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JPS64118B2 - - Google Patents
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JPS64118B2 - - Google Patents

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Publication number
JPS64118B2
JPS64118B2 JP58122232A JP12223283A JPS64118B2 JP S64118 B2 JPS64118 B2 JP S64118B2 JP 58122232 A JP58122232 A JP 58122232A JP 12223283 A JP12223283 A JP 12223283A JP S64118 B2 JPS64118 B2 JP S64118B2
Authority
JP
Japan
Prior art keywords
sludge
concentration
batch
reaction tank
activated sludge
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
JP58122232A
Other languages
Japanese (ja)
Other versions
JPS6014993A (en
Inventor
Tomio Suzuki
Yoichi Hamamoto
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.)
NISHIHARA KANKYO EISEI KENKYUSHO KK
Original Assignee
NISHIHARA KANKYO EISEI KENKYUSHO KK
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 NISHIHARA KANKYO EISEI KENKYUSHO KK filed Critical NISHIHARA KANKYO EISEI KENKYUSHO KK
Priority to JP58122232A priority Critical patent/JPS6014993A/en
Publication of JPS6014993A publication Critical patent/JPS6014993A/en
Publication of JPS64118B2 publication Critical patent/JPS64118B2/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

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  • Activated Sludge Processes (AREA)

Description

【発明の詳細な説明】 本発明は、活性汚泥法にもとづき汚水浄化処理
施設の運転及び管理をする際に、重要な指標とさ
れる各工程毎の汚泥状態の各種計測データを演算
装置によつて自動演算し、汚水処理を合理的最適
条件下で実施するバツチ式活性汚泥処理装置に関
する。
DETAILED DESCRIPTION OF THE INVENTION The present invention uses a computing device to collect various measurement data on the state of sludge in each process, which is an important indicator when operating and managing sewage purification facilities based on the activated sludge method. The present invention relates to a batch type activated sludge treatment device that automatically calculates the amount of wastewater and performs sewage treatment under rationally optimal conditions.

上記の各指標とはJIS−KO102「工場排水試験
方法」、又は「下水試験方法」等により次式のよ
うに表記されている。
Each of the above indicators is expressed as follows according to JIS-KO102 "Industrial Wastewater Test Method" or "Sewage Test Method".

SVI=SV×10000/MLSS …(1) SDI=MLSS/SV×100=100/SVI …(2) MLSS=a×1000/検体量(ml) …(3) SV=b/1000×100 …(4) 上式において、 SVI;汚泥容量指標 SDI;汚泥密度指標 MLSS;ばつ気槽内混合液の活性汚泥浮遊物濃
度〔mg/〕 SV;混合液の活性汚泥沈殿率(30分静置)
〔%〕 a;混合液検体中の活性汚泥浮遊物重量
〔mg〕 b;混合液体100ml中の30分静置後の沈殿
汚泥容量〔ml〕 しかし、上記(1)ないし(4)式のなかで(1)式のSVI
及び(2)式のSDIは計算式で算出されるが、その式
中のSV及びMLSSはばつ気槽から採取した混合
液体を分析しなければ得られない。また反応槽で
のSVは SV=H0/H1×100(%) …(5) 但し、 H0;反応槽の汚泥界面 H1;反応槽の最低水位 で表わされる。また汚泥引抜きの記録より活性汚
泥細胞平均滞留時間(SRT)を算出することが
できる。
SVI=SV×10000/MLSS…(1) SDI=MLSS/SV×100=100/SVI…(2) MLSS=a×1000/sample volume (ml)…(3) SV=b/1000×100…( 4) In the above formula, SVI: Sludge volume index SDI; Sludge density index MLSS: Activated sludge suspended solids concentration of the mixed solution in the aeration tank [mg/] SV: Activated sludge settling rate of the mixed solution (standing for 30 minutes)
[%] a; Weight of activated sludge suspended matter in mixed liquid sample [mg] b; Capacity of precipitated sludge after standing still for 30 minutes in 100 ml of mixed liquid [ml] However, in formulas (1) to (4) above, The SVI of equation (1) is
The SDI in equation (2) is calculated using a calculation formula, but the SV and MLSS in that equation can only be obtained by analyzing the mixed liquid collected from the aeration tank. The SV in the reaction tank is expressed as SV=H 0 /H 1 ×100 (%) (5) where H 0 is the sludge interface in the reaction tank, H 1 is the lowest water level in the reaction tank. Additionally, the average residence time (SRT) of activated sludge cells can be calculated from the sludge drawing records.

