JPH0256960B2 - - Google Patents
Info
- Publication number
- JPH0256960B2 JPH0256960B2 JP57105131A JP10513182A JPH0256960B2 JP H0256960 B2 JPH0256960 B2 JP H0256960B2 JP 57105131 A JP57105131 A JP 57105131A JP 10513182 A JP10513182 A JP 10513182A JP H0256960 B2 JPH0256960 B2 JP H0256960B2
- Authority
- JP
- Japan
- Prior art keywords
- flow rate
- sludge
- aeration tank
- water
- treated
- 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 - Lifetime
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Activated Sludge Processes (AREA)
Description
【発明の詳細な説明】
〔発明の目的〕
(産業上の利用分野)
本発明は曝気槽および沈殿池が系列化されてな
る複数の汚水処理系列を有する汚水処理設備に係
り、特に、曝気槽に流入する被処理水および沈殿
池より曝気槽に返送される汚泥を分配制御する曝
気槽流量分配制御方法に関する。[Detailed Description of the Invention] [Object of the Invention] (Industrial Application Field) The present invention relates to a sewage treatment facility having a plurality of sewage treatment lines in which aeration tanks and sedimentation tanks are arranged in series. The present invention relates to an aeration tank flow rate distribution control method for controlling the distribution of treated water flowing into a sedimentation tank and sludge returned from a settling tank to an aeration tank.
(従来の技術)
活性汚泥法による下水処理とは、好気性または
通性の細菌を主体とする多種多様な微生物の集合
体である活性汚泥(以下、単に汚泥という)と下
水(一次処理水をも含めて以下に被処理水と言
う)とを混合接触させ、下水中の汚泥有機物やそ
の他の懸濁性物質を除去する生物化学的下水処理
法の一種である。この活性汚泥法は生物の生活々
動を利用するものであるため、その処理効率は汚
泥が健全な状態に維持されている場合にのみ高
く、かつ、安定に保つことができる。(Prior art) Sewage treatment using the activated sludge method consists of activated sludge (hereinafter simply referred to as sludge), which is a collection of a wide variety of microorganisms mainly consisting of aerobic or facultative bacteria, and sewage (primary treated water). This is a type of biochemical sewage treatment method that removes sludge organic matter and other suspended substances from sewage by mixing and contacting sewage water (hereinafter referred to as treated water). Since this activated sludge method utilizes the living activities of living organisms, its treatment efficiency can be kept high and stable only if the sludge is maintained in a healthy state.
汚泥を健全な状態に維持するには、BOD―SS
負荷およびBOD―容積負荷等を適切に保つ必要
がある。 To maintain sludge in a healthy condition, BOD-SS
Load and BOD - volumetric load, etc. must be maintained appropriately.
下水処理場では汚泥の不全を起こさないよう
に、返送汚泥量および余剰汚泥量を決めて運転制
御を行つているが、それにもかかわらず、しばし
ば汚泥の不全状態が発生している。この原因とし
ては、曝気槽および沈殿池よりなる複数の汚水処
理系列を有する下水処理場であつても、下水およ
び返送汚泥などの流量が例えばシミユレーシヨン
モデルを用いて一括して監視されるのみで、各汚
水処理系列への流量が個々に監視されていないこ
とにある。 In sewage treatment plants, the amount of returned sludge and surplus sludge is determined and the operation is controlled to prevent sludge failure, but sludge failure often occurs despite this. The reason for this is that even in sewage treatment plants that have multiple sewage treatment systems consisting of aeration tanks and settling tanks, the flow rate of sewage and return sludge is monitored all at once using a simulation model, for example. This is because the flow rate to each wastewater treatment train is not individually monitored.
