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JPH0736918B2 - Supernatant discharge method in batch biological treatment - Google Patents
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JPH0736918B2 - Supernatant discharge method in batch biological treatment - Google Patents

Supernatant discharge method in batch biological treatment

Info

Publication number
JPH0736918B2
JPH0736918B2 JP5009551A JP955193A JPH0736918B2 JP H0736918 B2 JPH0736918 B2 JP H0736918B2 JP 5009551 A JP5009551 A JP 5009551A JP 955193 A JP955193 A JP 955193A JP H0736918 B2 JPH0736918 B2 JP H0736918B2
Authority
JP
Japan
Prior art keywords
supernatant
biological treatment
liquid
level
treatment tank
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 - Fee Related
Application number
JP5009551A
Other languages
Japanese (ja)
Other versions
JPH06312195A (en
Inventor
四郎 志村
三郎 小沢
之博 中沢
Original Assignee
株式会社新潟鉄工所
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 株式会社新潟鉄工所 filed Critical 株式会社新潟鉄工所
Priority to JP5009551A priority Critical patent/JPH0736918B2/en
Publication of JPH06312195A publication Critical patent/JPH06312195A/en
Publication of JPH0736918B2 publication Critical patent/JPH0736918B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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

  • Activated Sludge Processes (AREA)

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、生物処理槽で少なくと
も曝気工程と汚泥の静置分離工程と上澄液引抜き工程と
を有するサイクルを繰返して汚水処理を行う回分式生物
処理における上澄液の排出方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a supernatant liquid in a batch biological treatment for treating wastewater by repeating a cycle having at least an aeration step, a sludge static separation step and a supernatant liquid withdrawing step in a biological treatment tank. Regarding the discharge method.

【0002】[0002]

【従来の技術】従来から、図9に示すように生物処理槽
に対して、汚水等の排水をその生物処理槽に受入れる
「排水の受入れ工程」と、生物処理槽内に酸素含有ガス
を供給する「曝気工程」と、生物処理槽内の活性汚泥を
沈殿させる「汚泥の沈殿工程」と、その沈殿汚泥上方の
上澄液を生物処理槽から排出する「上澄液引抜き工程」
とを有するサイクルを繰返して汚水処理を行う回分式生
物処理や、上記曝気工程・汚泥の沈殿工程・上澄液引抜
き工程といえども生物処理槽に排水を常時受入れ、上記
サイクルとしては「汚水の受入れ工程」が存在しない回
分式生物処理、さらに「曝気工程」の前後に曝気せずに
生物処理槽内を嫌気状態にする工程等を加えた回分式生
物処理等の各種回分式生物処理が知られている。
2. Description of the Related Art Conventionally, as shown in FIG. 9, a biological wastewater treatment step of receiving wastewater such as sewage into the biological treatment tank, and supplying an oxygen-containing gas into the biological treatment tank. "Aeration process", "Sludge settling process" to settle the activated sludge in the biological treatment tank, and "Supernatant extraction process" to discharge the supernatant above the settling sludge from the biological treatment tank.
Even if the batch-type biological treatment is carried out by repeating the cycle including the treatment of wastewater, and the aeration process, sludge settling process, and supernatant removal process, wastewater is always received in the biological treatment tank. Various batch-type biological treatments such as batch-type biological treatments that do not have an "accepting step", and those that add a step of making the inside of the biological treatment tank anaerobic without aeration before and after the "aeration step" are known. Has been.

【0003】これら、生物処理槽で少なくとも曝気工程
と汚泥の沈殿工程と上澄液引抜き工程とを有するサイク
ルを繰返して汚水処理を行う回分式生物処理において
は、フロート式の上澄液引抜き管を用いて上澄液の引抜
きが行われる。すなわち、フロート式の上澄液引抜き管
を有する回分式生物処理装置においては、従来上澄液の
引抜き開始及び終了を、図12に示すように上澄液引抜
き管1の下降及び上昇により行うか、または図13に示
すように上澄液引抜き管2の排出端に設けた弁3を液面
検出器4からの検出信号に基づいて開閉することにより
行っている。そして、上澄液の引抜きは、生物処理槽5
内の液面と上澄液引抜き管1,2の排出開口端とのレベ
ル差による自然流下にまかせていた。
In a batch type biological treatment in which a cycle of at least an aeration step, a sludge settling step and a supernatant extraction step is repeated in the biological treatment tank to perform wastewater treatment, a float type supernatant extraction tube is used. The supernatant liquid is used for withdrawal. That is, in a batch-type biological treatment apparatus having a float type supernatant withdrawal pipe, is it conventionally necessary to start and end the withdrawal of the supernatant liquid by lowering and raising the supernatant liquid withdrawal pipe 1 as shown in FIG. Alternatively, as shown in FIG. 13, the valve 3 provided at the discharge end of the supernatant liquid withdrawing pipe 2 is opened and closed based on the detection signal from the liquid level detector 4. Then, the supernatant liquid is drawn out by the biological treatment tank 5
The liquid was left to flow naturally due to the level difference between the liquid surface inside and the discharge opening ends of the supernatant liquid withdrawing tubes 1 and 2.

【0004】したがって、上澄液引抜き管1,2の抜出
し口1a,2aと汚泥界面Sが近づく上澄液引抜き工程
の終了間際には上記のレベル差が小さくなつて上澄液引
抜き流量(流速)が小さくなり、汚泥の巻込みが回避さ
れるという利点があった。また上澄液引抜き管1,2の
フロート1b,2bを環状に形成することにより、上澄
液上に浮ぶスカムが上澄液引抜き管1,2の抜出し口1
a,2aに流入するのを防止することができるという利
点もあった。
Therefore, the above-mentioned level difference becomes small immediately before the completion of the supernatant liquid withdrawal step where the discharge ports 1a, 2a of the supernatant liquid withdrawing pipes 1, 2 and the sludge interface S approach, and the supernatant liquid withdrawing flow rate (flow velocity) is reduced. ) Is small, and the inclusion of sludge can be avoided. Further, by forming the floats 1b and 2b of the supernatant liquid withdrawing pipes 1 and 2 in an annular shape, the scum floating on the supernatant liquid has an outlet 1 of the supernatant liquid withdrawing pipes 1 and 2.
There was also an advantage that it could be prevented from flowing into a, 2a.

【0005】[0005]

【発明が解決しようとする課題】ところが、上記従来の
生物処理方式では、上澄液の引抜きは上述の如く自然流
下によるので引抜き初期は引抜き流量が大きく、このた
め、活性汚泥が所定のレベル以下(例えば静置分離工程
の液面レベルの略半分程度のレベル以下)まで沈殿して
汚泥の巻込みが生じないようになってから上澄液引抜き
工程を開始するのが実情であり、汚泥の静置分離工程と
上澄液引抜き工程に長時間を要すると共に、引抜き時間
が固定的で汚泥の沈降性状が変化した場合等の状況に合
わせてこれを調整することができないといった問題があ
った。
However, in the above-mentioned conventional biological treatment method, since the supernatant liquid is withdrawn by natural flow as described above, the withdrawal flow rate is large at the initial stage of withdrawal. Therefore, the activated sludge is below a predetermined level. It is the actual situation to start the supernatant withdrawal step after the sludge is prevented from being entrained up to the level (for example, about half or less of the liquid level in the stationary separation step) and the sludge removal step is started. There is a problem that the static separation step and the supernatant liquid withdrawing step take a long time, and the withdrawal time is fixed and cannot be adjusted according to the situation such as when the sedimentation property of sludge changes.

