に時間が経過すると床2の表面部に、次第
に汚泥層が形成され、水の過抵抗となり、過
量も減少するため曝気槽1の液面11が上昇し、
床表層部を境に圧力差が生じ、気泡が床内部
に吸込まれ、空気層を発生する気配が生ずる。し
かるときは逆洗用のポンプ10を作動し、貯槽8
内の処理水を、導管7中、矢印Bの方向に流し、
集水部3に設けた細孔から処理水を噴出させ、
床2の表面層に付着している汚泥を離脱させ、
床2の過抵抗を除く。過抵抗が零近くまでに
なれば、ポンプ10の作動を停止する。ポンプ1
0が作動を停止すれば、導管7内において、水は
再び矢印A方向に流れ、排水の処理が再開され、
以上の操作が繰返される。
As time passes further, a sludge layer is gradually formed on the surface of the bed 2, resulting in excessive resistance to water and reducing the excess amount, causing the liquid level 11 in the aeration tank 1 to rise.
A pressure difference occurs across the surface layer of the floor, causing air bubbles to be sucked into the floor, creating an air layer. When this happens, the backwashing pump 10 is activated and the storage tank 8
Flow the treated water in the pipe 7 in the direction of arrow B,
The treated water is spouted from the pores provided in the water collection part 3,
Removes sludge adhering to the surface layer of floor 2,
Exclude excessive resistance on floor 2. When the excessive resistance approaches zero, the operation of the pump 10 is stopped. pump 1
0 stops operating, the water flows again in the direction of arrow A in the conduit 7, and the wastewater treatment is restarted.
The above operations are repeated.

逆洗用のポンプ10としては、導管7の経路の
高低を避けるため、吸込管、吐出管が同軸の例え
ば渦巻型ポンプ(特に渦巻型ラインポンプ)が望
ましく、低揚程高揚量のものが適している。この
ような高揚量のポンプを用いることにより、少量
の水でもつて極めて短い時間の逆洗で、床表面
の汚泥層を破壊し、離脱させることができる。
As the pump 10 for backwashing, in order to avoid the height of the route of the conduit 7, it is preferable to use, for example, a centrifugal pump (particularly a centrifugal line pump) with a suction pipe and a discharge pipe coaxial, and a pump with a low head and high volume is suitable. There is. By using such a high-capacity pump, the sludge layer on the floor surface can be destroyed and removed by backwashing with a small amount of water in an extremely short period of time.

1回の逆洗に使用する逆洗水は処理水貯槽8内
に貯留されている処理水の一部を使用し、1回当
りの使用量は処理水貯槽8に設けられたレベルス
イツチ等により制御される。1回の逆洗に使用す
る水量は少量でよく、通常床容積の1/2〜1/3程
度でよい。
The backwash water used for each backwash uses a part of the treated water stored in the treated water storage tank 8, and the amount used per time is determined by a level switch etc. installed in the treated water storage tank 8. controlled. The amount of water used for one backwashing may be small, usually about 1/2 to 1/3 of the floor volume.

逆洗用のポンプ10を始動して逆洗を開始する
時期は、曝気槽1の液面11が処理水貯槽8の液
面12よりも上昇し始める時点から、液面11と
液面12との差が30cmまで、好ましくは10cmま
で、一層好ましくは3cmまでの範囲にあるときが
よい。この液面差が小さいほど、床内の過抵
抗を除くのが容易である。時間でいえば、原水処
理を30〜90分行なつて逆洗を行なうサイクルを繰
り返すのがよい。そして処理水の供給量、水質等
によつて予めこのサイクルの時間が定められ、タ
イマー等を使用し自動化することができる。
The time to start backwashing by starting the backwashing pump 10 is from the time when the liquid level 11 in the aeration tank 1 begins to rise above the liquid level 12 in the treated water storage tank 8, and when the liquid level 11 and the liquid level 12 are It is preferable that the difference is in the range of up to 30 cm, preferably up to 10 cm, more preferably up to 3 cm. The smaller this liquid level difference is, the easier it is to remove excess resistance within the bed. In terms of time, it is best to repeat the cycle of treating raw water for 30 to 90 minutes and then backwashing. The time for this cycle is determined in advance depending on the supply amount of treated water, water quality, etc., and can be automated using a timer or the like.

なお、導管7において弁の設置を示していない
が通常の運転を続けている間は弁の使用を必要と
しない。ただ装置の修理などで運転を止めるとき
などは弁を必要とするので、特に図示していない
が設けておくのがよい。
Although the installation of a valve in the conduit 7 is not shown, the use of the valve is not required during normal operation. However, a valve is required when stopping operation for equipment repair, etc., so it is recommended to provide one, although it is not particularly shown.

