JPH022479Y2 - - Google Patents

Info

Publication number
JPH022479Y2
JPH022479Y2 JP1982063355U JP6335582U JPH022479Y2 JP H022479 Y2 JPH022479 Y2 JP H022479Y2 JP 1982063355 U JP1982063355 U JP 1982063355U JP 6335582 U JP6335582 U JP 6335582U JP H022479 Y2 JPH022479 Y2 JP H022479Y2
Authority
JP
Japan
Prior art keywords
reaction tank
centrifugal
liquid
sludge
mlss
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
JP1982063355U
Other languages
Japanese (ja)
Other versions
JPS58166897U (en
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 filed Critical
Priority to JP1982063355U priority Critical patent/JPS58166897U/en
Publication of JPS58166897U publication Critical patent/JPS58166897U/en
Application granted granted Critical
Publication of JPH022479Y2 publication Critical patent/JPH022479Y2/ja
Granted legal-status Critical Current

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Classifications

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

Landscapes

  • Activated Sludge Processes (AREA)
  • Control Of Non-Electrical Variables (AREA)

Description

【考案の詳細な説明】 この考案は、単一の反応槽内でばつ気工程と沈
殿工程とを交互に繰返すことによつて汚水を処理
するバツチ式活性汚泥処理装置に関するものであ
る。
[Detailed Description of the Invention] This invention relates to a batch type activated sludge treatment apparatus that treats wastewater by alternately repeating an aeration process and a precipitation process in a single reaction tank.

従来のバツチ式活性汚泥処理装置において、処
理水の放流は、反応槽内で汚泥を沈殿させること
によつて上層部に分離した上澄液をデカンタを用
いて引抜くことによつて行われ、汚泥の引抜き
も、汚泥が沈殿している時期を選んで行われる。
沈殿した汚泥を引抜くことは、濃度の高い汚泥を
取出せる点で有利であるが、引抜き汚泥量の管理
が難しく、反応槽内に存在する汚泥量に過不足が
生じやすいという欠点がある。反応槽内の汚泥量
が少な過ぎると、生物学的処理が充分に行われな
いために処理水質が悪くなり、逆に多過ぎる場合
には、デカンタによる上澄液の放流時に汚泥がキ
ヤリーオーバーするなどの不都合が生じるので、
引抜汚泥量の制御はきわめて重要である。
In conventional batch-type activated sludge treatment equipment, treated water is discharged by precipitating sludge in a reaction tank and separating the supernatant liquid into an upper layer using a decanter. Sludge extraction is also carried out at a time when the sludge is settling.
Pulling out the precipitated sludge is advantageous in that highly concentrated sludge can be extracted, but it has the disadvantage that it is difficult to control the amount of sludge that is drawn out, and the amount of sludge present in the reaction tank is likely to be too large or too small. If the amount of sludge in the reaction tank is too small, the quality of the treated water will deteriorate because biological treatment is not carried out sufficiently, and if it is too large, the sludge will carry over when the supernatant liquid is discharged from the decanter. This may cause inconveniences such as
Control of the amount of sludge drawn is extremely important.

この考案は、反応槽内の汚泥量を所定の好適範
囲内に常に維持することにより、安定した処理条
件で汚水を処理できるようにしたバツチ式活性汚
泥処理装置を提供することを目的としている。
The purpose of this invention is to provide a batch type activated sludge treatment apparatus that can treat sewage under stable treatment conditions by always maintaining the amount of sludge in the reaction tank within a predetermined preferred range.

つぎにこの考案の一実施例について図面を参照
して説明する。図において、汚水を収容し得る反
応槽1の底部には、ばつ気工程で汚水に空気を吹
込むための散気管2が配設されている。また垂直
に配置されたバツフル3は、新たな流入汚水が直
ちに放流されるのを防止するためのものである。
Next, an embodiment of this invention will be described with reference to the drawings. In the figure, an aeration pipe 2 for blowing air into the wastewater in an aeration process is disposed at the bottom of a reaction tank 1 capable of containing wastewater. Further, the vertically arranged baffle 3 is for preventing newly inflowing sewage from being immediately discharged.

