JPS6331280B2 - - Google Patents

Info

Publication number
JPS6331280B2
JPS6331280B2 JP1422981A JP1422981A JPS6331280B2 JP S6331280 B2 JPS6331280 B2 JP S6331280B2 JP 1422981 A JP1422981 A JP 1422981A JP 1422981 A JP1422981 A JP 1422981A JP S6331280 B2 JPS6331280 B2 JP S6331280B2
Authority
JP
Japan
Prior art keywords
packed bed
granular material
pipe
tank
biological treatment
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
JP1422981A
Other languages
Japanese (ja)
Other versions
JPS57130590A (en
Inventor
Katsuyuki Kataoka
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
Original Assignee
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 Infilco Co Ltd filed Critical Ebara Infilco Co Ltd
Priority to JP1422981A priority Critical patent/JPS57130590A/en
Publication of JPS57130590A publication Critical patent/JPS57130590A/en
Publication of JPS6331280B2 publication Critical patent/JPS6331280B2/ja
Granted 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

Landscapes

  • Biological Treatment Of Waste Water (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は有機性廃水を粒状材に付着した微生
物により処理する装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to an apparatus for treating organic wastewater using microorganisms attached to granular material.

〔従来の技術〕[Conventional technology]

従来の浸漬床装置はエアリフト管のある槽内
に、砂、アンスラサイトなどの粒状材の充填槽
を設け、エアリフトエアレーシヨンによつて前記
充填層への酸素供給と液の循環を行なつて有機性
廃水を処理するものが多用されている。
Conventional soaked bed equipment has a tank filled with granular materials such as sand or anthracite in a tank with an air lift pipe, and air lift aeration supplies oxygen to the packed bed and circulates the liquid. It is widely used to treat organic wastewater.

すなわち、第1図に示すように槽28内に形成
された支持床26上に粒状材を充填して浸漬充
填床24とし、これに原水21が下向流で流下
する間に、空気25が供給されるエアリフト管2
3内で溶解された酸素と浸漬充填床24内の微
生物の作用により好気性生物処理を受け、処理水
は槽28の上部にある処理水流出部22から系外
へ排出される構成となつていて、槽底に逆洗水配
管27を備えている。
That is, as shown in FIG. 1, a support bed 26 formed in a tank 28 is filled with granular material to form an immersed packed bed 24, and while raw water 21 flows downward, air 25 is Air lift tube 2 supplied
The treated water is subjected to aerobic biological treatment by the action of oxygen dissolved in the tank 3 and microorganisms in the immersed packed bed 24, and the treated water is discharged outside the system from the treated water outlet 22 located at the upper part of the tank 28. A backwash water pipe 27 is provided at the bottom of the tank.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

しかしながら、この従来装置では支持床26上
にある浸漬充填床24内を下向流で液を循環さ
せているため、原水21中のSSやBODの除去に
伴つて発生する微生物スライムによる目詰まりが
起こるので、定期的に原水21の流入を止め逆洗
水配管27からの逆洗水で浸漬充填床24を逆
洗しなければならず高SSあるいは高BODの原水
21に対しては不適であり、また適用範囲が狭い
ばかりか逆洗操作が必要なのでメンテナンスが面
倒であると共に、エアリフトによつて酸素供給を
行なつているのでエアレーシヨン動力効率が低
い、即ち、エアリフト管23内に高流速の上向流
が生じ、空気泡の上昇速度がこの上向流により加
速され空気泡の水中滞留時間が短くなるためで問
題であり、浸漬充填床24を支持する多孔板な
どの支持板26が必要なので、支持床26にも目
詰まりが発生するトラブルも多いし、従来では小
粒径の粒状材は短時間内に前記目詰まりのトラ
ブルが発生するので使用できず、したがつてやむ
を得ず粒径の大きな材を使用せざるを得なく良
質な処理水が安定して得られなかつた。
However, in this conventional device, since the liquid is circulated in a downward flow in the immersed packed bed 24 on the support bed 26, clogging due to microbial slime that occurs when SS and BOD in the raw water 21 is removed is avoided. Therefore, it is necessary to periodically stop the inflow of raw water 21 and backwash the immersed packed bed 24 with backwash water from the backwash water pipe 27, which is not suitable for raw water 21 with high SS or high BOD. Moreover, not only is the scope of application narrow, but maintenance is troublesome as backwashing is required, and the aeration power efficiency is low because oxygen is supplied by air lift. This is a problem because a countercurrent occurs and the rising speed of the air bubbles is accelerated by this upward flow, shortening the residence time of the air bubbles in the water, and a support plate 26 such as a perforated plate is required to support the submerged packed bed 24. There are also many troubles such as clogging of the support bed 26, and conventionally, small-sized granular materials cannot be used because the clogging problem occurs within a short period of time. As a result, high-quality treated water could not be stably obtained.

