JPS60179195A - Method for controlling do in aeration vessel to fixed value by feedforward control - Google Patents

Method for controlling do in aeration vessel to fixed value by feedforward control

Info

Publication number
JPS60179195A
JPS60179195A JP59033722A JP3372284A JPS60179195A JP S60179195 A JPS60179195 A JP S60179195A JP 59033722 A JP59033722 A JP 59033722A JP 3372284 A JP3372284 A JP 3372284A JP S60179195 A JPS60179195 A JP S60179195A
Authority
JP
Japan
Prior art keywords
aeration
value
treated
amt
raw water
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.)
Pending
Application number
JP59033722A
Other languages
Japanese (ja)
Inventor
Nobuo Yamamoto
伸夫 山本
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.)
Toyota Motor Corp
Original Assignee
Toyota Motor Corp
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 Toyota Motor Corp filed Critical Toyota Motor Corp
Priority to JP59033722A priority Critical patent/JPS60179195A/en
Publication of JPS60179195A publication Critical patent/JPS60179195A/en
Pending 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)

Abstract

PURPOSE:To control precisely the DO value in an aeration vessel to a fixed value by agitating a fixed amt. of original water to be treated which is supplied into the aeration vessel and a fixed amt. of sludge taken from a settling vessel for specified hours, and measuring oxygen consumption during said hours. CONSTITUTION:The flow rate of the original water 2 to be treated which is charged into an aeration vessel 1 is measured by a flowmeter 22, and the detected value is inputted to a controller 21. The amt. of aeration air is obtained by the controller 21 on the basis of said inputted value and oxygen consumption. The obtained amt. of aeration air is inputted to an inverter 23 as an electric signal from the controller 21. The number of revolutions of a blower 7 is controlled by the output signal of the inverter 23 to obtain said amt. of air to be needed for aeration. Namely, the number of revolutions of the blower 7 is controlled by feedforward control so that the amt. of aeration air may be regulated in accordance with the BOD load of the original water 2 to be treated which is being supplied into the aeration vessel 1.

Description

【発明の詳細な説明】 産業上の利用分野 この発明は、排水を活性汚泥処理法によって処理するに
あたり、曝気槽内のDO値(溶存酸素量)を制御する方
法に関するものであり、排水処理あるいは公害防止の分
野で利用することができる。
DETAILED DESCRIPTION OF THE INVENTION Field of Industrial Application This invention relates to a method for controlling the DO value (dissolved oxygen amount) in an aeration tank when treating wastewater by an activated sludge treatment method. It can be used in the field of pollution prevention.

従来技術 生活排水等の有機排水の処理方法として活性汚泥法が知
られており、この方法は処理すべき排水に空気を送り込
んで曝気することにより、汚濁物質を活性汚泥によって
酸化分解し、しかる後活性汚泥を沈殿分離して清浄な上
澄みを放流する方法である。したがってこの方法では、
処理すべき排水のBODif1度に応じたくすなわちB
OD負荷に応じた)足の風聞で曝気を行なう必要があり
、従来、浄化能力の低下や不必要なエネルギーの消費を
防止するために、曝気槽でのDo値(溶存酸素量)が予
め定めた一定値となるよう制御している。
Conventional technology The activated sludge method is known as a method for treating organic wastewater such as domestic wastewater, and this method involves aerating the wastewater to be treated by pumping air into the wastewater to oxidize and decompose pollutants using activated sludge. This is a method in which activated sludge is separated by precipitation and the clean supernatant is discharged. Therefore, in this method,
According to the BODif of the wastewater to be treated, that is, B
It is necessary to perform aeration using foot pressure (according to the OD load). Conventionally, the Do value (dissolved oxygen amount) in the aeration tank was set in advance to prevent a decrease in purification ability and unnecessary energy consumption. It is controlled to maintain a constant value.

すなわち活性汚泥処理においては、活性汚泥が排水中に
溶存する酸素を消費して汚濁物質を分解するから、溶存
酸素量が少な過ぎ、もしくは殆んど零であれば、活性汚
泥の活動が停止して排水の処理を行なえなくなり、また
逆に活性汚泥が消費する最以上に溶存酸素量を高めて場
合には、曝気に要した動力を不必要に消費したことにな
る。したがって効率の良い処理を行なうには、Do値を
予め定めた一定値に、なるよう曝気風量を制御すること
が必要である。
In other words, in activated sludge treatment, activated sludge consumes oxygen dissolved in wastewater to decompose pollutants, so if the amount of dissolved oxygen is too low or almost zero, activated sludge activity will stop. If the amount of dissolved oxygen is increased beyond the maximum amount consumed by activated sludge, the power required for aeration will be consumed unnecessarily. Therefore, in order to perform efficient processing, it is necessary to control the aeration air volume so that the Do value is kept at a predetermined constant value.

