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JPS61291099A - Downward flow type biological membrane purifying apparatus - Google Patents

Downward flow type biological membrane purifying apparatus

Info

Publication number
JPS61291099A
JPS61291099A JP60131064A JP13106485A JPS61291099A JP S61291099 A JPS61291099 A JP S61291099A JP 60131064 A JP60131064 A JP 60131064A JP 13106485 A JP13106485 A JP 13106485A JP S61291099 A JPS61291099 A JP S61291099A
Authority
JP
Japan
Prior art keywords
air lift
pipe
filter medium
water
downward flow
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
JP60131064A
Other languages
Japanese (ja)
Other versions
JPH0232955B2 (en
Inventor
Shuzo Kakimoto
柿本 脩三
Toshiaki Murakami
村上 聰明
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.)
Sanki Engineering Co Ltd
Original Assignee
Sanki Engineering 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 Sanki Engineering Co Ltd filed Critical Sanki Engineering Co Ltd
Priority to JP60131064A priority Critical patent/JPS61291099A/en
Priority to KR1019850007706A priority patent/KR890004193B1/en
Priority to FR8604588A priority patent/FR2583406B1/en
Priority to CH1866/86A priority patent/CH667080A5/en
Priority to SE8602501A priority patent/SE467253B/en
Publication of JPS61291099A publication Critical patent/JPS61291099A/en
Publication of JPH0232955B2 publication Critical patent/JPH0232955B2/ja
Granted legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/12Activated sludge processes
    • C02F3/22Activated sludge processes using circulation pipes
    • C02F3/223Activated sludge processes using circulation pipes using "air-lift"
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/06Aerobic processes using submerged filters
    • 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

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

PURPOSE:To simultaneously perform the biological treatment of raw water and the washing of a filter material, by mounting a purifying tank, an air diffuser and a water collection chamber and arranging an air lift pipe in the purifying tank in the vertical direction to suck a filter material having a solid substance adhered thereto from the lower end of the air lift pipe. CONSTITUTION:The raw water supplied from the upper part of a purifying tank 23 by an inflow pipe passes through a filter tank 22a. The SS-component and BOD component contained in the raw water receive oxidative decomposition by the aerobic biological treatment of bacteria and a solid substance is adhered and accumulated to the surface of a filter material 22. The solid substance is collected on the surface of the filter material 22 or in the spaces of said filter material 22 and moves to the lower bed of the filter tank 22a in a collected state to be guided from an air lift pipe 27 to a separation apparatus 29. The raw water is downwardly flowed from the upper part of the purifying tank 23 by the suction force generated by an air lift apparatus 28 when passed through the filter tank 22a while purified and treated water is sucked in a water gathering chamber 25.

Description

【発明の詳細な説明】 (イ)発明の技術分野 本発明は、原水の生物処理と濾材の洗浄を同時に連続し
て行なう下向流型生物膜浄化装置に関する。
DETAILED DESCRIPTION OF THE INVENTION (a) Technical Field of the Invention The present invention relates to a downward flow type biofilm purification device that simultaneously and continuously performs biological treatment of raw water and cleaning of filter media.

(ロ)従来技術と問題点 従来から、有槻物によって汚染された水を微生物の(@
Jきによって浄化する方法の1つとして、微生物を固体
粒子に付着させ、これをjm過する原排水中の汚染物質
と接触させ、原排水を好気性消化し浄化する生物膜浄化
装置がある。この生物膜浄化装置の代表的なものとして
、原排水を該装置の上部から下向きに流す下向流型生物
膜浄化装置が知られている。
(b) Conventional technology and problems Conventionally, water contaminated with slag materials has been treated with microorganisms (@
One of the methods for purifying waste water by JM is a biofilm purification device that attaches microorganisms to solid particles and brings them into contact with pollutants in the raw wastewater to be purified by aerobic digestion of the raw wastewater. A typical example of this biofilm purification device is a downward flow type biofilm purification device in which raw wastewater flows downward from the top of the device.

この下向流型生物膜浄化装置は、最近開発されたもので
あって、例えば第11図に示すものが知られている。
This downward flow type biofilm purification device has been developed recently, and for example, the one shown in FIG. 11 is known.

図示のように、反応槽1は床板2によって仕切られ、床
板2の上部の原水処理室3にば濾材(例えばアンスラザ
イト、活性炭、軽量骨材等で粒径2〜10龍程度のもの
)4が充填されている。床板2の下部には原水処理室3
で生物処理された処理水を集水する集水室5が設けられ
ている。床板2には原水処理室3で処理された処理水を
集める集水ストレーナ6が設けられている。原水処理室
3には生物処理に必要な空気を曝気ブロア7によって原
水中に吹き込む散気装置8が配されている。
As shown in the figure, a reaction tank 1 is partitioned by a floor plate 2, and a raw water treatment chamber 3 above the floor plate 2 has a filter material (for example, anthrazite, activated carbon, lightweight aggregate, etc. with a particle size of about 2 to 10 mm) 4. is filled. At the bottom of the floorboard 2 is a raw water treatment chamber 3.
A water collection chamber 5 is provided to collect treated water that has been subjected to biological treatment. A water collection strainer 6 is provided on the floor plate 2 to collect treated water treated in the raw water treatment chamber 3. The raw water treatment chamber 3 is provided with an aeration device 8 that blows air necessary for biological treatment into the raw water using an aeration blower 7.

反応槽1とは別体に処理水槽9が設けられ、さらに、こ
の処理水槽9と反応槽1の間には集水室5からの処理水
を通す処理水管10が設けられている。固形物が付着し
た濾材4を洗浄処理するため、逆洗ポンプ11.逆洗ブ
ロア12.サイホン管13が、各々、処理水槽9.集水
室5.原水処理室3に配されている。
A treated water tank 9 is provided separately from the reaction tank 1, and a treated water pipe 10 through which treated water from the water collection chamber 5 passes is provided between the treated water tank 9 and the reaction tank 1. In order to wash the filter medium 4 to which solid matter has adhered, a backwash pump 11. Backwash blower 12. A siphon pipe 13 is connected to each treatment water tank 9. Water collection room 5. It is located in raw water treatment room 3.