ここでSRTは SRT=反応槽内汚泥量(W1)/引抜き汚泥量
(W2)…(6) W1、W2は W1=S×H1×A …(7) W2=q×t×S×H1/H0×n …(8) ただし S;MLSS濃度(水位H1での)〔mg/〕 A;反応槽表面積〔m2〕 q;汚泥引抜ポンプ流量〔m3/min〕 t;汚泥引抜ポンプ稼動時間〔min/回〕 n;汚泥引抜ポンプ稼動回数〔回/日〕 上記、(6)、(7)、(8)式より SRT=S×H1×A/q×t×S×H1/H0×n =H0×A/q×t×n …(9) で表わされる。そしてSVとは、例えば、検体
1000mlを内径6.5cm、容量1のメスシリンダに
入れ30分静止後の沈殿汚泥容量と検体容量(1000
ml)との比を百分率で表わしたものである。
Here, SRT is SRT = Amount of sludge in the reaction tank (W 1 ) / Amount of sludge extracted (W 2 )...(6) W 1 and W 2 are W 1 = S x H 1 x A... (7) W 2 = q ×t×S×H 1 /H 0 ×n …(8) where S: MLSS concentration (at water level H 1 ) [mg/] A: Reaction tank surface area [m 2 ] q: Sludge extraction pump flow rate [m 3 /min] t: Operation time of the sludge extraction pump [min/times] n: Number of operations of the sludge extraction pump [times/day] From the above equations (6), (7), and (8), SRT=S×H 1 ×A /q×t×S×H 1 /H 0 ×n =H 0 ×A/q×t×n (9). And SV is, for example, the sample
Pour 1000ml into a measuring cylinder with an inner diameter of 6.5cm and a capacity of 1. After standing still for 30 minutes, settle the sludge volume and sample volume (1000ml).
ml) expressed as a percentage.

一方、MLSSは検体を重心分離法、あるいは濾
紙法などの定められた方法によつて浮遊固形物と
液体とに分離したあと、この固形物を蒸発乾固し
て得られた固形物重量と検体容量との比〔mg/
〕で表わされるものである。
On the other hand, in MLSS, the sample is separated into suspended solids and liquid by a specified method such as centroid separation method or filter paper method, and then the solids are evaporated to dryness. Ratio to capacity [mg/
].

上記のMLSSは前記混合液に光線や超音波を透
過した時に生ずる減衰量と良好な相関を示すの
で、その方式をとり入れた濃度計を用いて装定装
置としている。
Since the above MLSS shows a good correlation with the amount of attenuation that occurs when a light beam or an ultrasonic wave is transmitted through the mixed liquid, a densitometer incorporating this method is used as the mounting device.

すなわち、従来のバツチ式活性汚泥処理制御装
置は沈殿汚泥の界面高さを知る手段として汚泥界
面計を用い、更にMLSS濃度を知る手段としては
MLSS計を回分式反応槽の内部へ夫々別個に設置
していたため、装置構成が複雑になり、経済的に
不利なものになるという欠点があつた。また、汚
泥の引抜きも引抜きパイプなどの手動による汚泥
引抜き手段を用いることが多く上澄液のSS濃度、
SVI、SRTも充分測定されないままに処理がな
されるという欠点があつた。
In other words, the conventional batch type activated sludge treatment control equipment uses a sludge interface meter as a means of knowing the interface height of settled sludge, and also uses a sludge interface meter as a means of knowing the MLSS concentration.
Since the MLSS meters were installed separately inside each batch reaction tank, the device configuration was complicated and economically disadvantageous. In addition, manual sludge extraction methods such as extraction pipes are often used to extract sludge, and the SS concentration of the supernatant liquid,
SVI and SRT also had the disadvantage of being processed without being sufficiently measured.