【0006】本発明は、上記事情に鑑みてなされたもの
で、生物処理槽からの上澄液の排出速度を遅く制御出来
て、汚泥の巻込みを防止できる回分式生物処理における
上澄液排出方法を提供することを目的とする。
The present invention has been made in view of the above circumstances, and can discharge the supernatant liquid from the biological treatment tank at a slow control rate to prevent sludge from being entrained. The purpose is to provide a method.

【0007】[0007]

【課題を解決するための手段】上記目的を達成するため
に、本発明は、生物処理槽で少なくとも曝気工程と汚泥
の沈殿工程と上澄液引抜き工程とを有するサイクルを繰
返して汚水処理を行う回分式生物処理において、上記生
物処理槽内に設けられ、先端部分にフロートと上澄液の
抜出し口を有して少なくとも該先端部分が水位の変動に
追従し、他端が処理水槽の上記生物処理槽における上澄
液引抜き下限レベル以下の位置で開口する上澄液引抜き
管により上記生物処理槽の上澄液を引抜く上澄液排出方
法であって、生物処理槽からの上澄液排出速度が、該生
物処理槽の液面レベルと上澄液引抜き管開口端のレベル
との差に基づく自然流下速度より遅くなるように、生物
処理槽から引抜かれた処理水槽の上澄液の液面が上記上
澄液引抜き管開口端を越えた状態で上記処理水槽に受入
れられた上澄液の排出量を制御する構成とした。
In order to achieve the above object, the present invention performs wastewater treatment in a biological treatment tank by repeating a cycle including at least an aeration step, a sludge precipitation step and a supernatant liquid withdrawal step. In the batch type biological treatment, the organism provided in the biological treatment tank has a float and a supernatant liquid outlet at its tip portion, at least the tip portion follows the fluctuation of the water level, and the other end of the organism in the treated water tank. A supernatant discharge method in which the supernatant of the above-mentioned biological treatment tank is drawn out by a supernatant draw-out pipe that opens at a position below the lower limit level of the supernatant of the biological treatment tank. The liquid of the supernatant of the treated water tank drawn out from the biological treatment tank so that the speed becomes slower than the natural flow rate based on the difference between the liquid level of the biological treatment tank and the level of the opening end of the supernatant drawing tube. Surface is the above supernatant liquid extraction tube opening And configured to control the emissions of supernatant received in the treating tank in a state of beyond.

【0008】[0008]

【作用】生物処理槽から引抜かれた処理水槽の上澄液の
液面が上記上澄液引抜き管開口端を越えた状態になる
と、生物処理槽の上澄液と処理水槽の引抜かれた上澄液
とが上記上澄液引抜き管を介してU字管状的に連通状態
になる。この状態で処理水槽の液面(処理水槽に受入れ
られた上澄液の排出量)を制御することにより、生物処
理槽からの上澄液引抜き速度が該生物処理槽の液面レベ
ルと上澄液引抜き管開口端のレベルとの差に基づく自然
流下速度より遅くすることがはじめて可能となる。
[Function] When the liquid level of the supernatant of the treated water tank drawn from the biological treatment tank exceeds the opening end of the above supernatant extraction tube, the supernatant of the biological treatment tank and the treated water tank are removed. The clear fluid is in a U-shaped tubular communication state through the supernatant drawing tube. In this state, by controlling the liquid level of the treated water tank (the discharge amount of the supernatant liquid received in the treated water tank), the supernatant liquid withdrawal rate from the biological treatment tank can be adjusted to the liquid surface level of the biological treatment tank and the supernatant liquid. It is possible for the first time to make it slower than the natural flow velocity based on the difference from the level at the opening end of the liquid drawing pipe.

【0009】すなわち、生物処理槽の上澄液と処理水槽
の引抜かれた上澄液とが上澄液引抜き管を介してU字管
状的に連通状態になると、生物処理槽からの上澄液引抜
き速度は、生物処理槽の液面レベルと処理水槽の液面レ
ベルとの差により制御されるので、生物処理槽の液面レ
ベルと上澄液引抜き管開口端のレベルとの差に基づく従
来の自然流下速度より必然的に遅くなる。特に、処理水
槽に受入れられた上澄液の排出量(排出速度)を例えば
もっと遅くすれば、生物処理槽と処理水槽の液面が略一
致(バランス)する状態となり、その後の生物処理槽の
上澄液の引抜き量は処理水槽からの排出量と略等しくな
る。
That is, when the supernatant liquid of the biological treatment tank and the drawn supernatant liquid of the treated water tank are brought into a U-shaped tubular communication state via the supernatant liquid drawing pipe, the supernatant liquid from the biological treatment tank is Since the drawing speed is controlled by the difference between the liquid level in the biological treatment tank and the liquid level in the treated water tank, the conventional method is based on the difference between the liquid level in the biological treatment tank and the level at the open end of the supernatant drawing tube. Inevitably slower than the natural flow rate of. In particular, if the discharge amount (discharge speed) of the supernatant liquid received in the treated water tank is made slower, for example, the liquid levels of the biological treatment tank and the treated water tank will be substantially the same (balanced), and The amount of the supernatant drawn is approximately equal to the amount discharged from the treated water tank.

【0010】したがって、生物処理槽の液面レベルと上
澄液引抜き管開口端のレベルとの差に基づく従来の自然
流下による場合よりも小さい引抜き量(流速)で上澄液
を引抜くことができ、上澄液への汚泥の混入が従来より
一層少なくなる。さらに、万一ミス等で処理水槽に受入
れられた上澄液の排出量(流速)を途中で非常に速くし
てしまった場合においても、生物処理槽からの上澄液の
引抜き量(速度)は、たとえ処理水槽内の液面が上澄液
引抜き管開口端以下に下がっても、生物処理槽の液面レ
ベルと上澄液引抜き管開口端のレベルとの差に基づく従
来の自然流下量(速度)に制約され、処理水槽からの上
記速い排出速度に影響されることがなく、上澄液の引抜
きが安全に行われる。
Therefore, the supernatant liquid can be drawn out with a smaller drawing amount (flow velocity) than in the case of the conventional natural flow based on the difference between the liquid level of the biological treatment tank and the level of the opening end of the supernatant drawing pipe. As a result, the amount of sludge mixed in the supernatant liquid is further reduced than before. Furthermore, even if the discharge rate (flow velocity) of the supernatant liquid received in the treated water tank is made extremely high on the way due to a mistake, etc., the amount (rate) of withdrawal of the supernatant liquid from the biological treatment tank will be increased. Even if the liquid level in the treated water tank drops below the opening of the supernatant drawing tube, the conventional natural flow rate based on the difference between the level of the biological treatment tank and the level of the supernatant drawing tube opening end. The supernatant liquid can be safely withdrawn without being affected by the above-mentioned high discharge speed from the treated water tank, being restricted by (speed).