原水処理室3の上部より流入した原水は、濾材4中を通
過し、生物処理されて、集水ストレーナ6を通って集水
室5に入る。集水室5に集められた処理水は、処理水管
10を通って処理水槽9に貯留後排出される。この間、
原水は、原水処理室3内の濾材4中を通過する際に、濾
材4表面に付着した微生物の働きにより浄化される。原
水中に含まれるSS成分及びBOI)成分等は生物処理
により濾材4表面にイ」着し、濾材4には固形物が蓄積
する。このため、濾材4の間には目詰まりが生じ原水の
通過抵抗が増大する。このように、濾材4に付着した固
形物を除去する必要から、濾材4の逆洗が行なわれる。
Raw water flowing from the upper part of the raw water treatment chamber 3 passes through the filter medium 4, is subjected to biological treatment, and enters the water collection chamber 5 through the water collection strainer 6. The treated water collected in the water collection chamber 5 passes through the treated water pipe 10 and is stored in the treated water tank 9 and then discharged. During this time,
When the raw water passes through the filter medium 4 in the raw water treatment chamber 3, it is purified by the action of microorganisms attached to the surface of the filter medium 4. SS components and BOI components contained in the raw water are deposited on the surface of the filter medium 4 through biological treatment, and solid matter accumulates on the filter medium 4. For this reason, the spaces between the filter media 4 become clogged, and the resistance to passage of raw water increases. In this manner, the filter medium 4 is backwashed because it is necessary to remove solid matter adhering to the filter medium 4.

即ち、逆洗ブロア12がら集水室5を通って原水処理室
3に多量の空気を吹き込み、濾材4から固形物を分離さ
せ、次いで、逆洗ポンプ11より処理水を原水処理室3
内に送り込んで、固形物を原水処理室3上部よりサイボ
ン管13を介して反応槽1外に排出する。
That is, a large amount of air is blown into the raw water treatment chamber 3 through the water collection chamber 5 from the backwash blower 12 to separate solids from the filter medium 4, and then the treated water is sent to the raw water treatment chamber 3 by the backwash pump 11.
The solids are discharged from the upper part of the raw water treatment chamber 3 to the outside of the reaction tank 1 via the cybon pipe 13.

しかしながら、このような下向流型生物膜浄化装置にあ
っては、第1に、濾材4の逆洗処理中には原水の浄化処
理機能が停止される。即ち、原水の浄化処理と逆洗によ
る濾材4の洗浄処理を同時に連続して行なうことができ
ず、該浄化装置の稼動率が下がる。このため、原水の浄
化処理と濾材4の洗浄処理を同時に連続して行なおうと
すれば、複数個の該浄化装置が必要となり装置が必然的
に大型化することになる。
However, in such a downward flow type biofilm purification device, firstly, the purification function of the raw water is stopped during the backwashing process of the filter medium 4. That is, the purification of raw water and the cleaning of the filter medium 4 by backwashing cannot be carried out simultaneously and continuously, and the operating rate of the purification device decreases. For this reason, if it is attempted to simultaneously and continuously perform the purification treatment of the raw water and the cleaning treatment of the filter medium 4, a plurality of such purification devices will be required, which will inevitably increase the size of the device.

第2に、原水の浄化処理中には、濾材4の洗浄処理は行
なわれない。従って、濾材4の洗浄後、時間の経過と共
に濾材4には固形物が付着し、生物処理による浄化率が
減少する。
Second, the filter medium 4 is not cleaned during the purification of the raw water. Therefore, after cleaning the filter medium 4, solid matter adheres to the filter medium 4 over time, and the purification rate by biological treatment decreases.

第3に、濾材4の逆洗処理には、多量の空気。Thirdly, a large amount of air is required for backwashing the filter medium 4.

大量の逆洗用水が必要なことから、逆洗ブロア12、逆
洗ポンプ11.大規模な処理水槽9を必要 ゛としてい
た。
Since a large amount of backwash water is required, a backwash blower 12, a backwash pump 11. A large-scale treatment water tank9 was required.

第4に、上述のように、生物処理による浄化率が低いの
で、大量の濾材4を必要とし、さらに、濾材4の逆洗処
理には、集水室5も必要となることから、大規模の反応
槽1を必要としていた。
Fourth, as mentioned above, since the purification rate by biological treatment is low, a large amount of filter media 4 is required, and furthermore, a water collection chamber 5 is also required for backwashing of the filter media 4. 1 reaction tank was required.

(ハ)発明の目的 本発明は、上述の問題を解決するためになされたもので
、その目的は、原水の生物処理と濾材の洗浄を同時に連
続して行なうことができ、原水の生物処理による浄化率
をアップし、逆洗ブロア。
(C) Purpose of the Invention The present invention has been made to solve the above-mentioned problems, and its purpose is to enable biological treatment of raw water and cleaning of filter media to be carried out simultaneously and continuously. Backwash blower increases purification rate.

逆洗ポンプ、大規模の処理水槽を廃止し、反応槽を小規
模にした下向流型生物膜浄化装置を提供することにある
The purpose of the present invention is to provide a downward flow type biofilm purification device in which a backwash pump and a large-scale treatment water tank are eliminated and the reaction tank is reduced in size.

仁)発明の構成 上記目的を達成するために、本発明は、濾材を充填した
浄化槽と、浄化槽内に設けられ酸素を供給する散気装置
と、生物処理された処理水を集める集水室と、集水室と
連通ずる処理水管と、浄化槽の垂直方向にエアリフト管
を配し、このエアリフト管の下端から原水の生物処理に
よって固形物が付着した濾材を吸い込むと共にエアリフ
ト管内で固形物を濾材から剥離させながら固形物と濾材
を同時に上昇させるエアリフト装置と、エアリフト管上
端に設けられ濾材と固形物を分離し濾材を浄化槽内へ循
環する分離装置と、この分離装置から固形物を排出する
排出管とから構成されているものである。
Structure of the Invention In order to achieve the above object, the present invention comprises a septic tank filled with a filter medium, an aeration device provided in the septic tank to supply oxygen, and a water collection chamber for collecting biologically treated treated water. A treatment water pipe that communicates with the water collection chamber and an air lift pipe are placed vertically in the septic tank, and from the lower end of the air lift pipe, filter media with solids attached due to the biological treatment of raw water are sucked in, and the solids are removed from the filter media within the air lift pipe. An airlift device that lifts solids and filter media simultaneously while peeling them off, a separation device installed at the upper end of the airlift pipe that separates the filter media and solids and circulates the filter media into the septic tank, and a discharge pipe that discharges the solids from this separation device. It is composed of.

(ホ)発明の実施例 以下、図面により本発明の実施例を詳細に説明する。(E) Examples of the invention Embodiments of the present invention will be described in detail below with reference to the drawings.

第1図は本発明の第1実施例に係る下向流型生物膜浄化
装置を示す。
FIG. 1 shows a downward flow type biofilm purification device according to a first embodiment of the present invention.