本発明は上記のような従来のものの欠点を除去
するためになされたもので、MLSS計のような1
台の濃度検出手段により、ばつ気工程時にMLSS
を測定するばかりか、沈殿工程時に設定汚泥界面
高さでの汚泥の有無の検出をも行なうようにし、
濃度検出手段からの出力信号により汚泥処理計測
データの演算を行なう演算手段と、この演算手段
からの出力信号を入力するコントローラとによ
り、ポンプ等の汚泥引抜き手段を自動的に駆動で
きるようにしたものである。
The present invention was made in order to eliminate the drawbacks of the conventional ones as described above.
The concentration detection means on the stand allows MLSS to be detected during the aeration process.
In addition to measuring sludge, the presence or absence of sludge at the set sludge interface height during the sedimentation process is also detected.
A device that can automatically drive sludge extraction means such as a pump by a calculation means that calculates sludge treatment measurement data based on the output signal from the concentration detection means and a controller that inputs the output signal from this calculation means. It is.

以下、本発明の一実施例を図について説明す
る。第1図において、1は回分式反応槽で、汚水
流水口2より汚水が取り込まれ、ばつ気工程、沈
殿工程後の排出工程で、上澄水は上澄水排出口3
より槽外に排水される。4は下端に濃度測定部5
を装備した濃度検出手段としての濃度計で、この
濃度計4によつて計測されたデータは信号線6を
介してマイクロコンピユーター等を内蔵した演算
手段としての演算装置7に伝送される。そして、
その演算結果は適宜、表示器8又はプリンタ9に
伝送されて然るべき出力表示を行う。また、10
は警報装置、11はコントローラでそのコントロ
ーラ11の出力は汚泥引抜き手段としてのポンプ
12を駆動し、沈殿汚泥13を回分式反応槽1の
外部に排出する。また、上記回分式反応槽1内に
最高水位高さをH2、最低水位高さをH1、設定汚
泥界面高さをH0(汚泥が上澄液と共に排出しない
ように、最低水位高さより30センチから100セン
チ程度で設定することがある。)として夫々設定
されており、濃度測定部5はH0の高さに取付け
られている。また、第2図は第1図の回分式活性
汚泥制御装置の各工程別測定動作を示したもの
で、S1ないしS4は工程毎の順序動作を、また
M1ないしM3は各工程毎に前記濃度計4によつ
て計測される測定項目である。
Hereinafter, one embodiment of the present invention will be described with reference to the drawings. In Fig. 1, 1 is a batch type reaction tank, in which sewage is taken in through the sewage flow outlet 2, and in the discharge process after the aeration process and the precipitation process, the supernatant water is discharged through the supernatant water outlet 3.
More water is drained out of the tank. 4 has a concentration measuring section 5 at the bottom end.
The data measured by the densitometer 4 is transmitted via a signal line 6 to an arithmetic unit 7 as an arithmetic means having a built-in microcomputer or the like. and,
The calculation results are appropriately transmitted to the display 8 or printer 9 for appropriate output display. Also, 10
11 is an alarm device, and 11 is a controller. The output of the controller 11 drives a pump 12 as a sludge drawing means, and the precipitated sludge 13 is discharged to the outside of the batch reaction tank 1. In addition, the maximum water level height in the batch type reaction tank 1 is H 2 , the minimum water level height is H 1 , and the set sludge interface height is H 0 (in order to prevent sludge from being discharged together with the supernatant liquid, the height is higher than the minimum water level height). ), and the concentration measuring section 5 is installed at a height of H 0 . Moreover, FIG. 2 shows the measurement operation for each process of the batch type activated sludge control device shown in FIG. This is a measurement item measured by a total of 4.

次に本発明の動作を第1図及び第2図を参照し
て以下に説明する。まず、回分式反応槽1内の汚
泥は所定位置の高さH0付近にあり、濃度計4の
濃度測定部5を浸漬することにより以下の動作を
行う。
Next, the operation of the present invention will be explained below with reference to FIGS. 1 and 2. First, the sludge in the batch reaction tank 1 is at a predetermined position near the height H0 , and the concentration measuring part 5 of the densitometer 4 is immersed to perform the following operation.