本発明は、これら従来の重大欠点をすべて適確
に解決できる有効な生物処理装置を提供すること
を目的とするものである。
An object of the present invention is to provide an effective biological treatment device that can appropriately solve all of these conventional serious drawbacks.

〔問題点を解決するための手段〕[Means for solving problems]

本発明は、下部に原水流入部と酸素含有気泡送
給部、上部に処理水流出部を設けた槽内の水面下
に比重1.0以上の粒状材で充填層を形成せしめ、
この充填層内下方部に下端が開口する材移送管
を垂直方向に設け、この材移送管の上端を充填
層界面より上方に開口配置すると共にその周囲
に、上端が水面上に突出した仕切壁で粒状材の
環流部を処理水流出部と区画して形成し、さらに
該環流部に粒状材と分離された洗浄排水を流出
させる洗浄排水流出管を配備し、かつ前記材移
送管下部に空気供給管を備え、供給される空気気
泡で前記粒状材を間欠的又は連続的に前記充填
層下方部より抜き出し、材移送管内に吸引し、
前記充填層の上方部に移送せしめつつ前記粒状
材を洗浄しながら環流部を経て充填層界面に循環
する構成としたことを特徴とする有機性廃水の生
物処理装置である。
The present invention forms a packed bed of granular material with a specific gravity of 1.0 or more under the water surface in a tank that has a raw water inlet and an oxygen-containing bubble feeder in the lower part and a treated water outlet in the upper part,
A material transfer pipe whose lower end is open is provided vertically in the lower part of the packed bed, and the upper end of this material transfer pipe is opened above the packed bed interface, and around it is a partition wall whose upper end protrudes above the water surface. A reflux part of the granular material is separated from a treated water outflow part, and a washing wastewater outflow pipe is provided in the reflux part for discharging washing wastewater separated from the granular material, and air is provided at the bottom of the material transfer pipe. comprising a supply pipe, the granular material is intermittently or continuously extracted from the lower part of the packed bed using supplied air bubbles, and is sucked into the material transfer pipe;
The biological treatment apparatus for organic wastewater is characterized in that the particulate material is circulated to the interface of the packed bed through a reflux part while being transferred to the upper part of the packed bed and while cleaning the particulate material.

〔実施例〕〔Example〕

本発明の実施例を第2図を参照しながら説明す
れば、処理槽3の底部に、多数の空気供給孔1
3′を有する円錐状(又は角錐状)の底部13が
設けられ、処理槽3の下端部中央には原水流入部
1が設けられている。また、底部13と処理槽3
の外壁3′により形成される空間部17には、充
填槽4の水平断面全体にわたつて均等に空気を散
気できるように散気管9が配備されている。
An embodiment of the present invention will be described with reference to FIG.
A conical (or pyramidal) bottom 13 having a diameter of 3' is provided, and a raw water inlet 1 is provided at the center of the lower end of the treatment tank 3 . In addition, the bottom part 13 and the processing tank 3
In the space 17 formed by the outer wall 3' of the filling tank 4, an aeration pipe 9 is arranged so as to diffuse air evenly over the entire horizontal cross section of the filling tank 4.