図示のように、本実施例に係る下向流型生物膜浄化装置
21は、濾材22を充填した浄化槽23と、浄化槽23
内に設けられ酸素を供給する散気装置24と、生物処理
された処理水を集める集水室25と、集水室25に接続
した処理水管26と、浄化槽23の垂直方向にエアリフ
ト管27を配し、エアリフト管27の下&1i127a
から原水の生物処理によって固形物が付着した濾材22
を吸い込むと共にエアリフト管27内で固形物を濾材2
2から剥離させながら固形物と濾材22を同時に上昇さ
せるエアリフト装置28と、エアリフト管27の上端2
7bに設けられ濾材22と固形物を分離し濾材22を浄
化槽23内に循環する分離装置29と、この分離装置2
9から固形物を排出する排出管30とから構成されてい
る。
As shown in the figure, the downward flow type biofilm purification device 21 according to the present embodiment includes a septic tank 23 filled with a filter medium 22, and a septic tank 23 filled with a filter medium 22.
An air diffuser 24 installed inside the tank to supply oxygen, a water collection chamber 25 that collects biologically treated water, a treated water pipe 26 connected to the water collection room 25, and an air lift pipe 27 installed in the vertical direction of the septic tank 23. Placed under the air lift pipe 27 & 1i127a
Filter media 22 with solid matter attached to it through biological treatment of raw water
At the same time, the solid matter is removed from the filter medium 2 in the air lift pipe 27.
an air lift device 28 that simultaneously lifts the solids and the filter medium 22 while peeling them from the air lift pipe 27;
7b, a separation device 29 that separates the filter medium 22 and solid matter and circulates the filter medium 22 into the septic tank 23;
9 and a discharge pipe 30 for discharging solid matter.

濾材22としては例えばアンスラサイト、活性炭、軽量
骨材等が用いられ、その粒径は2〜10額程度である。
As the filter medium 22, for example, anthracite, activated carbon, lightweight aggregate, etc. are used, and the particle size thereof is about 2 to 10 centimeters.

浄化槽23内にはこの濾材22によって濾過層22 a
が形成されている。浄化槽23の底部23aは円錐形状
となっている。これは固形物の付着した濾材22を滞留
させることなくすべてエアリフト管27に吸い込むため
である。
A filtration layer 22a is formed in the septic tank 23 by this filter material 22.
is formed. The bottom 23a of the septic tank 23 has a conical shape. This is to ensure that all of the filter medium 22 with solid matter attached to it is sucked into the air lift pipe 27 without stagnation.

集水室25はエアリフト管27の下方部においてエアリ
フト管27と一体に設けられている。集水室25は開口
部25aを有する椀型の容器である。
The water collection chamber 25 is provided integrally with the air lift pipe 27 at a lower portion of the air lift pipe 27. The water collection chamber 25 is a bowl-shaped container having an opening 25a.

この集水室25は断面多角形のコツプ状の容器とするこ
ともできる。処理水管26は集水室25から浄化槽23
の底部23aを貫通して浄化槽23の外部に配されてい
る。集水室25に集められた処理水は、水位差によって
処理水槽31に上昇するようになっている。散気装置2
4ば集水室25の上部に設けられている。このため、酸
素が平均に濾材22に供給され濾材22の表面には微生
物が付着成育している。エアリフト管27はその下端2
7aを浄化槽23の底部23aに位置させると共に、そ
の上端27bを浄化槽23の上部に位置させている。エ
アリフト管27の下端27aには、エアリフト用空気を
供給するエア装置28aがエアリフト管27とL字形状
を形成するように接続されている。分離装置29は、濾
材22を通さない程度の網目を有する例えばスリット・
パンチ穴の如き金網状の傾斜面29cを備えた円錐台形
状の中空構造部29aと、遮蔽板29bとから構成され
ている。遮蔽板29bは濾材22と固形物を中空構造部
29aの傾斜面29cに沿って流すためのものである。
The water collection chamber 25 can also be a cup-shaped container with a polygonal cross section. The treated water pipe 26 is connected from the water collection chamber 25 to the septic tank 23.
The septic tank 23 is disposed outside the septic tank 23 by penetrating the bottom 23a thereof. The treated water collected in the water collection chamber 25 rises to the treated water tank 31 due to the water level difference. Air diffuser 2
4 is provided above the water collection chamber 25. Therefore, oxygen is evenly supplied to the filter medium 22, and microorganisms adhere to and grow on the surface of the filter medium 22. The air lift pipe 27 has its lower end 2
7a is located at the bottom 23a of the septic tank 23, and its upper end 27b is located at the top of the septic tank 23. An air device 28a that supplies air for air lift is connected to the lower end 27a of the air lift pipe 27 so as to form an L-shape with the air lift pipe 27. The separation device 29 has a mesh that does not allow the filter medium 22 to pass through, for example, a slit or a mesh.
It is composed of a truncated conical hollow structure 29a having a wire mesh-like inclined surface 29c such as a punch hole, and a shielding plate 29b. The shielding plate 29b is for allowing the filter medium 22 and solid matter to flow along the inclined surface 29c of the hollow structure 29a.

遮蔽板29bは、保守点検を考慮して円筒体となってい
る。排出管30から処理水の一部と共に排出する固形物
の量は、エア装置28aの空気量の調節2分離装置29
の金網の面積の大小、排出管30のバルブ等の取付等に
よって行なうことができる。
The shielding plate 29b has a cylindrical shape in consideration of maintenance and inspection. The amount of solids discharged from the discharge pipe 30 together with a portion of the treated water is determined by adjusting the amount of air in the air device 28a and separating device 29.
This can be done by changing the area of the wire mesh, installing a valve, etc. on the discharge pipe 30, etc.

以上のような構成によって生じた本実施例の作用を次に
説明する。
The effects of this embodiment resulting from the above configuration will be described next.

浄化槽23内に充填された濾材22には、散気袋Ft 
24によって曝気用空気が供給され、濾材22表面には
微生物が付着成育した状態になっている。浄化槽23の
上部より図示しない流入管によって供給された原水は濾
過ii 22 aを通過する。
The filter medium 22 filled in the septic tank 23 is equipped with an aeration bag Ft.
Aeration air is supplied by 24, and microorganisms are attached and grown on the surface of the filter medium 22. Raw water supplied from the upper part of the septic tank 23 through an inflow pipe (not shown) passes through the filtration ii 22 a.