【0011】[0011]

【実施例】本発明を実施する回分式生物処理装置の一例
を図1ないし図11を参照して説明する。図中10は生
物処理槽で、この生物処理槽10内で図9に示す原排水
の受入れ工程と曝気工程と汚泥の静置分離工程と上澄液
引抜き工程とから成るサイクルが繰返されるようになっ
ている。そして、この生物処理槽10の内部に、先端に
フロート11と上澄液の抜出し口12を有し基端が連通
管13に接続して生物処理槽10外に連通された上澄液
引抜き管14が配設されると共に、この生物処理槽10
の槽壁10aの上部には、上記上澄液引抜き管14を起
倒する起倒装置15が設置されている。なお、上記連通
管13は上澄液引抜き管14の一部を構成している。ま
た、周知のように、原排水の受入れを、曝気工程、静置
分離工程、上澄液引抜き工程中に行ってもよい。
DESCRIPTION OF THE PREFERRED EMBODIMENTS An example of a batch type biological treatment apparatus for carrying out the present invention will be described with reference to FIGS. In the figure, 10 is a biological treatment tank. In the biological treatment tank 10, a cycle consisting of a raw wastewater receiving process, an aeration process, a sludge static separation process and a supernatant liquid withdrawing process shown in FIG. 9 is repeated. Has become. Then, inside the biological treatment tank 10, a float 11 and a supernatant liquid outlet 12 are provided at the tip, and the base end is connected to a communication pipe 13 to communicate with the outside of the biological treatment tank 10. 14 is provided and the biological treatment tank 10
On the upper part of the tank wall 10a, a tilting device 15 for tilting the supernatant drawing pipe 14 is installed. The communication pipe 13 constitutes a part of the supernatant drawing pipe 14. Further, as is well known, the raw waste water may be received during the aeration step, the stationary separation step, and the supernatant drawing step.

【0012】上記上澄液引抜き管14は、所定長さの直
管14aの先端に45度の曲り管14bを介して上記抜
出し口12を有する集液管14cが連設され、かつ、上
記直管14aの基端に90度の曲り管14dが連設され
たもので、その基端の曲り管14dが、槽壁10aに固
定された上記連通管13の曲り管に回転継手14eを介
して上下に回動自在に接続されている。そして、上記集
液管14cには左右一対の連結板14f,14fが固定
して取付けられると共に、集液管14cの上方には、4
本のパイプ11a,…を四角形の環状に組合せて形成し
た上記フロート11が、集液管14cの抜出し口12が
フロート11の中心下方にくるようにして、その互いに
対向する左右のパイプ11aに渡して取付けた左右一対
の取付け板11b,11bを上記連結板14f,14f
に連結軸14gによって連結されて、連結板14f,1
4fに対して上下に回動自在に設けられている。
The supernatant liquid withdrawing pipe 14 is provided with a straight pipe 14a having a predetermined length, and a collecting pipe 14c having the outlet 12 connected to the end of the straight pipe 14a through a bend pipe 14b of 45 degrees. A 90-degree bent pipe 14d is connected to the base end of the pipe 14a, and the bent pipe 14d at the base end is connected to the bend pipe of the communicating pipe 13 fixed to the tank wall 10a via a rotary joint 14e. It is connected to rotate up and down. A pair of left and right connecting plates 14f and 14f are fixedly attached to the liquid collecting pipe 14c, and 4 above the liquid collecting pipe 14c.
The float 11 formed by combining the book pipes 11a, ... In a rectangular ring shape is passed to the left and right pipes 11a facing each other so that the outlet 12 of the liquid collecting pipe 14c is located below the center of the float 11. The pair of left and right mounting plates 11b, 11b attached by connecting the connecting plates 14f, 14f
To the connecting plate 14f, 1
It is provided to be rotatable up and down with respect to 4f.

【0013】また、上記起倒装置15は、アングル材に
より形成され、生物処理槽10の槽壁10aの上部に固
定して設置された支持架台16と、この支持架台16の
上部中央に、ロッド17aを下方に向けた状態で固定し
て取付けられたエアシリンダ17と、このエアシリンダ
17のロッド17aの先端に連結部材18を介して固定
された前後一対の菱形の取付け板19,19の左右に軸
線を前後に向けて取付けられ、同一の鉛直面内において
回転自在なる左右一対の可動滑車20a,20bと、上
記エアシリンダ17のロッド17aの伸長端より若干下
方の位置にくるように支持架台16に軸線を前後に向け
て取付けられ、上記可動滑車20a,20bと同一の鉛
直面内において回転自在なる固定滑車21と、上記左方
の可動滑車20aから固定滑車21を経て右方の可動滑
車20bに巻回されると共に、一端が上記上澄液引抜き
管14の連結軸14gにシンブル22aを介して接続さ
れ、他端が、上記支持架台16の下面に鉛直に設けられ
たガイド管23の内部に挿入されている2個の錘24に
接続されたワイヤーロープ22とから構成されている。
The raising and lowering device 15 is formed of an angle member, and is provided with a support base 16 fixedly installed on the upper part of the tank wall 10a of the biological treatment tank 10, and a rod at the center of the upper part of the support base 16. Air cylinder 17 fixedly attached with 17a facing downward, and left and right of a pair of front and rear diamond-shaped attachment plates 19, 19 fixed to the tip of rod 17a of this air cylinder 17 via a connecting member 18. A pair of left and right movable sheaves 20a, 20b which are attached to each other with their axes oriented in the front-rear direction and are rotatable in the same vertical plane, and a support base so as to be positioned slightly below the extension end of the rod 17a of the air cylinder 17. 16, a fixed pulley 21 that is attached with its axis lined up and down and is rotatable in the same vertical plane as the movable pulleys 20a and 20b, and the left movable pulley 20a. From the stationary pulley 21 to the right movable pulley 20b, one end is connected to the connecting shaft 14g of the supernatant withdrawing pipe 14 via a thimble 22a, and the other end is connected to the support frame 16 It is composed of a wire rope 22 connected to two weights 24 inserted inside a guide tube 23 provided vertically on the lower surface.

【0014】そして、上記エアシリンダ17のシリンダ
本体17bには、スピードコントローラ25a,25b
をそれぞれに備えた2本の空気管26a,26bが接続
され、この2本の空気管26a,26bは空気供給管2
7によって圧縮空気源28に連絡された電磁切換弁29
に連絡されており、図10に示す如く、圧縮空気を下方
の空気管26bを通じてシリンダ本体17bに供給する
ことによりロッド17aを収縮させ、可動滑車20a,
20bを上昇させて固定滑車21から離間させる一方、
図1に示すように電磁切換弁29を切換えて圧縮空気を
上方の空気管26aからシリンダ本体17bに供給する
ことによりロッド17aを伸長させ、可動滑車20a,
20bを下降させて固定滑車21に接近させることがで
きるようになっている。
The speed controller 25a, 25b is provided on the cylinder body 17b of the air cylinder 17.
Are connected to two air pipes 26a and 26b, and the two air pipes 26a and 26b are connected to the air supply pipe 2
Solenoid switching valve 29 connected to compressed air source 28 by 7
As shown in FIG. 10, the compressed air is supplied to the cylinder body 17b through the lower air pipe 26b to contract the rod 17a, and the movable pulley 20a,
20b is lifted and separated from the fixed pulley 21,
As shown in FIG. 1, the electromagnetic switching valve 29 is switched to supply compressed air from the upper air pipe 26a to the cylinder body 17b, thereby extending the rod 17a to move the movable pulley 20a,
It is possible to lower 20b to bring it closer to the fixed pulley 21.