すなわち、下水処理場に流入する下水の流量は
時間的に大きく異り、これに伴つて返送汚泥の流
量も変えなければならないが、各汚水処理系列へ
の分配比が下水または汚泥の総流量の変化に対し
て大きく変化することがあり、これがために、曝
気槽における汚泥の滞留時間が長かつたり、短か
つたりし、その結果汚泥の不全状態が起こること
になる。 In other words, the flow rate of sewage flowing into a sewage treatment plant varies greatly over time, and the flow rate of returned sludge must also change accordingly, but the distribution ratio to each sewage treatment line is determined by the total flow rate of sewage or sludge. There can be large variations in response to changes, which can result in longer or shorter sludge residence times in the aeration tank, resulting in sludge failure conditions.
かかる不都合を解消する方法として、各汚水処
理系列の曝気槽に汚泥濃度計を設置し、これらの
濃度計の指示が等しくなるように各汚水処理系列
の入口に設けられた流量調整弁を制御することが
試みられている。 As a method to eliminate this inconvenience, a sludge concentration meter is installed in the aeration tank of each sewage treatment line, and the flow rate adjustment valve provided at the inlet of each sewage treatment line is controlled so that the readings of these concentration meters are equal. That is what is being attempted.
(発明が解決しようとする課題)
しかしながら、これらの汚泥濃度計には比較的
大きな機体差があること、および、汚泥が濃度計
に等しく付着していないことなどにより、各汚泥
濃度計の指示値が等しい場合でも、実際の汚泥濃
度にはかなりの違いがあつた。(Problem to be solved by the invention) However, there are relatively large differences between these sludge concentration meters, and sludge does not adhere to the concentration meters equally, so the indicated value of each sludge concentration meter Even when the values were the same, there were considerable differences in the actual sludge concentrations.
これに対して、例えば、曝気槽の汚泥濃度を一
定に運転し得たとしても、下水および返送汚泥の
分配比が予定された分配比に対して等しくずれて
いることがあり、各汚水処理系列の処理量が大き
く異なつてしまうという問題があつた。 On the other hand, for example, even if the sludge concentration in the aeration tank can be maintained constant, the distribution ratio of sewage and return sludge may deviate from the planned distribution ratio, and each sewage treatment There was a problem that the processing amount of the series varied greatly.
さらに、汚泥濃度計の検出値に対応して個々の
流量調整弁を制御することは、他の汚水処理系列
の流量をも同時に変化させることになり、この相
互干渉によつて制御不能になるという問題もあつ
た。 Furthermore, controlling individual flow rate adjustment valves in response to the detected value of the sludge concentration meter means that the flow rates of other sewage treatment systems will also change at the same time, and this mutual interference will result in loss of control. There were also problems.
この発明は上記の問題点を解決するためになさ
れたもので、機体差や測定誤差を伴う汚泥濃度計
を用いても複数の汚水処理系列に流入する被処理
水および返送汚泥を、目標とする比率(通常は均
等)で分配し得、かつ、各曝気槽の汚泥を健全な
状態に保ち得る曝気槽流量分配制御方法を提供す
ることを目的とする。 This invention was made to solve the above problems, and even if a sludge concentration meter with machine differences and measurement errors is used, it is possible to target treated water and return sludge that flow into multiple sewage treatment lines. It is an object of the present invention to provide an aeration tank flow rate distribution control method that can distribute the sludge at a ratio (usually evenly) and keep the sludge in each aeration tank in a healthy state.