原水中に含まれるSS成分及びBOD成分等は微生物の
好気性生物処理によって酸化分解され、その結果、濾材
22表面には固形物が付着蓄積する。そして、原水中の
固形物及び生物処理により発生した固形物は、濾材22
表面あるいは濾材22間に捕集されており、捕集された
まま、濾過N 22 aの下層へ移動していき、エアリ
フト管27より分離装置29へ導かれる。そのため、処
理水中の固形物混入が少なく、通常の接触酸化法、活性
汚泥法、散水濾床法等で必要な沈澱池が不要となる。
SS components, BOD components, etc. contained in the raw water are oxidized and decomposed by aerobic biological treatment by microorganisms, and as a result, solid matter adheres and accumulates on the surface of the filter medium 22. The solids in the raw water and the solids generated by biological treatment are removed from the filter medium 22.
It is collected on the surface or between the filter media 22, moves to the lower layer of the filter N 22 a while being collected, and is led to the separation device 29 through the air lift pipe 27. Therefore, there is less solid matter mixed into the treated water, and a settling tank, which is required in normal contact oxidation methods, activated sludge methods, trickling filter methods, etc., is not required.

原水は濾過層22aを通過する際に浄化されつつ、重力
作用及びエアリフト装置28によって生じたエアリフト
管27の下端27aへの吸込力によって浄化槽23の上
部から下向きに流れる。濾過層22aによって浄化され
た処理水は浄化槽23の底部23aに向かって流れるが
、浄化槽23の下部には集水室25が設けられているの
で、処理水の一部はエアリフト管27の下端27aに吸
い込まれるが、多くは空間部分となっている集水室25
に吸い込まれる。この際、集水室25は、適当な側面部
25bの長さを持ち、又、処理水管流入部26aが適当
な高さにセットしてあれば濾材22が処理水管26に入
り込む余地はない。集水室25に蓄水した処理水は、処
理水管26を介して水位差によって処理水槽31内に導
かれる6一方、固形物の付着した濾材22は、エア装置
28aから吹き込まれたエアリフト用空気により、エア
リフト管27の下端27aより吸い込まれてエアリフト
管27内を上昇する。エアリフト管27内を濾材22.
処理水の一部、空気が上昇するため、濾材22に付着し
た固形物は、攪拌され、濾材22から分離される。この
分離した固形物。
The raw water is purified as it passes through the filtration layer 22a, and flows downward from the upper part of the septic tank 23 due to the action of gravity and the suction force generated by the air lift device 28 to the lower end 27a of the air lift pipe 27. The treated water purified by the filtration layer 22a flows toward the bottom 23a of the septic tank 23, but since the water collection chamber 25 is provided at the bottom of the septic tank 23, a part of the treated water flows to the lower end 27a of the air lift pipe 27. The water is sucked into the water collection chamber 25, which is mostly a space.
be sucked into. At this time, if the water collection chamber 25 has an appropriate length of the side surface portion 25b and the treated water pipe inflow portion 26a is set at an appropriate height, there is no room for the filter medium 22 to enter the treated water pipe 26. The treated water stored in the water collection chamber 25 is guided into the treated water tank 31 via the treated water pipe 26 due to the difference in water level 6 On the other hand, the filter medium 22 with solid matter adhered to the air lift air blown from the air device 28a. As a result, the air is sucked in from the lower end 27a of the air lift pipe 27 and rises inside the air lift pipe 27. Filter medium 22.
Since a portion of the treated water, air, rises, solid matter adhering to the filter medium 22 is stirred and separated from the filter medium 22. This separated solid matter.

濾材22.処理水の一部はエアリフト管27を上昇して
、エアリフト管27の上端27bから分離装置29に排
出される。この時、固形物、濾材22、処理水の一部(
通常この処理水は逆洗水と呼ばれる)は分離装置29の
遮蔽板29bによって遮られ、中空構造部29aの傾斜
面29cに沿って流れる。エアリフト管27内で洗浄さ
れた濾材22は、分離装置29の金網状の傾斜面29C
によって篩にかけられ、浄化槽23内に循環する。
Filter medium 22. A portion of the treated water rises up the air lift pipe 27 and is discharged from the upper end 27b of the air lift pipe 27 to the separation device 29. At this time, the solid matter, filter medium 22, and part of the treated water (
This treated water (usually called backwash water) is blocked by the shielding plate 29b of the separation device 29 and flows along the inclined surface 29c of the hollow structure 29a. The filter medium 22 washed in the air lift pipe 27 is transferred to the wire mesh-like inclined surface 29C of the separation device 29.
is passed through a sieve and circulated into the septic tank 23.

固形物は分離装置29の中空構造部29a内に逆洗水と
共に入り込む。この固形物は、逆洗水と共に逆洗排水と
なる。この逆洗排水は、排水管30によって排出される
The solids enter the hollow structure 29a of the separator 29 together with the backwash water. This solid matter becomes backwash waste water together with backwash water. This backwash waste water is discharged through a drain pipe 30.

浄化装置21より排水された逆洗排水の処理を第3図に
よって説明する。
The treatment of backwash wastewater discharged from the purification device 21 will be explained with reference to FIG.

逆洗排水は、逆洗排水沈澱池33へ導かれる。The backwash wastewater is guided to a backwash wastewater sedimentation tank 33.

逆洗排水沈澱池33に於て、逆洗排水中の沈降した汚泥
は、汚泥骨として逆洗排水沈澱池33の排出口33.+
から引き抜かれ、分離処理される6逆洗排水沈澱池33
中の上澄水は、原水槽34に供給される。この上澄水は
、原水槽34に供給された排水と共に原水槽34から浄
化槽23に原水として循環供給される。
In the backwash wastewater sedimentation tank 33, the settled sludge in the backwash wastewater is treated as sludge bones at the discharge port 33 of the backwash wastewater sedimentation tank 33. +
6 backwash wastewater sedimentation basin 33
The supernatant water inside is supplied to the raw water tank 34. This supernatant water is circulated and supplied as raw water from the raw water tank 34 to the septic tank 23 together with the waste water supplied to the raw water tank 34.

以上の構成に係る下向流型生物膜浄化装置21によれば
、次の効果を生じる。
According to the downward flow type biofilm purification device 21 having the above configuration, the following effects are produced.

第1に、原水の浄化処理とエアリフト管内で濾材22の
洗浄処理とを同時に連続して行なうことができる。この
結果、本発明による下向流型生物膜浄化装置21の稼動
率は向上し、しかも1基の該装置21で浄化処理の稼動
を止めることなく、連続使用できると共に装置を大型に
する必要がなくなった。
First, the purification treatment of raw water and the cleaning treatment of the filter medium 22 within the air lift tube can be performed simultaneously and continuously. As a result, the operating rate of the downward flow biofilm purification device 21 according to the present invention is improved, and one device 21 can be used continuously without stopping the purification process, and there is no need to increase the size of the device. lost.