【0015】また、上記ガイド管23の支持架台16に
対する接合部には、錘24より小径のパイプや上方から
見て断面コ字形の部材等から成るストツパ30が設けら
れており、このストツパ30により錘24がガイド管2
3から上方へ抜けないようになっている。
Further, a stopper 30 composed of a pipe having a diameter smaller than that of the weight 24 or a member having a U-shaped cross section when viewed from above is provided at the joint portion of the guide tube 23 to the support frame 16. Weight 24 is guide tube 2
It does not come out from 3 upwards.

【0016】さらに、上記支持架台16の内部の前方と
後方側には、左右一対のアングル材を互いに対向配設し
て形成したガイドレール31,31が添設される一方、
上記取付け板19,19と連結部材18の上下の部位に
は、車軸32a,32aの両端にそれぞれ車輪32b,
32bを備えて成るガイド輪32,32が軸線を前後に
向けて取付けられ、このガイド輪32,32は上記ガイ
ドレール31,31に沿って上下動するようになってい
る。またさらに、上記生物処理槽10には、上澄液のレ
ベルが上澄液引抜き下限レベルLWLになったときにこ
れを検知する第1レベルスイッチ33が付設されてお
り、この第1レベルスイッチ33からの信号により上記
電磁切換弁29が図10の位置に切換えられるようにな
っている。
Further, guide rails 31, 31 formed by arranging a pair of left and right angle members facing each other are additionally provided on the front side and the rear side inside the support frame 16, while
At the upper and lower parts of the mounting plates 19 and 19 and the connecting member 18, wheels 32b and wheels 32b and 32a are provided at both ends of the axles 32a and 32a, respectively.
Guide wheels 32, 32 provided with 32b are attached with their axes directed forward and backward, and the guide wheels 32, 32 move up and down along the guide rails 31, 31. Further, the biological treatment tank 10 is further provided with a first level switch 33 for detecting when the level of the supernatant liquid reaches the supernatant liquid withdrawal lower limit level LWL. The electromagnetic switching valve 29 is switched to the position shown in FIG.

【0017】一方、上記生物処理槽10の隣には、内部
に上記連通管13の外方端が臨ませられる処理水槽34
(上澄液槽)が設置され、この処理水槽34の内底部に
は、吐出側に放流管35が接続されたポンプ36が設置
されている。そして、上記放流管35には、流量計37
とこの流量計37からの信号により開度が調整される流
量調整弁38とが設けられると共に、上澄液を処理水槽
34に戻す循環管39が接続され、この循環管39にオ
リフィス39aが設けられている。
On the other hand, next to the biological treatment tank 10, a treated water tank 34 in which the outer end of the communication pipe 13 is exposed.
A (supernatant tank) is installed, and a pump 36 having a discharge pipe 35 connected to the discharge side is installed at the inner bottom portion of the treated water tank 34. A flow meter 37 is attached to the discharge pipe 35.
And a flow rate adjusting valve 38 whose opening is adjusted by a signal from the flow meter 37, a circulation pipe 39 for returning the supernatant liquid to the treated water tank 34 is connected, and an orifice 39a is provided in the circulation pipe 39. Has been.

【0018】また、上記処理水槽34には、処理水槽3
4内の液面が所定の上限レベルH2WLに達したときに
これを検知すると共に上記ポンプ36を起動する上方レ
ベルスイッチ40aと、処理水槽34内の液面が所定の
下限レベルL2WLになつたときにこれを検知すると共
に上記ポンプ36を停止する下方レベルスイッチ40b
とが設けられており、この上方レベルスイッチ40aと
下方レベルスイッチ40bとが、処理水槽34の液面を
検知し、その検知信号に基づいて上記ポンプ36を停動
する液面検知装置40を構成している。
The treated water tank 34 includes the treated water tank 3
The upper level switch 40a that detects when the liquid level in 4 reaches a predetermined upper limit level H 2 WL and activates the pump 36, and the liquid level in the treated water tank 34 is a predetermined lower limit level L 2 WL. Lower level switch 40b that detects this when the
And the upper level switch 40a and the lower level switch 40b detect the liquid level of the treated water tank 34 and configure the liquid level detection device 40 that stops the pump 36 based on the detection signal. is doing.

【0019】ここで、処理水槽34に設けた連通管13
開口端の取付け高さは、生物処理槽10における上澄液
引抜き下限レベルLWL以下であればよいが、汚泥の静
置分離工程終了時の沈降汚泥界面Sと上記上澄液引抜き
下限レベルLWLとの間に設けるのがよく、好ましくは
上澄液引抜き下限レベルLWLの近傍に設けるのがよ
い。
Here, the communication pipe 13 provided in the treated water tank 34
The mounting height of the open end may be equal to or lower than the lower limit level LWL of the supernatant withdrawal in the biological treatment tank 10, but the settled sludge interface S at the end of the sludge static separation step and the lower limit level LWL of the supernatant withdrawal. It is preferable to provide it in the vicinity of the supernatant extraction lower limit level LWL.

【0020】また、上記処理水槽34の容量は、生物処
理槽10の1サイクルで処理する水量より遥かに小さ
い。さらに、上記下方レベルスイッチ40bの液面検出
位置高さ(すなわち処理水槽34の下限レベルL2
L)は、生物処理槽10の上澄液引抜き下限レベルLW
L以下であればよく、処理水槽34の容量や後述する自
然流下からポンプ36による抜出しへの切換えのタイミ
ング等によるが連通管13の開口端のレベル以下でもよ
く、さらには上澄液引抜き下限レベルLWLに同じレベ
ルと連通管13の開口下端との間、好ましくは上澄液引
抜き下限レベルLWLと同じレベルがよい。また、上記
上方レベルスイッチ40aの検出位置(すなわち処理水
槽34の上限レベルH2WL)は、当然上記下方レベル
スイッチ40bの液面検出位置を越えた高い位置で、生
物処理槽10の上澄液が上澄液引抜き管14を介して処
理水槽34内に流入して生物処理槽10と処理水槽34
の液面が互いに一致する(バランスする)仮想液面以下
の高さであり、好ましくは上澄液引抜き下限レベルLW
Lを越えた該上澄液引抜き下限レベル近傍のレベルがよ
い。
The capacity of the treated water tank 34 is much smaller than the amount of water treated in one cycle of the biological treatment tank 10. Furthermore, the liquid level detection position height of the lower level switch 40b (that is, the lower limit level L 2 W of the treated water tank 34).
L) is the lower limit level LW for extracting the supernatant of the biological treatment tank 10.
It may be equal to or lower than L, and may be equal to or lower than the level of the opening end of the communication pipe 13 depending on the capacity of the treated water tank 34 and the timing of switching from natural flow to be described later to withdrawal by the pump 36. Between the same level of LWL and the lower end of the opening of the communication tube 13, preferably the same level as the supernatant withdrawal lower limit level LWL. Further, the detection position of the upper level switch 40a (that is, the upper limit level H 2 WL of the treated water tank 34) is naturally higher than the liquid level detection position of the lower level switch 40b, and the supernatant of the biological treatment tank 10 is Flow into the treated water tank 34 through the supernatant liquid drawing pipe 14 and enter the biological treatment tank 10 and the treated water tank 34.
The liquid level of the liquid is equal to or less than the imaginary liquid level at which the liquid levels of (1) and (2) are equal to each other.
A level close to the lower limit level of the supernatant liquid extraction above L is preferable.