(課題を解決するための手段)
本発明は、曝気槽および沈殿池が系列化され、
これらの系列にそれぞれ被処理水の分配量を調節
する第1の流量調節弁と、前記沈殿池から前記曝
気槽への返送汚泥の分配量を調節する第2の流量
調節弁とを設けると共に、前記曝気槽の被処理水
と汚泥との混合状態をシミユレートし、その結果
に基づいて前記第1および第2の流量調節弁を制
御する曝気槽流量分配制御方法において、
前記被処理水および返送汚泥の分配比に対する
汚水処理系列毎の流量係数を演算処理装置に設定
し、
前記曝気槽に流入する被処理水の総流量、この
曝気槽に流入する返送汚泥の総流量およびその濃
度をそれぞれ測定した信号と、前記各曝気槽内の
被処理水と汚泥との混合液を曝気槽外の1台の濃
度計に順次送り込んで曝気槽毎に汚泥濃度を測定
した信号とを前記演算処理装置に取込み、
前記演算処理装置は、先ずこれらの測定データ
を記憶すると共に、その記憶データに基づいて前
記曝気槽の被処理水と汚泥との混合状態を前記汚
水処理系列毎にシミユレートすることによつて、
前記各曝気槽の汚泥濃度の実測位置に対応する汚
泥濃度の時系列データを算出し、次いでこの時系
列データと実測された汚泥濃度データとを前記汚
水処理系列毎に比較して両データの差が最も小さ
くなる前記各汚水処理系列の曝気槽に流入する被
処理水および返送汚泥の流量係数を探索し、続い
て、この流量係数および前記設定による流量係数
を比較してそのずれが最も大きい汚水処理系列の
前記第1および第2の流量調節弁を調節すること
を特徴としている。
(Means for Solving the Problems) The present invention has an aeration tank and a settling tank arranged in series,
Each of these series is provided with a first flow rate control valve that adjusts the distribution amount of the water to be treated, and a second flow rate control valve that adjusts the distribution amount of the return sludge from the settling tank to the aeration tank, In the aeration tank flow rate distribution control method, the mixing state of the water to be treated and the sludge in the aeration tank is simulated, and the first and second flow rate control valves are controlled based on the result. The flow rate coefficient for each sewage treatment line with respect to the distribution ratio was set in the arithmetic processing device, and the total flow rate of the treated water flowing into the aeration tank, the total flow rate of the return sludge flowing into this aeration tank, and its concentration were measured. A signal and a signal obtained by sequentially sending a mixture of water to be treated and sludge in each of the aeration tanks to one concentration meter outside the aeration tank and measuring the sludge concentration for each aeration tank are taken into the arithmetic processing device. , the arithmetic processing device first stores these measurement data and simulates the mixing state of the water to be treated and sludge in the aeration tank for each of the sewage treatment lines based on the stored data,
The time series data of the sludge concentration corresponding to the actual measurement position of the sludge concentration in each aeration tank is calculated, and then this time series data and the actually measured sludge concentration data are compared for each of the sewage treatment series to determine the difference between both data. Find the flow rate coefficient of the treated water and return sludge flowing into the aeration tank of each sewage treatment system that has the smallest value, and then compare this flow rate coefficient with the flow rate coefficient based on the settings above to find the sewage water with the largest deviation. The method is characterized in that the first and second flow control valves of the processing series are adjusted.
(作 用)
この発明においては、各曝気槽内の被処理水と
汚泥との混合液を曝気槽外の1台の濃度計に順次
送り込んで曝気槽毎に汚泥濃度を測定しており、
しかも、混合状態のシミユレートにより誤差の補
正も可能であるため、機体差や測定誤差を伴う汚
泥濃度計を用いても複数の汚水処理系列に流入す
る被処理水および返送汚泥を、目標とする比率で
分配することができる。(Function) In this invention, the mixed liquid of treated water and sludge in each aeration tank is sequentially sent to one concentration meter outside the aeration tank, and the sludge concentration is measured for each aeration tank.
Moreover, it is possible to correct errors by simulating the mixing state, so even if a sludge concentration meter with machine differences and measurement errors is used, the target ratio of treated water and returned sludge flowing into multiple sewage treatment lines can be adjusted. can be distributed.
また、演算された汚泥濃度の時系列データと、
実測された汚泥濃度データとを比較して両データ
の差が最も小さくなる前記各汚水処理系列の曝気
槽に流入する被処理水および返送汚泥の流量係数
を探索し、続いて、この流量係数および前記設定
による流量係数を比較してそのずれが最も大きい
汚水処理系列の流量調節弁を調節するので、従来
の方法で問題となつた制御不能に陥るという問題
も同時に解消され、各曝気槽の汚泥を健全な状態
に保つことができる。 In addition, time series data of calculated sludge concentration,
The flow rate coefficient of the treated water and return sludge flowing into the aeration tank of each sewage treatment line is searched for by comparing the actually measured sludge concentration data and the difference between both data is the smallest, and then this flow rate coefficient and Since the flow rate coefficients according to the above settings are compared and the flow rate control valve of the sewage treatment line with the largest deviation is adjusted, the problem of loss of control, which was a problem with the conventional method, is also solved, and the sludge in each aeration tank is can be kept in a healthy state.