第2に、上述の如く、原水の浄化処理と同時に濾材22
の洗浄処理が行なわれている。従って、洗浄された濾+
A22には固形物の付着している量が少なく、従って生
物処理による浄化率が向上する。
Second, as mentioned above, at the same time as the raw water is purified, the filter medium 22
A cleaning process is being carried out. Therefore, the washed filter +
The amount of solid matter adhering to A22 is small, so the purification rate by biological treatment is improved.

例えば、本実施例ではBOD負荷を次表の如く採った装
置に対して、原水の水質は次表の如き結果を得ている。
For example, in this embodiment, for a device whose BOD load was taken as shown in the table below, the quality of raw water was obtained as shown in the table below.

第3に、濾材22の洗浄が、エアリフト管27内で行な
われ、濾材22は、分離装置29で固形物と分離され、
洗浄された濾材22が浄化槽23内に循環する。従って
、従来例で必要とした濾材22の洗浄のための逆洗ブロ
ア、逆洗ポンプ、大規模な処理水槽、さらに、それらに
付属する自動弁類等が不要となった。
Thirdly, cleaning of the filter medium 22 is performed in the air lift tube 27, and the filter medium 22 is separated from solids in a separator 29,
The washed filter medium 22 is circulated into the septic tank 23. Therefore, there is no need for a backwash blower, a backwash pump, a large-scale treatment water tank, and the automatic valves attached thereto for cleaning the filter medium 22, which were required in the conventional example.

第4に、上述の如く、生物処理による浄化率が高いので
、処理すべき原水に対して濾材22の必要とする量も少
なくなり、さらに、従来例に於ける集水室も不要となる
ことから、浄化槽も小規模とすることができる。
Fourthly, as mentioned above, since the purification rate by biological treatment is high, the amount of filter media 22 required for the raw water to be treated is reduced, and furthermore, the water collection chamber in the conventional example is not required. Therefore, the septic tank can also be made smaller.

第5に、固形物と濾材22とは分離装置29の金網状等
の傾斜面29cによって篩にかけられる結果、固形物は
逆洗水と共に中空構造部29aの内部に入り込み、浄化
槽23内に循環することはない。従って、浄化槽23内
の処理水の中には分離装置29によって固形物が混入す
る虞が解消される。
Fifth, as a result of the solid matter and the filter medium 22 being sieved by the inclined surface 29c of the separator 29 such as a wire mesh, the solid matter enters the inside of the hollow structure 29a together with the backwash water and circulates into the septic tank 23. Never. Therefore, the possibility that solid matter will be mixed into the treated water in the septic tank 23 due to the separation device 29 is eliminated.

第6に、エアリフト管27の上端27aから排出した濾
材22は、分離装置29の傾斜面29c上でお互いに擦
られつつ浄化槽23に循環する。
Sixthly, the filter medium 22 discharged from the upper end 27a of the air lift pipe 27 is circulated to the septic tank 23 while being rubbed against each other on the inclined surface 29c of the separation device 29.

従って、固形物は分離装置29内においても濾材22か
ら剥離される。
Therefore, the solid matter is also separated from the filter medium 22 within the separator 29.

b 第7に、分離装置29でば、・濾材22と固形物は金網
状等の傾斜面29Cを介して物理的に分離されるので、
分離装置29に振動装置を取り付けることが可能になり
、分離速度を速めることができる。
b Seventhly, in the separation device 29, the filter medium 22 and the solid matter are physically separated via the inclined surface 29C, such as a wire mesh, so that
It becomes possible to attach a vibration device to the separation device 29, and the separation speed can be increased.

第8に、濾材22は分離装置29の網状の傾斜面29c
で篩をかけられるから、中空構造物29a内に固形物と
共に混入する虞はなくなり、無駄なく浄化槽23内に循
環する。
Eighth, the filter medium 22 is a net-like inclined surface 29c of the separation device 29.
Since the solids are sieved by the filter, there is no possibility that the solids will be mixed into the hollow structure 29a, and the solids are circulated into the septic tank 23 without waste.

第9に、通常の接触酸化法、活性汚泥法、散水濾床法等
で必要な沈澱池が不要となる。
Ninth, a settling tank, which is required in the usual catalytic oxidation method, activated sludge method, trickling filter method, etc., is not required.

次に、本発明の第2実施例に係る下向流型生物膜浄化装
置を第4図によって説明する。
Next, a downward flow type biofilm purification device according to a second embodiment of the present invention will be explained with reference to FIG. 4.

図示のように、本実施例に係る下向流型生物膜浄化装置
21Aは、濾材22Aを充填した浄化槽23Aと、浄化
槽23A内に設けられ酸素を供給する散気装W24Aと
、生物処理された処理水を集める集水室25A、25A
、25A、25A。
As shown in the figure, the downward flow biofilm purification device 21A according to the present embodiment includes a septic tank 23A filled with a filter medium 22A, a diffuser W24A installed in the septic tank 23A to supply oxygen, and a biologically treated biofilm purifier 21A. Water collection chambers 25A and 25A that collect treated water
, 25A, 25A.

25Aと、各集水室25Aに接続した処理水管26Aと
、浄化槽23Aの垂直方向に5個のエアリフ ト を配し、各エアリフト管27Aの各下端27bから原水
の生物処理によって固形物が付着した濾材22Aを吸い
込むと共に各エアリフト管27A内で固形物を濾材22
Aから剥離させながら固形物と濾材22Aを同時に上昇
させるエアリフト装置28A,  28A,  28A
,  28A,  28A’と、各エアリフト管27A
の各上端27Cに設けられ濾材22Aと固形物を分離し
濾材22Aを浄化槽23A内に循環する分離装置29A
,29A,29A,29A,29Aと、各分離装置29
Aから固形物を排出する排気管30Aとから構成されて
いる。
25A, treated water pipes 26A connected to each water collection chamber 25A, and five air lifts arranged in the vertical direction of the septic tank 23A, from each lower end 27b of each air lift pipe 27A to filter media to which solid matter has been attached due to biological treatment of raw water. 22A and solids are removed from the filter medium 22 in each air lift pipe 27A.
Air lift devices 28A, 28A, 28A that simultaneously lift solids and filter media 22A while separating them from A
, 28A, 28A' and each air lift pipe 27A
A separation device 29A is provided at each upper end 27C of the filter medium 22A to separate the solid matter from the filter medium 22A and circulate the filter medium 22A into the septic tank 23A.
, 29A, 29A, 29A, 29A and each separation device 29
It is composed of an exhaust pipe 30A for discharging solid matter from A and an exhaust pipe 30A.