(1) 最低水位高さH1において、汚水を流水しな
がらばつ気工程S1が開始されるとそれから所
定の設定時間t1経過後に回分式反応槽1内の混
合液について活性汚泥浮遊物濃度MLSSの測定
M1が行われる。
(1) At the minimum water level height H1 , when the aeration step S1 is started while flowing wastewater, after a predetermined set time t1 has elapsed, the activated sludge suspended solids concentration MLSS is determined for the mixed liquid in the batch reaction tank 1. Measurement M1 is performed.

(2) 回分式反応槽1内では時間の経過と共に水位
が上昇し、ばつ気工程S2に入るが、その水位
の変動に応じて前記MLSSの計測値も変動す
る。よつて、ばつ気開始後の設定時間t1を前記
MLSSの混合が充分に成される最小の時間に設
定することにより、MLSS測定時の水位を最定
水位高さH1に略等しく設定することができる
ので、測定時の水位を測定してMLSSを換算す
る必要がない。
(2) The water level in the batch reaction tank 1 rises with the passage of time and enters the aeration step S2, but the measured value of the MLSS also changes in accordance with the change in the water level. Therefore, the set time t 1 after the start of exposure is
By setting the minimum time for sufficient MLSS mixing, the water level at the time of MLSS measurement can be set approximately equal to the maximum water level height H1 , so the water level at the time of measurement can be measured and the MLSS There is no need to convert.

(3) 次に沈殿工程S3において汚泥の沈殿が充分
進行し、沈殿がほぼ終了した段階で設定汚泥界
面高さでの汚泥の有無と濃度検出M2のための
活性汚泥濃度測定を、濃度計4を用いて行う。
すなわち、設定汚泥界面高さでの活性汚泥濃度
検出M2の測定結果が所定設定値以上の濃度
(例えば、1000mg/以上)である場合は、汚
泥界面は濃度測定部5より上位にあることを意
味するので、濃度計4の出力信号は信号線6を
介して演算装置7に伝達される。即ち、この演
算装置7は、上記濃度計からの入力信号による
実際の汚泥濃度測定値と、予め設定された汚泥
濃度設定値とを比較演算し、該演算の結果、上
記汚泥濃度測定値が上記汚泥濃度設定値を越え
た時、コントローラ11に汚泥引抜き指令信号
を出力する。これにより、上記コントローラ1
1はポンプ(汚泥引抜き手段)12に駆動指令
信号を出力し、該信号で上記ポンプ12が駆動
されることにより、回分式反応槽1内の沈殿汚
泥が引抜かれる。
(3) Next, in the sedimentation step S3, when the sedimentation of sludge has sufficiently progressed and the sedimentation is almost completed, the presence or absence of sludge at the set sludge interface height and the activated sludge concentration measurement for concentration detection M2 are carried out using the densitometer 4. This is done using
In other words, if the measurement result of the activated sludge concentration detection M2 at the set sludge interface height is a concentration higher than a predetermined set value (for example, 1000 mg/or higher), it means that the sludge interface is higher than the concentration measuring section 5. Therefore, the output signal of the densitometer 4 is transmitted to the arithmetic unit 7 via the signal line 6. That is, this calculation device 7 compares and calculates the actual sludge concentration measurement value based on the input signal from the densitometer and the preset sludge concentration value, and as a result of the calculation, the sludge concentration measurement value is When the sludge concentration exceeds the set value, a sludge extraction command signal is output to the controller 11. As a result, the controller 1
1 outputs a drive command signal to a pump (sludge drawing means) 12, and the pump 12 is driven by the signal, whereby the precipitated sludge in the batch reaction tank 1 is drawn out.

また、設定汚泥界面高さでの活性汚泥濃度検
出M2の計測値の濃度が所定設定値以下である
場合は、汚泥界面は濃度計測定部5より下にあ
ることを意味することになるので、汚泥の引抜
きは行われない。
In addition, if the concentration of the measured value of activated sludge concentration detection M2 at the set sludge interface height is below the predetermined set value, it means that the sludge interface is below the concentration meter measurement part 5. No sludge extraction will be carried out.