第1図は曝気4nにおける従来のDO定値制御システム
を示す模式図であって、曝気01には、被処理原水2と
沈殿槽3からポンプ4を介して抜き取った返送汚泥5と
を供給し、かつ口気槽1内の混合液6中にブロワ−7に
よって空気を送り込むことより一気へを行なう。前記混
合液6のDoは、プロセスDo計8によって測定し、そ
の出力信号を制御器9に入力するとともに、ここで信号
処理および比較演P1等を行ない、その結果を次段のイ
ンバーター10に入力するとともに、インバーター10
の出力信号によって前記ブロワ−7の回転数の制御を行
なう。すなわちDo値が低下した場合には、ブロワ−7
の回転数を上げて曝気風口を増し、また逆にDo値が高
ぐなった場合には、ブロワ−7の回転数を下げて曝気風
9を減じる。
FIG. 1 is a schematic diagram showing a conventional DO constant value control system in aeration 4n, in which raw water to be treated 2 and return sludge 5 extracted from a settling tank 3 via a pump 4 are supplied to the aeration 01, In addition, by blowing air into the mixed liquid 6 in the mouth air tank 1 with a blower 7, it is carried out all at once. The Do of the mixed liquid 6 is measured by a process Do meter 8, and its output signal is input to a controller 9, where signal processing and comparison P1, etc. are performed, and the results are input to the next stage inverter 10. At the same time, inverter 10
The rotation speed of the blower 7 is controlled by the output signal of the blower 7. In other words, when the Do value decreases, the blower 7
The number of rotations of the blower 7 is increased to increase the number of aeration air ports, and conversely, when the Do value becomes high, the number of rotations of the blower 7 is lowered to reduce the amount of aeration air 9.

このように従来では、曝気槽1でのDo定値制御をフィ
ードバック制御によって行なっており、被処理原水2の
BOD負荷の増減に応じてDo値が変動するから、結局
曝気用0をBOD負荷に応じて増減することができる。
Conventionally, Do constant value control in the aeration tank 1 is performed by feedback control, and the Do value fluctuates according to increases and decreases in the BOD load of the raw water to be treated 2, so in the end, the aeration 0 is adjusted according to the BOD load. It can be increased or decreased.

しかしながら上述した従来の方法では、曝気槽1内のD
o値が上昇もしくは減少した後に曝気風量を変えること
になるから、制御時間の遅れが大きく、そのため被処理
原水2のBOD負荷の変動が大きい場合には、曝気41
1内のDo値と目標値とのバラつきが大ぎくなる問題か
生じる。このような場合、曝気、沈殿、放流の各過程を
連続して行なっているから、BODn度の高い排水を放
流してしまう危険がある。
However, in the conventional method described above, the D
Since the aeration air volume is changed after the o value increases or decreases, there is a large delay in control time, and therefore, if the BOD load of the raw water to be treated 2 fluctuates greatly, the aeration 41
A problem arises in which the variation between the Do value and the target value within 1 becomes large. In such a case, since the processes of aeration, precipitation, and discharge are carried out continuously, there is a risk that wastewater with a high BODn degree will be discharged.

発明の目的 この発明は上記の事情に名みてなされたもので、被処理
原水のSOD負荷の変動が大きい場合であっても、曝気
槽内のDo値を一定値に精度良く制御することのできる
Do定価制御方払を提供することを目的とするものであ
る。
Purpose of the Invention This invention was made in view of the above circumstances, and is capable of precisely controlling the Do value in the aeration tank to a constant value even when the SOD load of the raw water to be treated varies greatly. The purpose is to provide fixed price control method payment.

発明の構成 この発明は、曝気槽に供給すべき被処理原水の一定量と
沈殿槽から抜き取った活性汚泥の一定量とを、予め所定
時間撹拌混合し、かつその間の酸素消費量を測定し、1
すられた測定値に基づいて曝気槽内での曝気風qを制御
することを特徴とするものである。
Structure of the Invention The present invention involves stirring and mixing a certain amount of raw water to be treated to be supplied to an aeration tank and a certain amount of activated sludge extracted from a settling tank for a predetermined period of time, and measuring the amount of oxygen consumed during that time. 1
This system is characterized in that the aeration air q in the aeration tank is controlled based on measured values.