上澄液を放流するためのデカンタ4は、軸パイ
プ5に水平な軸心を中心として回動可能に連結さ
れた排出パイプ6と、この排出パイプ6の自由端
に取付けられた溢流管7と、この溢流管7の両側
に位置するスカムバツフルを兼ねたフロート8と
で構成されている。溢流管7には溢流口が設けて
あり、溢流管7が水面上に浮いている状態では、
反応槽1内の液体がこの溢流口から溢流管7内に
入り、ついで排出パイプ6および軸パイプ5を経
て外部に放流される。また溢流管7が水面よりも
高い位置に支持されている状態では、反応槽1内
の液体の放流は行われない。
The decanter 4 for discharging the supernatant liquid includes a discharge pipe 6 rotatably connected to a shaft pipe 5 about a horizontal axis, and an overflow pipe 7 attached to the free end of the discharge pipe 6. and floats 8, which also serve as scum baffles, located on both sides of this overflow pipe 7. The overflow pipe 7 is provided with an overflow port, and when the overflow pipe 7 is floating on the water surface,
The liquid in the reaction tank 1 enters the overflow pipe 7 from this overflow port, and is then discharged to the outside via the discharge pipe 6 and the shaft pipe 5. Further, in a state where the overflow pipe 7 is supported at a position higher than the water surface, the liquid in the reaction tank 1 is not discharged.

さらに反応槽1内から汚泥を引抜くための引抜
パイプ9は、遠心濃縮機の1種である遠心過濃
縮機10に接続されている。この遠心過濃縮装
置10は、コーン形の回転ドラムの内面に布を
敷き、この回転ドラムを高速回転させながら布
上に被濃縮液を供給する形式のもので、布を通
過した液は反応槽1内に戻され、布上から遠
心力で放出された濃縮汚泥は外部に取出される。
また遠心過濃縮機10の運転を制御するため
に、反応槽1内の適当な位置に検出端11aを配
置したMLSS計11が設けられている。この
MLSS計11は、ばつ気工程中に反応槽1内の液
体のMLSSを計測し、その計測があらかじめ設定
した設定値よりも高いときだけ、引抜きパイプ9
を通して反応槽1内の液体を引抜き、遠心過濃
縮機10で過したのち、濃縮汚泥を外部に取出
す動作を行わせ、これによつて反応槽1内の液体
のMLSSが低下してくる。この濃縮汚泥の引抜き
は、MLSSの計測値が設定値以上であることが検
出されてから一定時間だけ行うようにしてもよ
く、あるいは引抜き中もMLSS濃度を計測し、こ
の計測値が所定の下限値に達するまで継続しても
よい。
Further, a drawing pipe 9 for drawing sludge out of the reaction tank 1 is connected to a centrifugal superconcentrator 10, which is a type of centrifugal thickener. This centrifugal superconcentrator 10 is of a type in which a cloth is spread on the inner surface of a cone-shaped rotating drum, and the liquid to be concentrated is supplied onto the cloth while rotating the rotating drum at high speed. The thickened sludge returned to the inside of the cloth and released from the cloth by centrifugal force is taken out to the outside.
Further, in order to control the operation of the centrifugal superconcentrator 10, an MLSS meter 11 having a detection end 11a disposed at an appropriate position within the reaction tank 1 is provided. this
The MLSS meter 11 measures the MLSS of the liquid in the reaction tank 1 during the aeration process, and only when the measured value is higher than a preset value, the drawn pipe 9
After the liquid in the reaction tank 1 is drawn out through the centrifugal thickener 10, the thickened sludge is taken out to the outside, thereby reducing the MLSS of the liquid in the reaction tank 1. The drawing of this thickened sludge may be carried out only for a certain period of time after it is detected that the measured value of MLSS is equal to or higher than a set value, or the MLSS concentration may be measured even during drawing, and this measured value may be a predetermined lower limit. It may continue until the value is reached.