【0021】なお、図中HWLは生物処理槽10の上澄
液引抜き上限レベルで、汚泥の静置分離工程における生
物処理槽10の水位に相当する。
In the figure, HWL is the upper limit level of the supernatant of the biological treatment tank 10 and corresponds to the water level of the biological treatment tank 10 in the sludge static separation step.

【0022】次に、上記構成の生物処理装置を用いた本
実施例の回分式生物処理における上澄液排出方法を説明
するが、これに先立って先ず起倒装置15の作用を説明
する。上記起倒装置15によって上澄液引抜き管14を
液面上に浮上させるには、電磁切換弁29を図1の位置
にして圧縮空気を上方の空気管26aからシリンダ本体
17bに供給し、ロッド17aを伸長させる。すると、
可動滑車20a,20bが下降して固定滑車21に接近
するが、ロッド17aの伸長端では上澄液引抜き管14
を上方に起立させていたワイヤーロープ22の長さに余
裕が生じることになり、これにより上澄液引抜き管14
は回転継手14eの部分で下方に回動して上澄液液面上
に浮上させられる。
Next, the method of discharging the supernatant liquid in the batch type biological treatment of this embodiment using the biological treatment apparatus having the above-described structure will be described. Prior to this, the operation of the erection device 15 will be described first. In order to float the supernatant liquid withdrawing pipe 14 above the liquid surface by the inversion device 15, the electromagnetic switching valve 29 is moved to the position shown in FIG. 1 and compressed air is supplied from the upper air pipe 26a to the cylinder body 17b, and the rod is moved. 17a is extended. Then,
The movable pulleys 20a and 20b descend and approach the fixed pulley 21, but at the extension end of the rod 17a, the supernatant drawing pipe 14
The wire rope 22 that has been erected upward has a margin in length, which causes the supernatant liquid drawing tube 14
Is rotated downward at the rotary joint 14e and floated above the supernatant liquid surface.

【0023】なおことのとき、ワイヤーロープ22はそ
の端部に錘24が設けられているため弛むことはない
が、上澄液の液面が上澄液引抜き上限レベルHWLにあ
るときは図1の如く錘24はガイド管23の下端まで下
降している。
At this time, the wire rope 22 is not loosened because the weight 24 is provided at the end thereof, but when the liquid level of the supernatant liquid is at the supernatant liquid extraction upper limit level HWL, FIG. As described above, the weight 24 descends to the lower end of the guide tube 23.

【0024】また、起倒装置15によって上澄液引抜き
管14を上方に起立させるには、電磁切換弁29を図1
0の位置に切換える。すると、圧縮空気が今度は下方の
空気管26bからシリンダ本体17bに入ってロッド1
7aが収縮し、これにより、可動滑車20a,20bが
上昇して固定滑車21から離間していく。ワイヤーロー
プ22は可動滑車20a,20bと固定滑車21に交互
に巻回されているから、可動滑車20a,20bの上昇
に伴ってワイヤーロープ22が引上げられて先ず錘24
がストッパ30に当たり、錘24がストッパ30に係止
されてそれ以上の上昇ができなくなると、今度は上澄液
引抜き管14がワイヤロープ22を介して引上げられて
図10の如くの起立状態となる。
In order to raise the supernatant drawing pipe 14 upward by the raising / lowering device 15, the electromagnetic switching valve 29 is used as shown in FIG.
Switch to the 0 position. Then, the compressed air enters the cylinder body 17b from the lower air pipe 26b, and then the rod 1
7a contracts, whereby the movable pulleys 20a, 20b rise and move away from the fixed pulley 21. Since the wire rope 22 is wound around the movable sheaves 20a and 20b and the fixed sheave 21 alternately, the wire rope 22 is pulled up as the movable sheaves 20a and 20b rise, and the weight 24 is first pulled.
When the weight hits the stopper 30 and the weight 24 is locked by the stopper 30 and cannot rise further, this time, the supernatant liquid withdrawing pipe 14 is pulled up via the wire rope 22 and the standing state as shown in FIG. Become.

【0025】次に、上記構成の生物処理装置において、
液面が上澄液引抜き上限レベルHWLにある生物処理槽
10の上澄液を排出する場合について説明する。この場
合は起倒装置15を上述したようにして作動させて上澄
液引抜き管14を液面上に浮上させる。すると、生物処
理槽10内の上澄液は、まず処理水槽34の下限レベル
2WLが連通管13の開口端のレベル以下の場合は、
生物処理槽10の液面と連通管13開口端とのレベル差
により、抜出し口12から上澄液引抜き管14の内部に
入って自然流下し、連通管13を経て処理水槽34内に
流入する。さらに、処理水槽34の液面が連通管13開
口端を越えた状態になると、または処理水槽34の下限
レベルL2WLが連通管13の開口端のレベルを越えた
状態に始めから設定されていると、生物処理槽の上澄液
と処理水槽の引抜かれた上澄液とが上記上澄液引抜き管
を介してU字管状的に連通状態になり、生物処理槽から
の上澄液引抜き速度は、生物処理槽の液面レベルと処理
水槽の液面レベルとの差により規制され、生物処理槽の
液面レベルと上澄液引抜き管開口端のレベルとの差に基
づく上記自然流下速度より必然的に遅くなる。処理水槽
34の容量は極めて小さいのですぐに処理水槽34の液
面が上がって上方のレベルスイッチ40aが入り、ポン
プ36が起動され、これにより処理水槽34内の上澄液
は放流管35を通じて放流される。
Next, in the biological treatment apparatus having the above structure,
A case will be described in which the supernatant of the biological treatment tank 10 whose liquid level is at the upper limit level HWL for extracting the supernatant is discharged. In this case, the reversing device 15 is operated as described above to float the supernatant liquid drawing tube 14 above the liquid surface. Then, when the lower limit level L 2 WL of the treated water tank 34 is equal to or lower than the level of the open end of the communication pipe 13, the supernatant liquid in the biological treatment tank 10 is
Due to the level difference between the liquid level of the biological treatment tank 10 and the opening end of the communication pipe 13, the liquid enters the supernatant liquid drawing pipe 14 from the outlet 12 and flows down naturally, and then flows into the treated water tank 34 via the communication pipe 13. . Further, when the liquid level of the treated water tank 34 exceeds the opening end of the communication pipe 13, or the lower limit level L 2 WL of the treated water tank 34 is set to the state of exceeding the level of the opening end of the communication pipe 13 from the beginning. Then, the supernatant liquid of the biological treatment tank and the drawn supernatant liquid of the treated water tank become in a U-shaped tubular communication state through the above-mentioned supernatant liquid extraction pipe, and the supernatant liquid is withdrawn from the biological treatment tank. The speed is regulated by the difference between the liquid level of the biological treatment tank and the liquid level of the treated water tank, and the above natural flow rate is based on the difference between the liquid level of the biological treatment tank and the level of the supernatant drawing pipe opening end. Inevitably slower. Since the capacity of the treated water tank 34 is extremely small, the liquid level of the treated water tank 34 immediately rises, the upper level switch 40a is turned on, and the pump 36 is activated, whereby the supernatant liquid in the treated water tank 34 is discharged through the discharge pipe 35. To be done.