そして、前記の汚泥引抜きにおいてはコント
ローラ11からの出力信号が予め設定されたタ
イマによつて運転されるようになつているの
で、設定時間が経過するとポンプ12は自動停
止し、沈殿汚泥13の排出が停止される。
In the above-mentioned sludge drawing, the output signal from the controller 11 is operated by a preset timer, so when the set time elapses, the pump 12 is automatically stopped and the settled sludge 13 is discharged. will be stopped.

(4) 次に、汚泥引抜きが終了し、排出工程S4に
入ると汚泥界面は濃度測定部5より下位になる
が、必要に応じ所定位置の高さH0における汚
泥の有無の確認を実施すると共に、上澄液の
SS濃度測定M3を実施、記録する。
(4) Next, when the sludge extraction is completed and the discharge step S4 begins, the sludge interface will be lower than the concentration measurement part 5, but if necessary, the presence or absence of sludge at the height H0 of the predetermined position will be confirmed. together with the supernatant
Perform and record SS concentration measurement M3.

以上のような一連の制御動作を行うことによつ
て汚泥界面は常に所定位置の高さH0付近に保た
れることになり、前記MLSSの測定結果より汚泥
容量指標SVIが演算装置7により直ちに演算され
る。演算式は(1)式に示した。また、汚泥引抜き用
のポンプ12の稼動時間を加味して活性汚泥細胞
平均滞留時間SRTも(6)ないし(9)式の演算によつ
て求められ、その夫々の演算結果は表示器8又は
プリンタ9によつて出力表示される。
By performing the above series of control operations, the sludge interface is always maintained at a predetermined position near the height H0 , and the sludge volume index SVI is immediately calculated by the calculation device 7 from the measurement results of the MLSS. Calculated. The calculation formula is shown in equation (1). In addition, the activated sludge cell average residence time SRT is calculated by equations (6) to (9), taking into account the operating time of the pump 12 for sludge extraction, and the respective calculation results are displayed on the display 8 or on the printer. The output is displayed by 9.

以上のように、この発明によれば、回分式反応
槽内の所定位置に濃度検出手段の濃度測定部を定
置的に配置するだけでよく、その一つの濃度検出
手段によつて、単一の回分式反応槽内におけるば
つ気工程時の活性汚泥濃度と、沈殿工程終了時に
おける設定汚泥界面高さでの沈殿汚泥の有無とを
検出することができる。
As described above, according to the present invention, it is only necessary to stationarily arrange the concentration measuring section of the concentration detecting means at a predetermined position in the batch reaction tank, and one concentration detecting means can be used to detect a single concentration. The activated sludge concentration during the aeration process in the batch reaction tank and the presence or absence of settled sludge at the set sludge interface height at the end of the settling process can be detected.

即ち、上記濃度検出手段は、それ本来の濃度検
出検出機能をばつ気工程時に発揮し、且つ沈殿工
程終了時に設定汚泥界面高さでの沈殿汚泥の有無
とを検出するが、この沈殿汚泥の有無検出機能
は、上記濃度検出手段の濃度測定部の配置レベル
と、この配置レベルで活性汚泥濃度を検出する上
記濃度検出手段と、この濃度検出手段から濃度検
出信号を入力して実際の汚泥濃度検出値を予め設
定された汚泥濃度設定値と比較演算する演算手段
との組み合わせによつて得られる。
That is, the concentration detection means performs its original concentration detection function during the aeration process, and also detects the presence or absence of settled sludge at the set sludge interface height at the end of the settling process. The detection function is based on the arrangement level of the concentration measuring section of the concentration detection means, the concentration detection means that detects the activated sludge concentration at this arrangement level, and the actual sludge concentration detection by inputting the concentration detection signal from this concentration detection means. It is obtained by a combination of calculation means that compares and calculates the value with a preset sludge concentration setting value.