またMLSS計11は、デカンタ4による上澄液
の放流時に、汚泥がキヤリーオーバーするのを防
止するための指標としても利用することができ
る。この場合には、MLSS計11の検出端11a
は、放流時にキヤリーオーバーが起らない範囲で
最も高い位置に汚泥面がある状態での汚泥面を検
出できる位置に設置され、放流時にもMLSSの計
測が行われる。汚泥面が検出端11aよりも低け
れば、MLSSの計測値は低く、これによつてキヤ
リーオーバーのおそれがないことがわかる。また
汚泥面が検出端11aの位置よりも高い場合に
は、放流を中止し、沈殿時間を長くとるとか、ば
つ気風量を多くしてばつ気時間を短かくするなど
の適宜の措置をとることができる。
The MLSS meter 11 can also be used as an indicator to prevent sludge from carrying over when the supernatant liquid is discharged from the decanter 4. In this case, the detection end 11a of the MLSS meter 11
is installed at a position where it can detect the sludge surface at the highest level within the range where carry over does not occur during discharge, and MLSS measurements are also performed during discharge. If the sludge surface is lower than the detection end 11a, the measured value of MLSS is low, which indicates that there is no risk of carry over. In addition, if the sludge surface is higher than the position of the detection end 11a, take appropriate measures such as stopping the discharge and increasing the settling time or increasing the aeration air volume to shorten the aeration time. Can be done.

以上のようにこの考案によれば、バツチ式単一
曝気槽内のMLSSを計測して該計測値が設定値以
上になつた時にのみ出力するMLSS計と、該
MLSS計の出力信号で稼動する遠心濃縮機とだけ
の組合せにより、上記曝気槽内のMLSSを制御で
き、その他の制御要素を一切必要としないので、
構成が簡単で大幅なコスト高が抑えられ、メンテ
ナンスも容易であり、しかも、上記遠心濃縮機
は、上記MLSS計の出力信号による稼動時に上記
反応槽内の液体を引抜いて濃縮汚泥と濾液とに分
離し、その濃縮汚泥を排出する一方で上記濾液の
みを上記反応槽内に返送するので、その濾液返送
により、反応槽で過剰になりつつあるMLSSが上
記設定値まで薄められ、もつて、反応槽内の
MLSSを常時安定状態に維持でき、安定した活性
汚泥処理が行えると共に、単一反応槽内における
汚泥のキヤリーオーバーなどの不都合を未然に防
止できるなどの効果がある。
As described above, according to this invention, there is an MLSS meter that measures MLSS in a batch type single aeration tank and outputs only when the measured value exceeds a set value, and
The MLSS in the aeration tank can be controlled simply by combining it with a centrifugal concentrator operated by the output signal of the MLSS meter, and no other control elements are required.
The configuration is simple, significantly reducing costs, and maintenance is easy.Moreover, the centrifugal concentrator draws out the liquid in the reaction tank and converts it into concentrated sludge and filtrate when activated by the output signal of the MLSS meter. The concentrated sludge is separated and the concentrated sludge is discharged, while only the filtrate is returned to the reaction tank. By returning the filtrate, the MLSS that is becoming excessive in the reaction tank is diluted to the above set value, and the reaction begins. inside the tank
The MLSS can be maintained in a stable state at all times, allowing stable activated sludge treatment to be performed, and has the effect of preventing inconveniences such as sludge carry-over within a single reaction tank.

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

図はこの考案の一実施例によるバツチ式活性汚
泥処理装置を示す概略的縦断面図である。 1……反応槽、2……散気管、3……バツフ
ル、4……デカンタ、9……引抜パイプ、10…
…遠心過濃縮装置、11……MLSS計、11a
……検出端。
The figure is a schematic longitudinal sectional view showing a batch type activated sludge treatment apparatus according to an embodiment of the invention. 1... Reaction tank, 2... Diffusion pipe, 3... Buzzful, 4... Decanter, 9... Drawn pipe, 10...
...Centrifugal superconcentrator, 11...MLSS meter, 11a
...Detection end.