実 施 例 以下この発明を実施例に基づいて説明する。Example The present invention will be explained below based on examples.

先ず装置について説明すると、第2図はこの発明の方法
を実施例するだめの装置を、第1図に示す装置と同一部
材には第1図と同一符号を付して示す図であり、ここに
示す装置は、被処理原水2のBOD濃度の代用値どして
一定時間活性汚泥処理することによる酸素消費量を測定
し、その測定値に基づいて曝気爪間を制御するよう構成
されている。すなわち酸素消費量測定容器11は、ドレ
ン弁12を底部に右するとともに、その上端部からポー
タプルDO計13が挿入されており、またその測定容器
11の内部にマ′グネットスタラー14における撹拌子
15が収容されている。さらに原水ヘッドタンク16が
原水注入弁17を介して測定容器11に連通されている
とともに、汚泥ヘッドタンク18が汚泥注入弁19を介
して測定容器11に連通されている。そして原水ヘッド
タンク16【こは、原水サンプリングポンプ20によっ
て被処理原水2を汲み上げ、また汚泥ヘッドタンク18
には、前記ポンプ4によって返送汚泥の一部を圧送する
ように(3成されている。
First, to explain the apparatus, FIG. 2 is a diagram showing an apparatus for carrying out the method of the present invention, in which the same members as those in the apparatus shown in FIG. The device shown in 2 is configured to measure the amount of oxygen consumed by activated sludge treatment for a certain period of time as a substitute value for the BOD concentration of the raw water to be treated 2, and to control the aeration interval based on the measured value. . That is, the oxygen consumption measurement container 11 has a drain valve 12 at the bottom, a porta-pull DO meter 13 inserted from its upper end, and a stirrer in a magnetic stirrer 14 inside the measurement container 11. 15 are accommodated. Furthermore, the raw water head tank 16 is communicated with the measurement container 11 via the raw water injection valve 17, and the sludge head tank 18 is communicated with the measurement container 11 via the sludge injection valve 19. Then, the raw water head tank 16 [here, the raw water 2 to be treated is pumped up by the raw water sampling pump 20, and the sludge head tank 18
In this case, a part of the returned sludge is pumped by the pump 4 (3).

また前記ポータプルDo計′13が制御器21に接続さ
れる一方、被処理原水2の流0を測定する流0計22が
その測定結果を制御器21に入力するべく制御器21に
電気的に接続されている。モしてI131711器21
がインバーター23に接続され、インバーター23の出
力信号によって前記ブロワ−7の回転数を周波数変換方
式で制御するようになっている。
Further, while the portaple Do meter '13 is connected to the controller 21, the flow meter 22 which measures the flow 0 of the raw water to be treated 2 is electrically connected to the controller 21 in order to input the measurement result to the controller 21. It is connected. I131711 device 21
is connected to an inverter 23, and the number of rotations of the blower 7 is controlled by the output signal of the inverter 23 using a frequency conversion method.