さらに換言詳述すると、この発明では、上記濃
度測定部の配置レベルが設定汚泥界面高さとな
り、この設定汚泥界面高さにおける汚泥濃度を上
記濃度検出手段が検出し、且つ演算手段がその濃
度検出手段からの入力信号による汚泥濃度検出値
を汚泥濃度設定値と比較演算して、汚泥濃度検出
値が汚泥濃度設定値を越えると、回分式反応槽内
における実際の沈殿汚泥量が上記設定汚泥界面高
さを越えたことになり、従つて、汚泥濃度検出値
が汚泥濃度設定値を越えれば、上記設定汚泥界面
高さでの汚泥が“有”と判断され、汚泥濃度検出
値が汚泥濃度設定値に達しなければ、上記設定汚
泥界面高さでの汚泥が“無”と判断される。
In other words, in this invention, the arrangement level of the concentration measuring section is a set sludge interface height, the concentration detection means detects the sludge concentration at this set sludge interface height, and the calculation means detects the concentration. The sludge concentration detected value based on the input signal from the means is compared with the sludge concentration set value, and when the sludge concentration detected value exceeds the sludge concentration set value, the actual amount of settled sludge in the batch type reaction tank is equal to the above set sludge interface. Therefore, if the detected sludge concentration value exceeds the set sludge concentration value, it is determined that sludge exists at the set sludge interface height, and the detected sludge concentration value exceeds the set sludge concentration value. If the value is not reached, it is determined that there is no sludge at the set sludge interface height.

このようにして、上記濃度検出手段は、それ1
つでばつ気工程時における通常の活性汚泥濃度検
出機能と、沈殿工程終了時における設定汚泥界面
高さでの汚泥の有無検出機能とを発揮する。
In this way, the concentration detection means 1
It performs the normal activated sludge concentration detection function during the aeration process and the presence/absence detection function of sludge at the set sludge interface height at the end of the sedimentation process.

そして、上記演算手段は、上記“有”の時、汚
泥引抜き指令信号をコントローラに出力し、この
コントローラが汚泥引抜き手段を駆動することに
より、回分式反応槽内の余剰汚泥が自動的に引抜
かれ、これによつて、回分式反応槽内の沈殿汚泥
量を上記設定汚泥界面高さ付近に安定維持させる
ことができる。
The calculation means outputs a sludge extraction command signal to the controller when "Yes", and the controller drives the sludge extraction means, whereby excess sludge in the batch reaction tank is automatically extracted. As a result, the amount of precipitated sludge in the batch reaction tank can be stably maintained near the above-mentioned set sludge interface height.

従つて、この発明によれば、頗る簡単で経済的
にも有利な装置構成により、回分式反応槽内の汚
泥管理、BOD−SS負荷等の管理を効率的に行う
ことができ、さらに、上澄液のSS濃度、SVI、
SRTなどについて充分正確な測定を行なつた状
態で汚泥処理を行なうことができるという効果が
ある。
Therefore, according to the present invention, it is possible to efficiently manage the sludge in the batch reaction tank, the BOD-SS load, etc. with a very simple and economically advantageous device configuration. Clear liquid SS concentration, SVI,
This has the advantage that sludge treatment can be carried out with sufficiently accurate measurements of SRT and the like.

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

第1図は本発明の一実施例を示す回分式汚泥処
理制御装置の概略図、第2図は第1図の動作を示
す各工程別測定動作図である。 1……回分式反応槽、4……濃度検出手段(濃
度計)、5……濃度測定部、7……演算手段(演
算装置)、11……コントローラ、12……汚泥
引抜き手段(ポンプ)、H0……所定位置。
FIG. 1 is a schematic diagram of a batch-type sludge treatment control device showing one embodiment of the present invention, and FIG. 2 is a measurement operation diagram for each process showing the operation of FIG. 1. DESCRIPTION OF SYMBOLS 1... Batch type reaction tank, 4... Concentration detection means (concentration meter), 5... Concentration measuring section, 7... Calculation means (computation device), 11... Controller, 12... Sludge drawing means (pump) , H 0 ...predetermined position.