さらに、処理槽3内中央部に垂直方向に粒状
材の移送管としてのドラフトチユーブ5が、該ド
ラフトチユーブ5の下部周囲には砂、アンスラサ
イトなど比重が1.0以上の粒状材の充填層4が
充填層界面7の上部に空間部10を残すように形
成されている。前記ドラフトチユーブ5の上部は
充填層界面7よりも上方に出て開口されており、
ドラフトチユーブ5の下部は充填層4内に開口さ
れ、かつドラフトチユーブ5内にエアリフトを生
起させるための空気供給管11が接続されてい
る。
Furthermore, a draft tube 5 serving as a transfer pipe for granular material is provided vertically in the center of the treatment tank 3, and around the lower part of the draft tube 5, a packed bed 4 of granular material having a specific gravity of 1.0 or more, such as sand or anthracite, is provided. A space 10 is left above the filled layer interface 7. The upper part of the draft tube 5 is opened above the filled layer interface 7,
The lower part of the draft tube 5 is opened into the packed bed 4, and an air supply pipe 11 for generating an air lift is connected inside the draft tube 5.

さらに、前記ドラフトチユーブ5の上端開口に
は、原水1′がドラフトチユーブ5内をシヨート
パスしないようにするための弁12が開閉自在に
設けられ、その上端の開口部6を開閉できるよう
になつている。
Furthermore, a valve 12 is provided at the opening at the upper end of the draft tube 5 to prevent the raw water 1' from passing through the draft tube 5, so that the valve 12 can be opened and closed, and the opening 6 at the upper end can be opened and closed. There is.

なお、前記処理槽3には処理水流出部2と、散
気管9に接続された空気供給管8を備え、かつ粒
状材の還流部14を前記ドラフトチユーブ5の
上方部に設け、さらに洗浄排水流出管15と粒状
材洗浄後の洗浄排水が処理水流出部2へ流出す
るのを防止するための仕切壁16とを備えてい
る。
The treatment tank 3 is equipped with a treated water outflow part 2 and an air supply pipe 8 connected to an aeration pipe 9, and a particulate material return part 14 is provided in the upper part of the draft tube 5. It is provided with an outflow pipe 15 and a partition wall 16 for preventing washing wastewater after washing the granular material from flowing out to the treated water outflow section 2.

即ち、前記充填層4内の下方部に下端が開口す
るドラフトチユーブ5を垂直方向に設け、このド
ラフトチユーブ5の上端を充填層界面7より上方
に開口配置すると共にその周囲に、上端が水面上
に突出した仕切壁16で粒状材の環流部14を
処理水流出部2と区画して形成し、さらに該環流
部14に粒状材と分離された洗浄排水を流出さ
せる洗浄排水流出管15を配備し、かつ前記ドラ
フトチユーブ5下部に空気供給管11を備え、供
給される空気気泡で前記粒状材を間欠的又は連
続的に前記充填層4の下方部より抜き出し、ドラ
フトチユーブ5内に吸引し、前記充填層4の上方
部に移送せしめつつ前記粒状材を洗浄しながら
環流部14を経て充填層界面7に循環する構成と
してある。
That is, a draft tube 5 whose lower end is open is vertically provided in the lower part of the packed bed 4, and the upper end of the draft tube 5 is opened above the packed bed interface 7, and around it, the upper end is above the water surface. The reflux part 14 of the granular material is separated from the treated water outflow part 2 by a partition wall 16 that protrudes from the outside, and a washing waste water outflow pipe 15 is provided in the reflux part 14 to allow the washing waste water separated from the granular material to flow out. and an air supply pipe 11 is provided at the lower part of the draft tube 5, and the granular material is intermittently or continuously extracted from the lower part of the packed bed 4 using the supplied air bubbles and sucked into the draft tube 5, The particulate material is transported to the upper part of the packed bed 4 and circulated to the packed bed interface 7 via the reflux part 14 while cleaning the particulate material.