(考案の効果) 本考案は以上のような構造からなり、次の効果
を奏するものである。
(Effects of the invention) The present invention has the structure described above and has the following effects.

(イ) 本考案の装置は従来の水と汚泥の分離を沈降
分離する方式によらず、両者の分離を過によ
つて行なうので汚泥の凝集沈降性は問題にする
必要がなく、管理上の制約が低減される。
(b) Since the device of the present invention separates water and sludge by overpassing, instead of using the conventional method of separating water and sludge by sedimentation, there is no need to worry about the flocculation and sedimentation of sludge, and it is important for management purposes. Constraints are reduced.

(ロ) 水と汚泥の分離として過方式を採るにして
も、本考案の装置では通常考えられる、曝気槽
からの排水を処理水貯槽に送る導管として立ち
上り部分がないため、エヤーリフトの現象によ
るような問題がない。
(b) Even if a filtration method is used to separate water and sludge, the device of the present invention does not have a rising part to serve as a conduit for sending wastewater from the aeration tank to the treated water storage tank, so it may be caused by the phenomenon of air lift. There are no problems.

(ハ) 曝気槽からの処理水の導出管と床に逆洗水
を送りこむ導管が同一配管で兼用され、処理水
の導出、逆洗水の送給を切替えるための切替バ
ルブは必要なく、装置が安価になるだけでな
く、作業管理も容易である。
(c) The pipe for discharging treated water from the aeration tank and the pipe for sending backwash water to the floor are shared by the same pipe, and there is no need for a switching valve to switch between discharging treated water and supplying backwash water. It is not only cheaper, but also easier to manage.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本考案装置の一例の縦断正面略図であ
る。 図中1は曝気槽、2は床、3は集水部、4は
散気管、7は曝気槽と処理水貯槽をつなぐ導管、
8は処理水貯槽、10はポンプである。
FIG. 1 is a schematic longitudinal sectional front view of an example of the device of the present invention. In the figure, 1 is the aeration tank, 2 is the floor, 3 is the water collection part, 4 is the aeration pipe, 7 is the conduit connecting the aeration tank and the treated water storage tank,
8 is a treated water storage tank, and 10 is a pump.

Claims (1)

【実用新案登録請求の範囲】[Scope of utility model registration request] 曝気槽1と処理水貯槽8とよりなり、曝気槽1
の底部には濾床2を形成させ、この濾床2の表面
付近に散気管4を、濾床2の下部に集水部3を設
け、この集水部3と処理水貯槽8の下部とを、途
中にポンプ10を有する導管7で連結し、このポ
ンプ10は、これが作動するとき処理水貯槽8内
の水を集水部3に送りこむように配置し、ポンプ
10の非作動時には、曝気槽1内の水圧によつて
集水部3の水が導管7を経て処理水貯槽8に流入
するようにしてなる活性汚泥を用いる排水処理装
置。
Consisting of an aeration tank 1 and a treated water storage tank 8, the aeration tank 1
A filter bed 2 is formed at the bottom of the filter bed 2, an aeration pipe 4 is provided near the surface of the filter bed 2, a water collection section 3 is provided at the bottom of the filter bed 2, and the water collection section 3 and the bottom of the treated water storage tank 8 are connected. are connected by a conduit 7 having a pump 10 in the middle, and this pump 10 is arranged so as to send the water in the treated water storage tank 8 to the water collection part 3 when the pump 10 is in operation, and when the pump 10 is not in operation, the aeration is carried out. A wastewater treatment device using activated sludge in which water in a water collection section 3 flows into a treated water storage tank 8 through a conduit 7 due to water pressure in a tank 1.
JP1984053526U 1984-04-13 1984-04-13 Wastewater treatment equipment Granted JPS60165098U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1984053526U JPS60165098U (en) 1984-04-13 1984-04-13 Wastewater treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1984053526U JPS60165098U (en) 1984-04-13 1984-04-13 Wastewater treatment equipment

Publications (2)

Publication Number Publication Date
JPS60165098U JPS60165098U (en) 1985-11-01
JPH0244880Y2 true JPH0244880Y2 (en) 1990-11-28

Family

ID=30574473

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1984053526U Granted JPS60165098U (en) 1984-04-13 1984-04-13 Wastewater treatment equipment

Country Status (1)

Country Link
JP (1) JPS60165098U (en)

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5626867U (en) * 1979-08-08 1981-03-12
JPS5627311A (en) * 1979-08-14 1981-03-17 Sudo Jiyuusaburou Concrete mortar filler
JPS58171297U (en) * 1982-05-10 1983-11-15 株式会社クボタ water treatment equipment

Also Published As

Publication number Publication date
JPS60165098U (en) 1985-11-01

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