【0026】この場合、通常、放流に伴って生物処理槽
10と処理水槽34の液面レベルが略一致(バランス)
して降下するようにポンプ36による上澄液の放流を調
節する。すなわち、処理水槽に受入れられた上澄液の排
出量(排出速度)を、例えば、生物処理槽の液面レベル
と処理水槽の液面レベルとの差に基づく生物処理槽から
の上澄液引抜き速度より遅くすると、生物処理槽と処理
水槽の液面が略一致(バランス)する状態となり、その
後の生物処理槽の上澄液の引抜き量は処理水槽からの排
出量と略等しくなる。したがって、生物処理槽の液面レ
ベルと上澄液引抜き管開口端のレベルとの差に基づく従
来の自然流下による場合よりも極めて小さい引抜き量
(流速)で上澄液を引抜くことができ、上澄液への汚泥
の混入が従来より一層少なくなる。また、汚泥の沈降性
状が変化した場合、その状況に合わせて処理水槽からの
排出量を調整することにより、生物処理槽10の上澄液
の引抜き速度を調整する。つまり、生物処理槽10の上
澄液の引抜き流量は、ポンプ36による上澄液の排出流
量を調整することにより調整することができ、そのポン
プ36による上澄液の排出流量の調整は、放流管35に
設けた流量調整弁38あるいはポンプ36の回転制御等
の公知手段によって行うことができる。
In this case, normally, the liquid surface levels of the biological treatment tank 10 and the treated water tank 34 substantially match (balance) with the discharge.
The discharge of the supernatant liquid by the pump 36 is adjusted so as to descend. That is, the discharge amount (drainage rate) of the supernatant liquid received in the treated water tank is determined based on, for example, the difference between the liquid surface level of the biological treatment tank and the liquid surface level of the treated water tank. If the speed is slower than the speed, the liquid levels of the biological treatment tank and the treated water tank will be substantially the same (balanced), and the amount of supernatant liquid withdrawn thereafter will be substantially equal to the amount discharged from the treated water tank. Therefore, the supernatant can be withdrawn with a significantly smaller withdrawal amount (flow velocity) than in the case of conventional natural flow based on the difference between the liquid level of the biological treatment tank and the level of the supernatant of the supernatant withdrawal pipe, The amount of sludge mixed in the supernatant liquid is further reduced than before. When the sedimentation property of the sludge changes, the discharge rate from the treated water tank is adjusted according to the situation to adjust the withdrawal rate of the supernatant of the biological treatment tank 10. That is, the withdrawal flow rate of the supernatant of the biological treatment tank 10 can be adjusted by adjusting the discharge flow rate of the supernatant liquid by the pump 36, and the discharge flow rate of the supernatant liquid with the pump 36 is adjusted by releasing the discharge. It can be performed by a known means such as rotation control of the flow rate adjusting valve 38 provided in the pipe 35 or the pump 36.

【0027】一方、上澄液の引抜きが進んで生物処理槽
10の液面が上澄液引抜き下限レベルLWLに達すると
生物処理槽10の第1レベルスイッチ33がこれを検知
し、その検知信号によって起倒装置15が作動して上澄
液引抜き管14が上昇し、上澄液の引抜きが停止され
る。また、ポンプ36は、処理水槽34の液面が下限レ
ベルL2WLに達し、下方レベルスイッチ40bがこれ
を検知するまで運転される。
On the other hand, when the supernatant liquid withdrawal progresses and the liquid level of the biological treatment tank 10 reaches the supernatant liquid extraction lower limit level LWL, the first level switch 33 of the biological treatment tank 10 detects this and the detection signal thereof. Thus, the inversion device 15 is activated to raise the supernatant withdrawing tube 14 and stop the withdrawal of the supernatant. Further, the pump 36 is operated until the liquid level of the treated water tank 34 reaches the lower limit level L 2 WL and the lower level switch 40b detects this.

【0028】このように、本実施例の回分式生物処理に
おける上澄液排出方法においては、生物処理槽10から
の上澄液の抜出しが、生物処理槽10の液面と連通管1
3開口端とのレベル差に基づく自然流下や生物処理槽の
液面レベルと処理水槽の液面レベルとの差に基づく上澄
液の引抜きから、すぐに、処理水槽10の液面が上記上
澄液引抜き管開口端を越えた状態でのポンプ36による
抜出し制御に変えられるから、ポンプ36による処理水
槽34からの上澄液の排出流量を調整することにより、
生物処理槽10からの上澄液の引抜き流量を予め調整す
ることができる。
As described above, in the supernatant discharging method in the batch type biological treatment of this embodiment, the supernatant liquid is extracted from the biological treatment tank 10 and the communicating pipe 1
3 From the natural flow-down based on the level difference from the opening end and the drawing of the supernatant liquid based on the difference between the liquid level of the biological treatment tank and the liquid level of the treated water tank, the liquid level of treated water tank 10 immediately rises to the above level. Since the withdrawal control by the pump 36 in a state of exceeding the opening end of the clear liquid withdrawal tube can be changed, by adjusting the discharge flow rate of the supernatant liquid from the treated water tank 34 by the pump 36,
The withdrawal flow rate of the supernatant liquid from the biological treatment tank 10 can be adjusted in advance.

【0029】このように、生物処理槽10内の液面と連
通管13開口端とのレベル差による自然流下よりも小さ
い引抜き流量(流速)で上澄液を引抜くから、上澄液へ
の汚泥の混入が従来より一層少なくなり、またこのこと
により、静置分離工程において汚泥が完全に上澄液引抜
き下限レベルLWL以下の所定レベルまで沈殿していな
くとも、この静置分離工程の途中(例えば汚泥の沈殿が
所定レベルの40%〜70%しか沈殿していない時点)
でも静置分離工程と並行して上澄液引抜き工程を開始す
ることができ、結果的には静置分離工程と上澄液引抜き
工程との総合計時間を短縮することができる。また、上
記の自然流下からポンプ36による抜出しへの切換えの
タイミングは上方レベルスイッチ40aと下方レベルス
イッチ40bの取付け位置を調整することにより最適に
設定することができる。
As described above, since the supernatant liquid is drawn out at a drawing flow rate (flow velocity) smaller than the natural flow due to the level difference between the liquid level in the biological treatment tank 10 and the opening end of the communication pipe 13, Contamination of sludge is further reduced than before, and even if sludge is not completely settled to a predetermined level below the lower limit level LWL of supernatant extraction in the stationary separation step, this still separation step ( For example, when the sludge settles only 40% to 70% of the predetermined level)
However, the supernatant drawing process can be started in parallel with the stationary separation process, and as a result, the total time of the stationary separation process and the supernatant drawing process can be shortened. Further, the timing of switching from the natural flow down to the extraction by the pump 36 can be optimally set by adjusting the mounting positions of the upper level switch 40a and the lower level switch 40b.