しかして、ドラフトチユーブ5にある弁12を
閉じた状態で原水1′を供給して充填槽4内を上
向流で通水すると共に散気管9から空気8′を送
給すると、原水1′中のBOD成分などが散気管9
からの空気気泡から供給される酸素と充填槽4内
の粒状材に付着した微生物によつて好気性生物
処理が行なわれる。
Therefore, when the raw water 1' is supplied with the valve 12 in the draft tube 5 closed and the water is passed through the filling tank 4 in an upward flow, and the air 8' is fed from the aeration pipe 9, the raw water 1' The BOD components inside the air diffuser 9
Aerobic biological treatment is performed by oxygen supplied from air bubbles from the filling tank 4 and microorganisms attached to the granular material in the filling tank 4.

この生物処理操作を継続するに従つて充填層4
内に原水1′中のSSとBODの除去に伴つて発生
する微生物SSが蓄積してくるが、上向流で原水
1′を通水しているため、ある値以上にヘツドロ
スが増大してくると充填層4の一部が僅かに膨張
し、それまで捕捉されていたSSが逸出されるの
で、ヘツドロスの増大が抑制される。
As this biological treatment operation continues, the packed bed 4
Microbial SS generated as SS and BOD in the raw water 1' are removed accumulates within the tank, but since the raw water 1' is passed in an upward flow, the hetudross increases beyond a certain value. When this happens, a part of the packed bed 4 expands slightly, and the SS that has been trapped until then escapes, thereby suppressing an increase in hedose loss.

しかしながら、このような通常の生物処理時の
水のみでは充填層4内に目詰まりが残り、最終的
に充填層4内に極端な原水1′の偏流が発生し、
所期の生物処理が不可能となるので、間欠的に弁
12を開放してドラフトチユーブ5内に空気供給
管11から空気11′を送給する。この操作によ
つて、ドラフトチユーブ5内にエアリフト作用が
発生するため充填層4底部の粒状材が材移送
管となるドラフトチユーブ5の下端部から吸引さ
れ、ドラフトチユーブ5内を空気気泡と共に激し
い乱流を伴つて移送されながら洗浄され、その上
端の開口部6から溢流して還流部14に流入した
のち、充填層界面7上に落下、還流され汚染され
た材を上方から抜き出して洗浄でき常に材を
最適状態に維持できる。かくて一定時間の後には
充填層4内の粒状材が全量ドラフトチユーブ5
内を通過し、それまで充填層4内に蓄積していた
SSや余分な微生物は効果的に剥離され、該SSや
余分な微生物は洗浄排水と共に洗浄排水流出管1
5から系外へ排出される。この場合、処理水流出
部2への前記洗浄排水の流入は仕切壁16により
防止される。
However, if only water is used during such normal biological treatment, clogging remains in the packed bed 4, and eventually an extreme drift of the raw water 1' occurs in the packed bed 4.
Since the desired biological treatment becomes impossible, the valve 12 is opened intermittently to feed air 11' into the draft tube 5 from the air supply pipe 11. Due to this operation, an air lift effect occurs in the draft tube 5, so that the granular material at the bottom of the packed bed 4 is sucked from the lower end of the draft tube 5, which serves as a material transfer pipe, and the inside of the draft tube 5 is violently disturbed together with air bubbles. The material is washed while being transferred with the flow, overflows from the opening 6 at the upper end and flows into the reflux section 14, and then falls onto the packed bed interface 7, and the refluxed and contaminated material can be extracted from above and cleaned at all times. The material can be maintained in optimal condition. Thus, after a certain period of time, all of the granular material in the packed bed 4 is transferred to the draft tube 5.
had accumulated in the packed layer 4 until then.
The SS and extra microorganisms are effectively removed, and the SS and extra microorganisms are removed together with the washing wastewater from the washing wastewater outflow pipe 1.
5 and is discharged from the system. In this case, the partition wall 16 prevents the cleaning wastewater from flowing into the treated water outflow portion 2 .