つぎに上記の装置を用いたこの発明の詳細な説明すると
、原水ヘッドタンク16に被処理原水2を原水サンプリ
ングポンプ20によって汲み上げておくとともに、汚泥
ヘッドタンク]8に返送汚泥5の一部を供給しておき、
その状態で原水注入弁17および汚泥注入弁19をそれ
ぞれ所定時間開いて一定量の被処理原水2と汚泥5とを
測定容’AN 11 Tr’Z送り込む。しかる後マグ
ネツl〜スタラー14を起動して測定容器11内の混合
液を撹拌するとどもに、ポータプルDO計13によって
DO値を予め定めた一定時間測定し、測定完了後ドレン
弁12を問いC測定容器11内の混合液を排出する。そ
して測定間殆時のDO値から測定終了時のD O値を滅
0すれば、前記測定容器11内に供給した被処理原水2
および汚泥5の一定量に対する前記一定時間内での酸素
消費Rがまる。このような演鐸は、ポータプルDO計1
3の出力信号を常旧制御器21に入力することにより制
御器21にて行ない、同時に被処理原水2のヴ気槽1に
対する流量を流量計22によって測定するとともに、そ
の測定値を制御器21に入力し、かつその入力値と前記
9素消費伶とに基づいて、必要とする陽気風量を制御器
21においてめる。このようにしてめられた曝気風量は
、制御器21から電気信号としてインバーター23に入
力され、そしてブロワ−7はインバーター23の出力信
号により、前述した必要呼気l111fitとなるよう
回転数が制御される。すなわち曝気槽1に供給しつつあ
る被処理原水2のBO’D負荷に応じた陽気風量となる
ようブロワ−7の回転数をフィードフォワード制御する
ことになる。
Next, to explain in detail the present invention using the above-mentioned device, the raw water 2 to be treated is pumped up to the raw water head tank 16 by the raw water sampling pump 20, and a part of the return sludge 5 is supplied to the sludge head tank 8. Keep it
In this state, the raw water injection valve 17 and the sludge injection valve 19 are each opened for a predetermined time to feed a certain amount of the raw water 2 and sludge 5 into the measuring volume 'AN 11 Tr'Z. After that, the magnetic stirrer 14 is started to stir the liquid mixture in the measuring container 11, and at the same time, the DO value is measured for a predetermined period of time using the portable DO meter 13, and after the measurement is completed, the drain valve 12 is checked and the C measurement is performed. The mixed liquid in the container 11 is discharged. Then, by subtracting the DO value at the end of the measurement from the DO value during most of the measurement, the raw water to be treated 2 supplied into the measurement container 11 is
And the oxygen consumption R within the certain period of time for a certain amount of sludge 5 is calculated. This kind of Entaku has a total of 1 Portaple DO.
3 is input to the conventional controller 21, and at the same time, the flow rate of the raw water to be treated 2 to the air tank 1 is measured by the flow meter 22, and the measured value is transmitted to the controller 21. The controller 21 determines the required amount of positive air air based on the input value and the above-mentioned nine element consumption values. The thus determined aeration air volume is inputted from the controller 21 to the inverter 23 as an electric signal, and the rotation speed of the blower 7 is controlled by the output signal of the inverter 23 so that the above-mentioned required exhalation l111fit is achieved. . That is, the number of revolutions of the blower 7 is controlled in a feedforward manner so that the air flow rate corresponds to the BO'D load of the raw water 2 to be treated that is being supplied to the aeration tank 1.

したがって前述した酸素消費nの測定操作をタイマー等
を用いて自動的に行ない、また酸素消費量の測定を含め
た暉気旭りのフィードフォワード制御を、一定時間毎に
行なうことにより、陽気風量を被処理原水2のBOD負
荷に適合した吊に随時設定でき、その結果匠気(11内
でのDo値を。一定値に維持することができる。なお、
曝気411内の混合液6のDo値は、プロセスDo計8
によって連続測定する。
Therefore, by automatically performing the measurement operation of the oxygen consumption n described above using a timer, etc., and by performing the feedforward control of the rising and falling air, including the measurement of the oxygen consumption amount, at regular intervals, the volume of positive airflow can be increased. The suspension can be set at any time to match the BOD load of the raw water to be treated 2, and as a result, the Do value within 11 can be maintained at a constant value.
The Do value of the mixed liquid 6 in the aeration 411 is the process Do total 8
Continuously measure by

発明の効果 以上の説明から明らかなようにこの発明の方法によれば
、曝気槽に供給すべき被処理原水の一定角と沈F2櫓か
ら抜き取った活性汚泥の一定量とを、 ゛予め定めた所
定時間撹拌混合し、かつその間の酸素消費量を測定し、
得られた測定値に基づいて曝気槽内での曝気ff1mを
制御するから、曝気槽に供給中の被処理原水のBOD負
荷に応じた陽気風量とすることができ、換言すれば制御
時間の遅れが殆んどなく、したがって被処理原水のBO
D負荷の変動が大きいj烏合であっても、DO値が目標
値となるにう粘度良く制岬することができる。またこの
弁明の方法では、制し0精麿が良好であるから、Do値
の制御目標値を理論値に近づけることができ、イの結果
曝気風りに余裕を見込む必要かなくなるため、ブロワ−
の駆動エネルギーを必要最少限に抑え、省エネルギー化
を図ることかできる。
Effects of the Invention As is clear from the above explanation, according to the method of the present invention, a certain angle of the raw water to be treated to be supplied to the aeration tank and a certain amount of activated sludge extracted from the settling F2 tower are determined in advance. Stir and mix for a predetermined period of time, and measure oxygen consumption during that time.
Since the aeration ff1m in the aeration tank is controlled based on the obtained measurement value, the air volume can be set according to the BOD load of the raw water to be treated that is being supplied to the aeration tank.In other words, the control time is delayed. There is almost no BO of raw water to be treated.
Even in cases where the D load fluctuates greatly, the viscosity can be controlled with good viscosity so that the DO value becomes the target value. In addition, in this defense method, since the control target value of 0 is good, the control target value of the Do value can be brought close to the theoretical value, and as a result of (a), there is no need to allow for a margin in the aeration air, so the blower
It is possible to reduce the driving energy to the minimum necessary and save energy.