【0030】さらに、生物処理槽10の上澄液が上澄液
引抜き管14を介して処理水槽34に流入するのは、生
物処理槽10の液面と処理水槽34の液面または連通管
13の開口とのレベル差によるので、生物処理槽10に
おける液面が上澄液引抜き下限レベルLWLに近くなれ
ば、上記ポンプ36が仮に何らかの原因で大きな吐出流
量で運転されていたとしても、上澄液の引抜き量は、生
物処理槽10の液面と処理水槽34の液面とのレベル差
による流れに制約され、さらにたとえ処理水槽34内の
液面が連通管13開口端以下に下がっても、生物処理槽
10の液面レベルと連通管13開口端のレベルとの差に
基づく従来の自然流下量(速度)に制約され、処理水槽
からの上記速い排出速度に影響されることがなく、上澄
液の引抜きが安全に行われる。
Further, the supernatant liquid of the biological treatment tank 10 flows into the treated water tank 34 through the supernatant liquid withdrawal pipe 14 because the liquid surface of the biological treatment tank 10 and the liquid surface of the treated water tank 34 or the communicating pipe 13 are provided. Since the liquid level in the biological treatment tank 10 becomes close to the supernatant liquid extraction lower limit level LWL, even if the pump 36 is operated at a large discharge flow rate for some reason, The liquid withdrawal amount is restricted by the flow due to the level difference between the liquid surface of the biological treatment tank 10 and the liquid surface of the treated water tank 34, and even if the liquid surface in the treated water tank 34 drops below the opening end of the communication pipe 13. Is restricted by the conventional natural flow rate (velocity) based on the difference between the liquid level of the biological treatment tank 10 and the level of the communication pipe 13 at the open end, and is not affected by the above-mentioned fast discharge rate from the treated water tank, Safe withdrawal of supernatant It takes place.

【0031】ところで、上記実施例において、下方レベ
ルスイッチ40bを生物処理槽10の第1レベルスイッ
チ33と同じレベルまたはそのレベルの近傍に設ける場
合は、生物処理槽10の第1レベルスイッチ33と上記
下方レベルスイッチ40bを一つのレベルスイッチで処
理するようにしてどちらか一方を省略することができ、
また第1レベルスイッチ33または上記下方レベルスイ
ッチ40bに代えて低流量のポンプ36の吐出側配管に
積算流量計を取付け、これにより生物処理槽10の1サ
イクルで排出される上澄液量と等しい液量が処理水槽3
4から排出されたのを検知してポンプ36を停止するよ
うにしてもよい。
By the way, in the above embodiment, when the lower level switch 40b is provided at the same level as the first level switch 33 of the biological treatment tank 10 or in the vicinity of the level, the first level switch 33 of the biological treatment tank 10 and the above The lower level switch 40b can be processed by one level switch, and either one can be omitted.
Further, instead of the first level switch 33 or the lower level switch 40b, an integrated flow meter is attached to the discharge side pipe of the low flow rate pump 36, whereby the amount of the supernatant liquid discharged in one cycle of the biological treatment tank 10 is equal. Liquid volume is treated water tank 3
The pump 36 may be stopped upon detection of discharge from the pump 4.

【0032】さらに上記実施例においてポンプ36を起
動する手段として上方レベルスイッチ40aを用いた
が、上澄液引抜きの初期には生物処理槽10と処理水槽
34の液面を一致させ、もはや連通管13内を上澄液が
流れないようにすることができるので、上記上方レベル
スイッチ40aに代えてタイマを用い、このタイマが上
澄液引抜きが開始された信号例えば起倒装置15の電磁
切換弁29の作動信号を受け、その信号を受けた時から
予め定めた時間にポンプ36を起動するようにしてもよ
い。したがってポンプを起動停止する制御手段は直接ま
たは間接に処理水槽34の液面を検知できるものであれ
ばよい。また、上澄液引抜きの開始及び終了を起倒装置
15によらず、図13の如く弁3を開閉することにより
行っても勿論構わない。
Further, in the above-mentioned embodiment, the upper level switch 40a is used as means for starting the pump 36. However, the liquid levels of the biological treatment tank 10 and the treated water tank 34 are made to coincide with each other at the initial stage of withdrawing the supernatant liquid, and the communicating pipe is no longer used. Since it is possible to prevent the supernatant liquid from flowing inside 13, a timer is used instead of the above-mentioned upper level switch 40a, and this timer gives a signal indicating that the supernatant liquid extraction has started, for example, an electromagnetic switching valve of the inversion device 15. Alternatively, the pump 36 may be started at a predetermined time from the time when the operation signal of 29 is received. Therefore, the control means for starting and stopping the pump may be one that can directly or indirectly detect the liquid surface of the treated water tank 34. Further, of course, the start and end of the supernatant liquid withdrawal may be performed by opening and closing the valve 3 as shown in FIG.

【0033】さらに、生物処理槽10内に連続的または
断続的に液面レベルと汚泥界面を測定できる液面レベル
計と汚泥界面計とを備え、液面と汚泥界面とのレベル差
に基づいて制御装置によって流量調整弁38またはポン
プ36の回転数を制御し、ポンプ36による上澄液の排
出量を連続的に制御するようにしてもよい。
Furthermore, the biological treatment tank 10 is provided with a liquid level meter and a sludge interface meter capable of continuously or intermittently measuring the liquid level and the sludge interface, and based on the level difference between the liquid surface and the sludge interface. The controller may control the rotation speed of the flow rate adjusting valve 38 or the pump 36 to continuously control the discharge amount of the supernatant liquid by the pump 36.

【0034】またさらに、連通管13の開口端部に回転
継手を介してさらに他の曲り管等を接続し、該曲り管等
の回動位置を変えることにより連通管の開口端の高さを
調整できるようにすることもできる。本発明は上澄液引
抜き管の構成を、例えば、図13のように、連通管と一
体とすることもできる。
Further, another bent pipe or the like is connected to the open end of the communicating pipe 13 through a rotary joint, and the rotational position of the bent pipe or the like is changed to thereby increase the height of the open end of the communicating pipe. It can also be adjustable. In the present invention, the structure of the supernatant liquid withdrawal pipe may be integrated with the communication pipe as shown in FIG. 13, for example.