なお、上記した粒状材洗浄操作は間欠的なも
のであつたが、これを連続的に行なうことも可能
であり、この場合、散気管9及び空気供給管11
から並行してそれぞれ空気8′及び空気11′が送
給されると共に、原水1′が供給され、処理水
2′は処理水流出部2から、また洗浄排水は洗浄
排水流出管15からそれぞれ並行して係外へ排出
される(原水1′の一部はドラフトチユーブ5に、
残部は充填層4内を上昇する)。なお、ドラフト
チユーブ5内に吸引された原水1′が処理水流出
部2へシヨートパスしないようにするためには処
理水2′の排出量が洗浄排水の排出量よりも多く
なるように設定することがより好ましい。このよ
うに本発明によれば、通常の生物処理中に粒状
材の洗浄操作を同時に行なうことができる。
Although the granular material cleaning operation described above was performed intermittently, it is also possible to perform this continuously. In this case, the air diffuser pipe 9 and the air supply pipe 11
Air 8' and air 11' are fed in parallel from each other, and raw water 1' is supplied from the wafer, treated water 2' is fed from the treated water outlet 2, and wash water is fed from the wash water outlet pipe 15 in parallel. (A part of the raw water 1' is discharged to the draft tube 5,
The remainder rises in the packed bed 4). In addition, in order to prevent the raw water 1' sucked into the draft tube 5 from short-passing to the treated water outflow section 2, the discharge amount of the treated water 2' must be set to be greater than the discharge amount of the washing wastewater. is more preferable. As described above, according to the present invention, granular material can be washed simultaneously during normal biological treatment.

本発明においては、第2図例のように弁12を
設ける代わりにドラフトチユーブ5の上端を開放
すると共に、該上端を水面よりも高位置に立ち上
げてもよく、これにより生物処理操作中に原水
1′がドラフトチユーブ5を通つて洗浄排水流出
管15からシヨートパスにより系外へ流出するの
を防止することができる。また、第3図のよう
に、処理槽3の底面に原水流入口と散気口を分散
して配置すれば槽底内周囲(図示斜線部)の粒状
材は静止したままで自然に安息角が形成され、
一部の粒状材は安息角に沿つて移動するので、
前例の円錐ないし角錐状の多孔性底板13を省略
することが可能となる。
In the present invention, instead of providing the valve 12 as in the example shown in FIG. 2, the upper end of the draft tube 5 may be opened and the upper end may be raised to a higher position than the water surface. It is possible to prevent the raw water 1' from flowing out of the system through the draft tube 5 from the cleaning wastewater outflow pipe 15 by a shot pass. In addition, as shown in Figure 3, if the raw water inlet and air diffuser are arranged in a distributed manner on the bottom of the treatment tank 3, the granular materials around the tank bottom (the shaded area in the figure) will remain stationary and will naturally have an angle of repose. is formed,
Some granular materials move along the angle of repose, so
It becomes possible to omit the conical or pyramidal porous bottom plate 13 of the previous example.

なお前記充填層4における粒状材の洗浄操作
を処理槽3内で行なう代わりに、充填層4の上方
部と下方部を遠心ポンプなどのポンプを備えた循
環路により連絡して、粒状材を該循環路を移送
せしめながら(所望により該循環路に加圧空気等
を吹き込んで粒状材の撹拌を促進せしめてもよ
い)洗浄してもよい。
Note that instead of performing the cleaning operation for the particulate material in the packed bed 4 in the processing tank 3, the upper part and the lower part of the packed bed 4 are connected by a circulation path equipped with a pump such as a centrifugal pump, and the particulate material is The cleaning may be carried out while moving the granular material through the circulation path (if desired, pressurized air or the like may be blown into the circulation path to promote agitation of the granular material).

第4図の実施例では処理槽3の底部を円錐形の
底部13により構成し、該底板13に近接して散
気管9を複数、放射状(環状の散気管9を同心状
に複数配設してもよい)に配設した構造の処理装
置を適用してもよい。
In the embodiment shown in FIG. 4, the bottom of the processing tank 3 is constituted by a conical bottom 13, and a plurality of aeration tubes 9 are disposed close to the bottom plate 13, and a plurality of radial (annular) aeration tubes 9 are arranged concentrically. It is also possible to apply a processing device having a structure arranged in