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

第1図は従来のDo定値制御システムを概略的に示す模
式日、第2図はこの発明の方法を実加するための装置を
概略的に示す模式図である。 1・・・曝気槽、 2・・・被処理原水、 3・・・沈
y1槽、5・・・活性汚泥、 7・・・ブロワ−111
・・・酸素消i i g、i定容器、 13・・・ポー
タプルDO計、 14・・・マグネットスタラー、 1
6・・・原水ヘッドタンク、 17・・・原水注入弁、
 18・−・汚泥ヘッドタンク、 19・・・汚泥注入
弁、 21・・・制御器、22・・・流量計、23・・
・インバーター。 出願人 トヨタ自動市株式会社 代理人 弁理士 豊 1)武 久 (ほか1名) 臨2図
FIG. 1 is a schematic diagram schematically showing a conventional Do constant value control system, and FIG. 2 is a schematic diagram schematically showing an apparatus for implementing the method of the present invention. 1... Aeration tank, 2... Raw water to be treated, 3... Sediment Y1 tank, 5... Activated sludge, 7... Blower-111
...Oxygen quencher, i-static container, 13... Portable DO meter, 14... Magnetic stirrer, 1
6... Raw water head tank, 17... Raw water injection valve,
18... Sludge head tank, 19... Sludge injection valve, 21... Controller, 22... Flow meter, 23...
·inverter. Applicant Toyota Motor City Co., Ltd. Agent Patent Attorney Yutaka 1) Hisashi Take (and 1 other person) Rin 2

Claims (1)

【特許請求の範囲】[Claims] 被処理原水を曝気槽内で活性汚泥処理した後、活性汚泥
を沈殿槽にて沈殿分離するにあたり、曝気槽に供給すべ
き被処理原水の一定量と沈殿槽から抜き取った活性汚泥
の一定量とを、予め定めた所定時間撹拌混合するととも
に、その間の酸素消費量を測定し、得られた測定値に基
づいて曝気槽内での暉気風旦を制御することを特徴とす
るフィードフォワード制御による曝気槽内Do定値制御
方法。
After the raw water to be treated is subjected to activated sludge treatment in the aeration tank, the activated sludge is separated by sedimentation in the settling tank. A certain amount of the raw water to be treated is to be supplied to the aeration tank, a certain amount of activated sludge extracted from the settling tank, and Aeration by feedforward control characterized by stirring and mixing for a predetermined period of time, measuring the amount of oxygen consumed during that time, and controlling the aeration in the aeration tank based on the measured value. In-tank Do constant value control method.
JP59033722A 1984-02-24 1984-02-24 Method for controlling do in aeration vessel to fixed value by feedforward control Pending JPS60179195A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59033722A JPS60179195A (en) 1984-02-24 1984-02-24 Method for controlling do in aeration vessel to fixed value by feedforward control

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59033722A JPS60179195A (en) 1984-02-24 1984-02-24 Method for controlling do in aeration vessel to fixed value by feedforward control

Publications (1)

Publication Number Publication Date
JPS60179195A true JPS60179195A (en) 1985-09-13

Family

ID=12394287

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59033722A Pending JPS60179195A (en) 1984-02-24 1984-02-24 Method for controlling do in aeration vessel to fixed value by feedforward control

Country Status (1)

Country Link
JP (1) JPS60179195A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7879245B2 (en) * 2006-11-01 2011-02-01 Markham Gary W Process for treating industrial effluent water with activtated media
CN107024883A (en) * 2017-05-03 2017-08-08 中国神华能源股份有限公司 Fired power generating unit load adjusting method and device and storage medium, processor

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7879245B2 (en) * 2006-11-01 2011-02-01 Markham Gary W Process for treating industrial effluent water with activtated media
CN107024883A (en) * 2017-05-03 2017-08-08 中国神华能源股份有限公司 Fired power generating unit load adjusting method and device and storage medium, processor

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