第2実施例によれば、第1実施例の効果に加えて、大量
の原水の浄化が可能となる効果を奏する。
According to the second embodiment, in addition to the effects of the first embodiment, it is possible to purify a large amount of raw water.

なお、第1実施例に於ては、処理水管26の取入口26
aは、集水室25の内側に導かれているが、第5図に示
すように、処理水管26を集水室25の側面部25aに
連結することも可能である。
In addition, in the first embodiment, the intake port 26 of the treated water pipe 26
Although the pipe a is guided inside the water collection chamber 25, it is also possible to connect the treated water pipe 26 to the side surface 25a of the water collection chamber 25, as shown in FIG.

第2実施例に於ても、その態様が具体的に示されている
The second embodiment also specifically shows this aspect.

又、第1実施例、第2実施例によれば、集水室25.2
5Aとエアリフト管27.27Aは一体となっているが
、第6図に示すように、集水室25Bを略ドーナツ状の
空間とし、このドーナツ状空間の中心部35にエアリフ
ト管27を集水室25Bと別体に配置することも可能で
ある。この場合、処理水管26は、集水室25Bの側面
部を構成する浄化槽23と連結されている。
Further, according to the first embodiment and the second embodiment, the water collection chamber 25.2
5A and the air lift pipe 27.27A are integrated, but as shown in FIG. 6, the water collection chamber 25B is formed into a substantially doughnut-shaped space, and the air lift pipe 27 is placed in the center 35 of this doughnut-shaped space to collect water. It is also possible to arrange it separately from the chamber 25B. In this case, the treated water pipe 26 is connected to the septic tank 23 that forms the side surface of the water collection chamber 25B.

さらに、原水中に浮上性物質が多く、スカムが発生する
場合には浄化槽23上部にスカム取出しノズル32を設
け、これにより定期的にスカムを排出することもできる
。排出後のスカムは通常逆洗排水と混合し、逆洗排水沈
澱池33で処理される。
Furthermore, if there are many floating substances in the raw water and scum is generated, a scum removal nozzle 32 may be provided at the top of the septic tank 23, thereby making it possible to periodically discharge the scum. The scum after discharge is usually mixed with backwash wastewater and treated in a backwash wastewater sedimentation tank 33.

又、本実施例では、エアリフト管27は浄化槽23内に
設けられているが、その吸込口を浄化槽23内に設ける
と共に、L字状の管体で構成し、浄化槽23を貫通して
浄化槽外に配し、さらに、分解装置29をも浄化槽23
外に配することも可能である。
In addition, in this embodiment, the air lift pipe 27 is provided inside the septic tank 23, but its suction port is provided inside the septic tank 23, and it is constructed of an L-shaped pipe body and penetrates through the septic tank 23 to the outside of the septic tank. Furthermore, the decomposition device 29 is also installed in the septic tank 23.
It is also possible to arrange it outside.

さらに、第1実施例及び第2実施例では、エアリフト用
空気を供給するエア装置28aが、エアリフト管27.
27Aの下端27a、27bでエアリフト管27.27
Aと釜1字形状を形成するように接続されているが、第
7図に示すように、エアリフト管27.27Aと一体に
エア装置35を垂直に設けることも可能である。空気は
エアリフト管27.27Aの最」口端35aから供給さ
れている。
Furthermore, in the first and second embodiments, the air device 28a that supplies air for air lift is the air lift pipe 27.
Air lift tube 27.27 at the lower end 27a, 27b of 27A
Although the air device 35 is connected to the air lift pipe 27, 27A so as to form a hook shape, as shown in FIG. Air is supplied from the most open end 35a of the air lift tube 27.27A.

又、エア装置とエアリフト管を一体にした態様として、
第8図〜第9図に示す例が挙げられる。
In addition, as an embodiment in which the air device and air lift pipe are integrated,
Examples shown in FIGS. 8 to 9 are given.

即ち、第8図、第9図に示すように、エアリフト管27
.27Aの外周に同心円状にエア装置35Aが配されて
いる。この場合、第10図に示すようにエア装置35A
を構成する垂直管の中間部36に空気供給口37を設げ
ることもできる。
That is, as shown in FIGS. 8 and 9, the air lift pipe 27
.. An air device 35A is arranged concentrically around the outer periphery of 27A. In this case, as shown in FIG.
It is also possible to provide an air supply port 37 in the middle part 36 of the vertical tube constituting the pipe.

(へ)発明の効果 以上述べたように、本発明によれば、第1に、原水の生
物処理と濾材の洗浄を同時に連続して行なうことができ
、第2に、原水の生物処理による浄化率を向上すること
ができ、第3に、逆洗ブロア、逆洗ポンプ、大規模な処
理水槽等が不要となり、第4に、浄化槽を小さくするこ
とができ、第5に、処理水の中に固形物が混入する虞を
解消することができ、第6に、分離装置によっても固形
物を濾材から剥離する力を与えることができ、第7に、
分離装置に振動装置を取り付けることを可能にし、第8
に、濾材を浄化槽内へ無駄なく循環させることができ、
第9に、通常の接触酸化法等で必要な沈澱池を廃止でき
るという効果を奏する。
(F) Effects of the Invention As described above, according to the present invention, firstly, biological treatment of raw water and cleaning of filter media can be carried out simultaneously and continuously, and secondly, biological treatment of raw water can be performed. Thirdly, there is no need for backwash blowers, backwash pumps, large-scale treatment water tanks, etc., fourthly, the septic tank can be made smaller, and fifthly, Sixthly, the separation device can also provide a force to separate the solids from the filter medium, and seventhly,
It is possible to attach a vibration device to the separation device, and the eighth
In addition, the filter media can be circulated into the septic tank without waste.
Ninthly, it is possible to eliminate the settling tank required in ordinary catalytic oxidation methods.