〔発明の効果〕〔Effect of the invention〕

本発明は、下部に原水流入部と酸素含有気泡送
給部、上部に処理水流出部を設けた槽内の水面下
に比重1.0以上の粒状材で充填層を形成せしめ、
この充填層内下方部に下端が開口する材移送管
を垂直方向に設け、この材移送管の上端を充填
層界面より上方に開口配置すると共にその周囲
に、上端が水面上に突出した仕切壁で粒状材の
環流部を処理水流出部と区画して形成し、さらに
該環流部に粒状材と分離された洗浄排水を流出
させる洗浄排水流出管を配備し、かつ前記材移
送管下部に空気供給管を備え、供給される空気気
泡で前記粒状材を間欠的又は連続的に前記充填
層下方部より抜き出し、材移送管内に吸引し、
前記充填層の上方部に移送せしめつつ前記粒状
材を洗浄しながら環流部を経て充填層界面に循環
する構成としたことにより、粒径の小さな、比表
面積の大きな粒状材を使用しても全く目詰まり
が発生しない。したがつて、メンテナンスが容易
で処理効率も向上すると共に、空気などの酸素含
有気泡を直接浸漬充填層内に供給するので、従来
法のようにエアリフトによる曝気時に気泡が短時
間に大気中に逸出することがなく、浸漬充填層内
の小さな空隙部に抑留される結果、気泡の滞留時
間が長くなり、例えば酸素供給動力効率が従来法
の約3倍となり、3Kg・O2/KWHが安定して得
られるし、浸漬充填層を支持する支持床(第1図
参照)が不要になるので、支持床の孔に目詰まり
が発生するトラブルが起きないし、ドラフトチユ
ーブへの空気供給はエアレーシヨンが目的ではな
いので、間欠的、しかも短時間でよいので、消費
電力が従来法に比べ格段に少なくて済み、しかも
処理槽底部をテーパー状に限ずしもする必要がな
いので、構造簡単で、製作が容易になるほか、原
水の生物処理と粒状材の洗浄操作を並行して、
しかも連続して行なうことができるので、前記洗
浄操作のために生物処理を中断する必要がなく常
に粒状材を最適状態に維持でき、しかも良質の
処理水を安定して得ることができる。
The present invention forms a packed bed of granular material with a specific gravity of 1.0 or more under the water surface in a tank that has a raw water inlet and an oxygen-containing bubble feeder in the lower part and a treated water outlet in the upper part,
A material transfer pipe whose lower end is open is provided vertically in the lower part of the packed bed, and the upper end of this material transfer pipe is opened above the packed bed interface, and around it is a partition wall whose upper end protrudes above the water surface. A reflux part of the granular material is separated from a treated water outflow part, and a washing wastewater outflow pipe is provided in the reflux part for discharging washing wastewater separated from the granular material, and air is provided at the bottom of the material transfer pipe. comprising a supply pipe, the granular material is intermittently or continuously extracted from the lower part of the packed bed using supplied air bubbles, and is sucked into the material transfer pipe;
By having a structure in which the particulate material is transferred to the upper part of the packed bed and circulated to the packed bed interface through the reflux part while being washed, there is no problem even when using particulate material with a small particle size and a large specific surface area. No clogging occurs. Therefore, maintenance is easy and processing efficiency is improved, and since oxygen-containing bubbles such as air are directly supplied into the immersed packed bed, the bubbles do not escape into the atmosphere in a short period of time during aeration using an air lift, unlike conventional methods. As a result, the residence time of the bubbles becomes longer, and the oxygen supply power efficiency is approximately three times that of the conventional method, resulting in a stable 3Kg・O 2 /KWH. Since the supporting bed (see Figure 1) that supports the immersed packed bed is not required, there is no problem of clogging of the holes in the supporting bed, and the air supply to the draft tube requires no aeration. Since it is not a specific purpose, it can be done intermittently and for a short time, so the power consumption is much lower than the conventional method.Furthermore, the structure is simple as there is no need to limit the bottom of the treatment tank to a tapered shape. In addition to making production easier, biological treatment of raw water and cleaning of granular materials can be performed in parallel.
Moreover, since it can be carried out continuously, there is no need to interrupt the biological treatment for the cleaning operation, and the granular material can always be maintained in an optimal state, and high-quality treated water can be stably obtained.