Claims (1)

【特許請求の範囲】 1 流入汚水を受け入れ、ばつ気工程、沈殿工
程、汚泥引抜き工程及び排出工程が行われる回分
式反応槽と、この回分式反応槽に取付けられ、前
記汚泥の引抜きを行う汚泥引抜き手段とを備えた
バツチ式活性汚泥処理装置において、前記回分式
反応槽内の所定位置を設定汚泥界面高さとしてそ
の高さ位置に配置された濃度測定部を有し、前記
ばつ気工程時には活性汚泥濃度を測定し、且つ前
記沈殿工程終了時には上記設定汚泥界面高さでの
汚泥の有無を検出する濃度検出手段と、この濃度
検出手段から濃度検出信号を入力し、該濃度検出
値を予め設定された汚泥濃度設定値と比較演算す
る演算手段と、その演算により実際の濃度検出値
が上記汚泥濃度設定値を越えた時、上記演算手段
からの入力信号に基づく汚泥引抜き指令信号を上
記汚泥引抜き手段に出力して該汚泥引抜き手段を
駆動するコントローラとを備えたバツチ式活性汚
泥処理装置。 2 前記濃度検出手段による活性汚泥濃度測定値
と汚泥引抜き結果による汚泥容量指標及び活性汚
泥細胞平均滞留時間を、演算手段により自動的に
算出、表示又は記録することを特徴とする特許請
求の範囲第1項記載のバツチ式活性汚泥処理装
置。
[Scope of Claims] 1. A batch-type reaction tank that receives inflow sewage and undergoes an aeration process, a precipitation process, a sludge extraction process, and a discharge process, and a sludge that is attached to this batch-type reaction tank and performs the extraction of the sludge. In the batch type activated sludge treatment apparatus, the batch type activated sludge treatment apparatus is provided with a predetermined position in the batch type reaction tank as a set sludge interface height, and has a concentration measuring unit disposed at a height position thereof, and during the aeration process, a concentration detection means for measuring the activated sludge concentration and detecting the presence or absence of sludge at the set sludge interface height at the end of the settling step; a calculation means that performs a comparison calculation with a set sludge concentration value, and when the actual concentration detected value exceeds the sludge concentration setting value by the calculation, a sludge extraction command signal based on an input signal from the calculation means is sent to the sludge A batch type activated sludge treatment apparatus comprising a controller that outputs to a drawing means and drives the sludge drawing means. 2 The activated sludge concentration measured by the concentration detection means, the sludge volume index based on the sludge extraction result, and the activated sludge cell average residence time are automatically calculated, displayed, or recorded by the calculation means. Batch-type activated sludge treatment equipment according to item 1.
JP58122232A 1983-07-04 1983-07-04 Batch treating apparatus for activated sludge Granted JPS6014993A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58122232A JPS6014993A (en) 1983-07-04 1983-07-04 Batch treating apparatus for activated sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58122232A JPS6014993A (en) 1983-07-04 1983-07-04 Batch treating apparatus for activated sludge

Publications (2)

Publication Number Publication Date
JPS6014993A JPS6014993A (en) 1985-01-25
JPS64118B2 true JPS64118B2 (en) 1989-01-05

Family

ID=14830837

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58122232A Granted JPS6014993A (en) 1983-07-04 1983-07-04 Batch treating apparatus for activated sludge

Country Status (1)

Country Link
JP (1) JPS6014993A (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0790231B2 (en) * 1987-03-18 1995-10-04 日立機電工業株式会社 Control method for batch type waste water treatment equipment
KR20020083978A (en) * 2002-09-28 2002-11-04 주식회사 퍼텍코리아 CPA(Continuity inflow Periodic Activated-sludge System)PROCESS
JP7601550B2 (en) * 2019-09-06 2024-12-17 オルガノ株式会社 Water treatment method and water treatment device

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS587326B2 (en) * 1975-04-24 1983-02-09 株式会社安川電機 How to manage sludge volume at sewage treatment plants
JPS51145169A (en) * 1975-06-09 1976-12-13 Hitachi Ltd Active mud boundary detector for settling pond
JPS5579091A (en) * 1978-12-07 1980-06-14 Mitsubishi Electric Corp Drawing controller for excessive sludge

Also Published As

Publication number Publication date
JPS6014993A (en) 1985-01-25

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