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

第1図は本発明の第1実施例に係る下向流型生物膜浄化
装置の断面構成図、第2図は第1図のA−A断面矢視図
、第3図は同生物膜浄化装置の使用状態説明図、第4図
は本発明の第2実施例に係る下向流型生物膜浄化装置の
断面構成図、第5図は処理水管の他の接続方法を示す断
面図、第6図は集水室の他の例を示す断面図、第7図は
エア装置の他の実施態様を示す断面図、第8図はエア装
置のさらに他の実施態様を示す部分図、第9図は第8図
のB−B断面図、第10図はエア装置に於けるエアの供
給位置を説明する説明図、第11図は従来における下向
流型生物膜浄化装置の断面構成図である。 21・・・第1実施例に係る下向流型生物膜浄化装置、
22・・・濾材、22a・・・濾過層、23・・・浄化
槽、24・・・散気装置、25・・・集水室、25a・
・・開口部、26・・・処理水管、26a・・・取入口
、27・・・エアリフト管、28・・・エアリフト装置
、29・・・分離装置、29a・・・中空構造部、29
C・・・傾斜面、30・・・排水管、31・・・処理水
槽。 第8図 第10図 第9図 27 、27A
FIG. 1 is a cross-sectional configuration diagram of a downward flow type biofilm purification device according to the first embodiment of the present invention, FIG. 2 is a cross-sectional view taken along the line A-A in FIG. 1, and FIG. FIG. 4 is a cross-sectional configuration diagram of the downward flow type biofilm purification device according to the second embodiment of the present invention. FIG. 5 is a cross-sectional diagram showing another method of connecting treated water pipes. 6 is a sectional view showing another example of the water collection chamber, FIG. 7 is a sectional view showing another embodiment of the air device, FIG. 8 is a partial view showing still another embodiment of the air device, and FIG. 9 is a sectional view showing another embodiment of the air device. The figure is a cross-sectional view taken along line B-B in Figure 8, Figure 10 is an explanatory diagram explaining the air supply position in the air device, and Figure 11 is a cross-sectional diagram of a conventional downward flow type biofilm purification device. be. 21...Downward flow type biofilm purification device according to the first embodiment,
22... Filter medium, 22a... Filter layer, 23... Septic tank, 24... Air diffuser, 25... Water collection room, 25a.
... Opening section, 26 ... Treated water pipe, 26a ... Intake port, 27 ... Air lift pipe, 28 ... Air lift device, 29 ... Separation device, 29a ... Hollow structure section, 29
C... Inclined surface, 30... Drain pipe, 31... Treatment water tank. Figure 8 Figure 10 Figure 9 Figure 27, 27A

Claims (12)

【特許請求の範囲】[Claims] (1)濾材を充填した浄化槽と、浄化槽内に設けられ酸
素を供給する散気装置と、生物処理された処理水を集め
る集水室と、集水室と連通する処理水管と、浄化槽の垂
直方向にエアリフト管を配し、このエアリフト管の下端
から原水の生物処理によって固形物が付着した濾材を吸
い込むと共にエアリフト管内で固形物を濾材から剥離さ
せながら固形物と濾材を同時に上昇させるエアリフト装
置と、エアリフト管の上端に設けられ濾材と固形物を分
離し濾材を浄化槽内へ循環する分離装置と、この分離装
置から固形物を排出する排出管とから構成されているこ
とを特徴とする下向流型生物膜浄化装置。
(1) A septic tank filled with filter media, an aeration device installed in the septic tank to supply oxygen, a water collection chamber for collecting biologically treated water, a treated water pipe communicating with the water collection room, and a vertical wall of the septic tank. An air lift device in which an air lift tube is disposed in the direction of the air lift tube, and the filter medium to which solid matter has adhered due to biological treatment of raw water is sucked in from the lower end of the air lift tube, and the solid matter and the filter medium are lifted simultaneously while peeling the solid matter from the filter medium within the air lift tube. , a downward-directing device comprising a separation device installed at the upper end of the air lift tube to separate the filter medium and solids and circulate the filter medium into the septic tank, and a discharge pipe to discharge the solids from the separation device. Flow-type biofilm purification device.
(2)エアリフト管は、浄化槽内に設けられていること
を特徴とする特許請求の範囲第1項記載の下向流型生物
膜浄化装置。
(2) The downward flow type biofilm purification device according to claim 1, wherein the air lift pipe is provided in a septic tank.
(3)エアリフト管と集水室は一体となっていることを
特徴とする特許請求の範囲第2項記載の下向流型生物膜
浄化装置。
(3) The downward flow type biofilm purification device according to claim 2, wherein the air lift pipe and the water collection chamber are integrated.
(4)エアリフト管と集水室は別体となっていることを
特徴とする特許請求の範囲第2項記載の下向流型生物膜
浄化装置。
(4) The downward flow type biofilm purification device according to claim 2, wherein the air lift pipe and the water collection chamber are separate bodies.
(5)エアリフト管は、直線状の管体であり、その吸込
口が浄化槽内に設けられていることを特徴とする特許請
求の範囲第1項記載の下向流型生物膜浄化装置。
(5) The downward flow type biofilm purification device according to claim 1, wherein the air lift pipe is a straight pipe body, and the suction port thereof is provided in the septic tank.
(6)エアリフト管は、L字状の管体であり、その吸込
口が浄化槽内に設けられていることを特徴とする特許請
求の範囲第1項記載の下向流型生物膜浄化装置。
(6) The downward flow type biofilm purification device according to claim 1, wherein the air lift pipe is an L-shaped pipe body, and the suction port thereof is provided in the septic tank.
(7)エア装置は、エアリフト管と別体に構成され、エ
アリフト管の下端部に接続していることを特徴とする特
許請求の範囲第1項記載の下向流型生物膜浄化装置。
(7) The downward flow type biofilm purification device according to claim 1, wherein the air device is configured separately from the air lift pipe and is connected to the lower end of the air lift pipe.
(8)エア装置は、エアリフト管と一体になっているこ
とを特徴とする特許請求の範囲第1項記載の下向流型生
物膜浄化装置。
(8) The downward flow biofilm purification device according to claim 1, wherein the air device is integrated with an air lift pipe.
(9)エア装置は、エアリフト管の外側に同心円状に配
されていることを特徴とする特許請求の範囲第7項記載
の下向流型生物膜浄化装置。
(9) The downward flow biofilm purification device according to claim 7, wherein the air device is arranged concentrically outside the air lift tube.
(10)集水室は、開口部を有する椀型又は断面多角形
のコップ状の容器であり、開口部は下向に成ると共に椀
型又は断面多角形のコップ状の容器内部には処理水管の
取入口が導かれていることを特徴とする特許請求の範囲
第1項記載の下向流型生物膜浄化装置。
(10) The water collection chamber is a bowl-shaped or cup-shaped container with a polygonal cross section and has an opening, and the opening faces downward and a treated water pipe is installed inside the bowl-shaped or polygonal cross-sectional cup-shaped container. 2. A downward flow type biofilm purification device according to claim 1, wherein the intake port is guided.
(11)分離装置には、濾材を通さない程度の網目を有
する金網状の傾斜面を備えた中空構造部が設けられてい
ることを特徴とする特許請求の範囲第1項記載の下向流
型生物膜浄化装置。
(11) The downward flow according to claim 1, characterized in that the separation device is provided with a hollow structure having a wire mesh-like sloped surface having a mesh that does not allow the filter medium to pass through. Type biofilm purification device.
(12)分離装置には、濾材を通さない程度のスリット
パンチ孔を有する傾斜面を備えた中空構造部が設けられ
ていることを特徴とする特許請求の範囲第1項記載の下
向流型生物膜浄化装置。
(12) The downward flow type according to claim 1, characterized in that the separation device is provided with a hollow structure having an inclined surface having slit punch holes that do not allow the filter medium to pass through. Biofilm purification device.
JP60131064A 1985-06-17 1985-06-17 Downward flow type biological membrane purifying apparatus Granted JPS61291099A (en)