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

第1図は従来法を示す系統説明図、第2図は本
発明の一実施例の系統説明図、第3図及び第4図
はそれぞれ他の実施例の一部の系統説明図であ
る。 1……原水流入部、1′……原水、2……処理
水流出部、2′……処理水、3……処理槽、3′…
…外壁、4……充填層、5……ドラフトチユー
ブ、6……開口部、7……充填層界面、8……空
気供給管、8′……空気、9……散気管、10…
…空間部、11……空気供給管、11′……空気、
12……弁、13……底板、13′……空気供給
孔、14……還流部、15……洗浄排水流出管、
16……仕切壁、17……空間部。
FIG. 1 is a system explanatory diagram showing a conventional method, FIG. 2 is a system explanatory diagram of one embodiment of the present invention, and FIGS. 3 and 4 are system explanatory diagrams of a part of other embodiments. 1... Raw water inlet, 1'... Raw water, 2... Treated water outlet, 2'... Treated water, 3... Treatment tank, 3'...
...Outer wall, 4...Filled bed, 5...Draft tube, 6...Opening, 7...Filled bed interface, 8...Air supply pipe, 8'...Air, 9...Diffusion pipe, 10...
...Space part, 11...Air supply pipe, 11'...Air,
12...Valve, 13...Bottom plate, 13'...Air supply hole, 14...Recirculation section, 15...Washing drainage outflow pipe,
16... Partition wall, 17... Space section.

Claims (1)

【特許請求の範囲】 1 下部に原水流入部と酸素含有気泡送給部、上
部に処理水流出部を設けた槽内の水面下に比重
1.0以上の粒状材で充填層を形成せしめ、この
充填層内下方部に下端が開口する材移送管を垂
直方向に設け、この材移送管の上端を充填層界
面より上方に開口配置すると共にその周囲に、上
端が水面上に突出した仕切壁で粒状材の環流部
を処理水流出部と区画して形成し、さらに該環流
部に粒状材と分離された洗浄排水を流出させる
洗浄排水流出管を配備し、かつ前記材移送管下
部に空気供給管を備え、供給される空気気泡で前
記粒状材を間欠的又は連続的に前記充填層下方
部より抜き出し、材移送管内に吸引し、前記充
填層の上方部に移送せしめつつ前記粒状材を洗
浄しながら環流部を経て充填層界面に循環する構
成としたことを特徴とする有機性廃水の生物処理
装置。 2 前記充填層が、空気供給孔のある錐状板上に
充填されるものであつて、該錐状板と槽外壁との
間に形成される空間部にある散気部の上方に配置
されているものである特許請求の範囲第1項記載
の生物処理装置。 3 前記充填槽が、状材の移動に安息角が形
成されるように原水流入口と散気口と分散配備さ
れたものである特許請求の範囲第1項記載の生物
処理装置。 4 前記充填層が、円錐形槽底中に備えられるも
のであつて、該円錐形槽底に接近して散気管を内
装したものである特許請求の範囲第1項記載の生
物処理装置。
[Scope of Claims] 1. Specific gravity under the water surface in a tank with a raw water inlet and an oxygen-containing bubble feeder in the lower part and a treated water outlet in the upper part.
A packed bed is formed with granular material of 1.0 or more, and a material transfer pipe whose lower end is open is vertically provided in the lower part of the packed bed, and the upper end of this material transfer pipe is opened above the interface of the packed bed. A washing wastewater outflow pipe is formed around the periphery to separate the reflux part of the granular material from the treated water outflow part by a partition wall whose upper end protrudes above the water surface, and further drains the washing wastewater separated from the granular material into the reflux part. and an air supply pipe at the bottom of the material transfer pipe, and the granular material is intermittently or continuously extracted from the lower part of the packed bed using the supplied air bubbles, sucked into the material transfer pipe, and then A biological treatment device for organic wastewater, characterized in that the granular material is circulated to the interface of the packed bed via a reflux section while being transported to the upper part of the bed and washed. 2. The packed layer is filled on a conical plate having air supply holes, and is arranged above an air diffuser in a space formed between the conical plate and the outer wall of the tank. A biological treatment device according to claim 1, which comprises: 3. The biological treatment apparatus according to claim 1, wherein the filling tank has a raw water inlet and an aeration port arranged in a distributed manner so that an angle of repose is formed in the movement of the shaped materials. 4. The biological treatment apparatus according to claim 1, wherein the packed bed is provided in a conical tank bottom, and an aeration pipe is installed close to the conical tank bottom.
JP1422981A 1981-02-04 1981-02-04 Biological treatment of org. waste water Granted JPS57130590A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1422981A JPS57130590A (en) 1981-02-04 1981-02-04 Biological treatment of org. waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1422981A JPS57130590A (en) 1981-02-04 1981-02-04 Biological treatment of org. waste water