【0035】[0035]

【発明の効果】以上説明したように、本発明の回分式生
物処理における上澄液排出方法は、生物処理槽で少なく
とも曝気工程と汚泥の沈殿工程と上澄液引抜き工程とを
有するサイクルを繰返して汚水処理を行う回分式生物処
理において、上記生物処理槽内に設けられ、先端部分に
フロートと上澄液の抜出し口を有して少なくとも該先端
部分が水位の変動に追従し、他端が処理水槽の上記生物
処理槽における上澄液引抜き下限レベル以下の位置で開
口する上澄液引抜き管により上記生物処理槽の上澄液を
引抜く上澄液排出方法であって、生物処理槽からの上澄
液排出速度が、該生物処理槽の液面レベルと上澄液引抜
き管開口端のレベルとの差に基づく自然流下速度より遅
くなるように、生物処理槽から引抜かれた処理水槽の上
澄液の液面が上記上澄液引抜き管開口端を越えた状態で
上記処理水槽に受入れられた上澄液の排出量を制御する
構成とされているから、上澄液への汚泥の混入を確実に
防止して、汚泥の静置分離工程中であっても上澄液の引
抜きを開始することができ、結果的に静置分離工程と上
澄液引抜き工程の合計時間を短縮することができる。ま
た、汚泥の性状等の状況に合せて上澄液引抜き時間を調
整できる等の効果を奏する。
Industrial Applicability As described above, the method of discharging a supernatant liquid in the batch type biological treatment of the present invention repeats a cycle having at least an aeration step, a sludge precipitation step and a supernatant liquid withdrawal step in the biological treatment tank. In a batch type biological treatment in which sewage treatment is performed by using a biological treatment tank, the tip portion has a float and a supernatant liquid outlet, and at least the tip portion follows fluctuations in water level, and the other end is A method of discharging a supernatant liquid of the biological treatment tank by a supernatant liquid extraction pipe that opens at a position below the lower limit level of the supernatant liquid extraction in the biological treatment tank of the treated water tank. Of the treated water tank drawn out from the biological treatment tank so that the supernatant discharge speed of the biological treatment tank becomes slower than the natural flow rate based on the difference between the liquid level of the biological treatment tank and the level of the opening of the supernatant drawing tube. The liquid level of the supernatant is above Since it is configured to control the discharge amount of the supernatant liquid received in the treated water tank above the opening of the clear liquid drawing tube, it is possible to reliably prevent the mixing of sludge into the supernatant liquid, The withdrawal of the supernatant can be started even during the stationary separation step, and as a result, the total time of the stationary separation step and the supernatant withdrawal step can be shortened. In addition, the supernatant liquid withdrawing time can be adjusted according to the condition of sludge properties.

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

【図1】 本発明を実施する回分式生物処理装置の断面
図である。
FIG. 1 is a sectional view of a batch type biological treatment apparatus for carrying out the present invention.

【図2】 上澄液引抜き管の平面図である。FIG. 2 is a plan view of a supernatant drawing tube.

【図3】 同じく、要部断面の側面図である。FIG. 3 is likewise a side view of the cross section of the main part.

【図4】 図2のIV−IV矢視断面図である。FIG. 4 is a sectional view taken along the line IV-IV in FIG.

【図5】 起倒装置の拡大図である。FIG. 5 is an enlarged view of the tilting device.

【図6】 図5のVI−VI矢視断面図である。6 is a sectional view taken along the line VI-VI of FIG.

【図7】 図5のVII−VII矢視断面図である。7 is a sectional view taken along the line VII-VII of FIG.

【図8】 図5のVIII−VIII矢視図である。FIG. 8 is a view on arrow VIII-VIII in FIG.

【図9】 排水処理工程の説明図である。FIG. 9 is an explanatory diagram of a wastewater treatment process.

【図10】 作用を説明するための全体の断面図であ
る。
FIG. 10 is an overall cross-sectional view for explaining the operation.

【図11】 同じく、作用を説明するための全体の断面
図である。
FIG. 11 is also an overall cross-sectional view for explaining the operation.

【図12】 従来例を示す断面略図である。FIG. 12 is a schematic sectional view showing a conventional example.

【図13】 他の従来例を示す断面略図である。FIG. 13 is a schematic sectional view showing another conventional example.

【符号の説明】[Explanation of symbols]

10 生物処理槽 11 フロート 12 抜出し口 14 上澄液引抜き管 34 処理水槽 10 Biological Treatment Tank 11 Float 12 Extraction Port 14 Supernatant Extraction Pipe 34 Treated Water Tank

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 生物処理槽で少なくとも曝気工程と汚泥
の沈殿工程と上澄液引抜き工程とを有するサイクルを繰
返して汚水処理を行う回分式生物処理において、上記生
物処理槽内に設けられ、先端部分にフロートと上澄液の
抜出し口を有して少なくとも該先端部分が水位の変動に
追従し、他端が処理水槽の上記生物処理槽における上澄
液引抜き下限レベル以下の位置で開口する上澄液引抜き
管により上記生物処理槽の上澄液を引抜く上澄液排出方
法であって、生物処理槽からの上澄液排出速度が、該生
物処理槽の液面レベルと上澄液引抜き管開口端のレベル
との差に基づく自然流下速度より遅くなるように、生物
処理槽から引抜かれた処理水槽の上澄液の液面が上記上
澄液引抜き管開口端を越えた状態で上記処理水槽に受入
れられた上澄液の排出量を制御することを特徴とする回
分式生物処理における上澄液排出方法。
1. A batch type biological treatment in which a cycle of at least an aeration step, a sludge precipitation step, and a supernatant liquid withdrawing step is repeated in the biological treatment tank to perform wastewater treatment, and the tip is provided in the biological treatment tank. At least the tip part follows the fluctuation of the water level with a float and a supernatant liquid outlet in the part, and the other end opens at a position below the lower limit level of the supernatant liquid withdrawal in the biological treatment tank of the treated water tank. A method of discharging a supernatant liquid by extracting a supernatant liquid of the biological treatment tank by a supernatant liquid extraction pipe, wherein a supernatant discharge speed from the biological treatment tank is a liquid level of the biological treatment tank and a supernatant liquid extraction. The liquid level of the supernatant of the treated water tank drawn out from the biological treatment tank exceeds the above-mentioned supernatant drawing tube opening end so as to be slower than the natural flow rate based on the difference from the level at the tube opening end. Discharge of the supernatant received in the treated water tank A method for discharging a supernatant liquid in a batch-type biological treatment, which comprises controlling an output amount.
JP5009551A 1993-01-22 1993-01-22 Supernatant discharge method in batch biological treatment Expired - Fee Related JPH0736918B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5009551A JPH0736918B2 (en) 1993-01-22 1993-01-22 Supernatant discharge method in batch biological treatment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5009551A JPH0736918B2 (en) 1993-01-22 1993-01-22 Supernatant discharge method in batch biological treatment

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
JP60234724A Division JPS6295198A (en) 1985-10-21 1985-10-21 Batch type biological treatment tank

Publications (2)

Publication Number Publication Date
JPH06312195A JPH06312195A (en) 1994-11-08
JPH0736918B2 true JPH0736918B2 (en) 1995-04-26

Family

ID=11723419

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5009551A Expired - Fee Related JPH0736918B2 (en) 1993-01-22 1993-01-22 Supernatant discharge method in batch biological treatment

Country Status (1)

Country Link
JP (1) JPH0736918B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE60036686T2 (en) * 1999-10-22 2008-07-17 Teijin Ltd. Laminated base film for a thermal transfer recording medium
JP5213153B2 (en) * 2007-06-13 2013-06-19 学校法人 芝浦工業大学 Purification method of contaminated seawater by seawater-derived microorganisms
JP7144497B2 (en) * 2020-10-01 2022-09-29 株式会社日水コン Supernatant water drainage device and supernatant water drainage method

Also Published As

Publication number Publication date
JPH06312195A (en) 1994-11-08

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