Claims (1)

【実用新案登録請求の範囲】[Scope of utility model registration request] 流入汚水を受け入れ、ばつ気工程と沈殿工程お
よび放流工程をその工程順序で繰返し行う単一の
反応槽と、上記ばつ気工程時に上記反応槽内の液
体中に空気を吹込むための散気管と、上記反応槽
内に装備され、上記放流工程で上澄液を放流する
デカンタと、上記反応槽内のばつ気混合液を取り
込んで濾液と濃縮汚泥とに分離する遠心濃縮機
と、上記反応槽内の液中に浸漬定置され上記反応
槽内のばつ気混合液の浮遊物質濃度を計測し、該
計測値が設定値を越えた時点でのみ上記遠心濃縮
機に起動信号を出力して該遠心濃縮機を稼動させ
るMLSS計とを備え、このMLSS計からの入力信
号による上記遠心濃縮機の稼動時に該遠心濃縮機
で分離された濃縮汚泥を外部に排出し且つ濾液を
上記反応槽内に返送することを特徴とするバツチ
式活性汚泥処理装置。
a single reaction tank that receives inflow sewage and repeats an aeration process, a precipitation process, and a discharge process in that process order; an aeration pipe for blowing air into the liquid in the reaction tank during the aeration process; A decanter that is installed in the reaction tank and discharges the supernatant liquid in the discharge process, a centrifugal concentrator that takes in the atomized mixed liquid in the reaction tank and separates it into a filtrate and thickened sludge, and The concentration of suspended solids in the atomized mixed liquid in the reaction tank is immersed and fixed in the liquid, and only when the measured value exceeds a set value, a start signal is output to the centrifugal concentrator. and an MLSS meter that operates the centrifugal thickener, and when the centrifugal thickener is operated by an input signal from the MLSS meter, the thickened sludge separated by the centrifugal thickener is discharged to the outside, and the filtrate is returned to the reaction tank. Batch-type activated sludge treatment equipment featuring:
JP1982063355U 1982-04-30 1982-04-30 Batch type activated sludge treatment equipment Granted JPS58166897U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1982063355U JPS58166897U (en) 1982-04-30 1982-04-30 Batch type activated sludge treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1982063355U JPS58166897U (en) 1982-04-30 1982-04-30 Batch type activated sludge treatment equipment

Publications (2)

Publication Number Publication Date
JPS58166897U JPS58166897U (en) 1983-11-07
JPH022479Y2 true JPH022479Y2 (en) 1990-01-22

Family

ID=30073460

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1982063355U Granted JPS58166897U (en) 1982-04-30 1982-04-30 Batch type activated sludge treatment equipment

Country Status (1)

Country Link
JP (1) JPS58166897U (en)

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5549196A (en) * 1978-10-04 1980-04-09 Toshiba Corp Control method for excess sludge extraction
JPS565186A (en) * 1979-06-26 1981-01-20 Yoshizumi Ogishima Microorganism concentration controller for activated sludge in aeration tank
JPS5697593A (en) * 1980-01-07 1981-08-06 Nobutsugu Kato Apparatus for controlling sludge turbidity in aeration vessel

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5549196A (en) * 1978-10-04 1980-04-09 Toshiba Corp Control method for excess sludge extraction
JPS565186A (en) * 1979-06-26 1981-01-20 Yoshizumi Ogishima Microorganism concentration controller for activated sludge in aeration tank
JPS5697593A (en) * 1980-01-07 1981-08-06 Nobutsugu Kato Apparatus for controlling sludge turbidity in aeration vessel

Also Published As

Publication number Publication date
JPS58166897U (en) 1983-11-07

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