Related Child Applications (1)

Application Number Title Priority Date Filing Date
JP62289449A Division JPS63214392A (en) 1987-11-18 1987-11-18 Biological treatment of organic waste water

Publications (2)

Publication Number Publication Date
JPS57130590A JPS57130590A (en) 1982-08-13
JPS6331280B2 true JPS6331280B2 (en) 1988-06-23

Family

ID=11855235

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1422981A Granted JPS57130590A (en) 1981-02-04 1981-02-04 Biological treatment of org. waste water

Country Status (1)

Country Link
JP (1) JPS57130590A (en)

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5979290U (en) * 1982-11-17 1984-05-29 株式会社西原環境衛生研究所 Sewage treatment equipment
JPH01199693A (en) * 1988-02-04 1989-08-11 Sumitomo Jukikai Envirotec Kk Activated sludge type water treatment device
JPH01266897A (en) * 1988-04-19 1989-10-24 Keiji Goto Continuous moving bed type iron removing method for utilizing iron bacteria
CN103459331B (en) * 2011-03-31 2016-01-06 株式会社久保田 Sewage purifier
JP2012213697A (en) * 2011-03-31 2012-11-08 Kubota Corp Sewage purification facility
JP2012213696A (en) * 2011-03-31 2012-11-08 Kubota Corp Sewage purification facility
JP5814583B2 (en) * 2011-03-31 2015-11-17 株式会社クボタ Septic tank

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52111062A (en) * 1976-03-03 1977-09-17 Nordstjernan Rederi Ab Suspension or emulsion filtrating method and system
JPS5359252A (en) * 1976-11-08 1978-05-27 Hitachi Chem Co Ltd Apparatus for treating waste liquid
JPS5394443A (en) * 1977-01-29 1978-08-18 Unitika Ltd Method of and device for treating waste water by moving layer filter
JPS54108464A (en) * 1978-02-14 1979-08-25 Chiyoda Chem Eng & Constr Co Ltd Method of biologically treating drainage by downward flow
JPS54136746A (en) * 1978-04-14 1979-10-24 Nippon Kentetsu Co Ltd Waste water disposal process
JPS5529753A (en) * 1978-08-25 1980-03-03 Hitachi Ltd Detecting method for foreign matter

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52111062A (en) * 1976-03-03 1977-09-17 Nordstjernan Rederi Ab Suspension or emulsion filtrating method and system
JPS5359252A (en) * 1976-11-08 1978-05-27 Hitachi Chem Co Ltd Apparatus for treating waste liquid
JPS5394443A (en) * 1977-01-29 1978-08-18 Unitika Ltd Method of and device for treating waste water by moving layer filter
JPS54108464A (en) * 1978-02-14 1979-08-25 Chiyoda Chem Eng & Constr Co Ltd Method of biologically treating drainage by downward flow
JPS54136746A (en) * 1978-04-14 1979-10-24 Nippon Kentetsu Co Ltd Waste water disposal process
JPS5529753A (en) * 1978-08-25 1980-03-03 Hitachi Ltd Detecting method for foreign matter

Also Published As

Publication number Publication date
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