Priority Applications (5)

Application Number Priority Date Filing Date Title
JP60131064A JPS61291099A (en) 1985-06-17 1985-06-17 Downward flow type biological membrane purifying apparatus
KR1019850007706A KR890004193B1 (en) 1985-06-17 1985-10-18 Apparatus for biological purification of waste water by using submerged filter
FR8604588A FR2583406B1 (en) 1985-06-17 1986-04-01 BIOLOGICAL PURIFIER WITH MEMBRANE OF THE DOWNFLOW TYPE FOR BIOLOGICAL TREATMENT OF WASTEWATER.
CH1866/86A CH667080A5 (en) 1985-06-17 1986-05-06 BIOLOGICAL PURIFIER WITH MEMBRANE OF THE DOWNFLOW TYPE.
SE8602501A SE467253B (en) 1985-06-17 1986-06-03 PURIFICATION DEVICE WITH BIOLOGICAL MEMBRANE AND DOWNLOADED FLOW

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60131064A JPS61291099A (en) 1985-06-17 1985-06-17 Downward flow type biological membrane purifying apparatus

Publications (2)

Publication Number Publication Date
JPS61291099A true JPS61291099A (en) 1986-12-20
JPH0232955B2 JPH0232955B2 (en) 1990-07-24

Family

ID=15049161

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60131064A Granted JPS61291099A (en) 1985-06-17 1985-06-17 Downward flow type biological membrane purifying apparatus

Country Status (5)

Country Link
JP (1) JPS61291099A (en)
KR (1) KR890004193B1 (en)
CH (1) CH667080A5 (en)
FR (1) FR2583406B1 (en)
SE (1) SE467253B (en)

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JPS63107798A (en) * 1986-06-19 1988-05-12 Ebara Infilco Co Ltd Organism filter
JP2010184210A (en) * 2009-02-13 2010-08-26 Best Plant Ltd Co Automatic cleaning device for floating filter medium layer for biofiltration treatment
CN102923842A (en) * 2012-11-14 2013-02-13 四川人福生物环保有限公司 Aerated biological filtration tank
CN103613188A (en) * 2013-12-02 2014-03-05 上海理工大学 Outside cycle continuous biological aerated filter for composite fillers
JP2020104052A (en) * 2018-12-27 2020-07-09 三機工業株式会社 Water treatment device
JP2020146664A (en) * 2019-03-15 2020-09-17 三機工業株式会社 Water treatment device

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FR2623794B1 (en) * 1987-12-01 1991-07-26 Sogea CONTINUOUS BIOLOGICAL PURIFICATION DEVICE OF THE UPWATER CIRCULATION TYPE
FR2626868B1 (en) * 1988-02-08 1990-06-08 Sogea METHOD AND DEVICE FOR REDUCING POLLUTION DISSOLVED IN A LIQUID
FR2694209B1 (en) * 1992-07-31 1994-10-28 Omnium Traitement Valorisa Chute type device for washing filters in biological water treatment.
US5232586A (en) * 1992-09-25 1993-08-03 Malone Ronald F Floating media hourglass biofilter
SE502856C2 (en) * 1993-06-23 1996-01-29 Nordic Water Prod Ab Method and apparatus for biological treatment of water
NL9302260A (en) * 1993-12-24 1995-07-17 Stork Friesland Bv Membrane bioreactor with gas-lift system.
SE504447C2 (en) * 1994-03-03 1997-02-10 Nordic Water Prod Ab Treatment of water in a biologically activated and continuously operating granular filter bed
NL9401439A (en) * 1994-05-27 1996-01-02 Shieer Globe Int Nv Method and device for the biochemical cleaning of a liquid medium.
DE69522944T2 (en) * 1994-07-21 2002-06-13 Knud Peter Brockdorff REACTOR FOR USE IN WATER TREATMENT WITH MICROFILM CARRIERS AND A METHOD FOR OPERATING THE REACTOR
NL9401669A (en) * 1994-10-10 1996-05-01 Boat Care Holland Bv Organic waste fluid cleaner.
DE102011009067A1 (en) 2011-01-20 2012-07-26 Bruno Moos Purifying a liquid medium having impurities comprises conducting liquid medium through a bed containing granular filter material, present in a container
CN202297249U (en) * 2011-10-12 2012-07-04 林长青 Inner-circulated anaerobic fluidize bed reactor
CN115432810B (en) * 2022-09-15 2023-07-07 盐城工学院 Water treatment device and water treatment method

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JPS5182961A (en) * 1975-01-17 1976-07-21 Hiroyuki Tsucha
JPS58114795A (en) * 1981-12-28 1983-07-08 Miyoshi Shokai:Kk Fluidized bed type treating device for sewage

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JPS58114795A (en) * 1981-12-28 1983-07-08 Miyoshi Shokai:Kk Fluidized bed type treating device for sewage

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63107798A (en) * 1986-06-19 1988-05-12 Ebara Infilco Co Ltd Organism filter
JP2010184210A (en) * 2009-02-13 2010-08-26 Best Plant Ltd Co Automatic cleaning device for floating filter medium layer for biofiltration treatment
CN102923842A (en) * 2012-11-14 2013-02-13 四川人福生物环保有限公司 Aerated biological filtration tank
CN103613188A (en) * 2013-12-02 2014-03-05 上海理工大学 Outside cycle continuous biological aerated filter for composite fillers
JP2020104052A (en) * 2018-12-27 2020-07-09 三機工業株式会社 Water treatment device
JP2020146664A (en) * 2019-03-15 2020-09-17 三機工業株式会社 Water treatment device

Also Published As

Publication number Publication date
FR2583406A1 (en) 1986-12-19
CH667080A5 (en) 1988-09-15
JPH0232955B2 (en) 1990-07-24
SE467253B (en) 1992-06-22
KR870000246A (en) 1987-02-17
SE8602501D0 (en) 1986-06-03
FR2583406B1 (en) 1991-07-05
SE8602501L (en) 1986-12-18
KR890004193B1 (en) 1989-10-27

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