(実施例)
以下、図面を参照して本発明の一実施例につい
て説明する。(Example) Hereinafter, an example of the present invention will be described with reference to the drawings.
第1図は本発明に係る曝気槽流量分配制御方法
を実施する流量分配制御装置の構成を、汚水処理
系列と併せて示したブロツク図である。ここで汚
水処理系統は被処理水と返送汚泥とを混合する3
台の曝気槽11,12,13と、これらの曝気槽
の混合液を導入して汚泥を沈降分離させる沈殿池
21,22,23とでなり、曝気槽11および沈
殿池21が第1の汚水処理系統を、曝気槽12お
よび沈殿池22が第2の汚水処理系統を、曝気槽
13および沈殿池23が第3の汚水処理系統をそ
れぞれ形成している。 FIG. 1 is a block diagram showing the configuration of a flow rate distribution control device for implementing the aeration tank flow rate distribution control method according to the present invention, together with a sewage treatment system. Here, the sewage treatment system mixes the water to be treated and the returned sludge.
It consists of three aeration tanks 11, 12, and 13, and settling tanks 21, 22, and 23 that introduce the mixed liquid of these aeration tanks and sediment and separate the sludge. The aeration tank 12 and settling tank 22 form a second sewage treatment system, and the aeration tank 13 and settling tank 23 form a third sewage treatment system.
また、曝気槽11,12,13の入口、すなわ
ち、各汚水処理系統の入口には管路1を通して返
送される返送汚泥の分配量を調節する流量調節弁
41,42,43とが設けられており、さらに、
管路1には被処理水の総流量を測定する流量計3
が、管路2には返送汚泥の総流量を測定する流量
計4およびこの返送汚泥の濃度を測定する汚泥濃
度計5がそれぞれ設けられている。 Further, flow rate control valves 41, 42, 43 are provided at the inlets of the aeration tanks 11, 12, 13, that is, the inlets of each sewage treatment system, for adjusting the distribution amount of the return sludge returned through the pipe 1. In addition,
A flow meter 3 is installed in the pipe line 1 to measure the total flow rate of the water to be treated.
However, the pipe line 2 is provided with a flow meter 4 for measuring the total flow rate of the returned sludge, and a sludge concentration meter 5 for measuring the concentration of the returned sludge.
また、曝気槽11,12,13には、被処理水
の流下方向より見て曝気槽長の略1/3の位置に、
混合液を汲み上げるポンプ51,52,53がそ
れぞれ設けられている。これらのポンプ51,5
2,53は演算処理装置100の制御信号Ya,
Yb,Ycによつて順次駆動され、曝気槽の外部に
設けた1台の汚泥濃度計6に混合液を供給する。
そして、この汚泥濃度計6の汚泥濃度信号Xaが
演算処理装置100に取込まれる。 In addition, in the aeration tanks 11, 12, and 13, there are
Pumps 51, 52, and 53 for pumping up the mixed liquid are provided, respectively. These pumps 51,5
2, 53 are control signals Y a of the arithmetic processing unit 100,
It is sequentially driven by Y b and Y c and supplies the mixed liquid to one sludge concentration meter 6 installed outside the aeration tank.
Then, the sludge concentration signal X a from the sludge concentration meter 6 is taken into the arithmetic processing device 100 .
さらに、流量計3,4によつて測定された流量
信号QS,QRおよび汚泥濃度計5によつて測定さ
れた汚泥濃度計信号XCも演算処理装置100に
取込まれる。 Furthermore, the flow rate signals Q S and Q R measured by the flow meters 3 and 4 and the sludge concentration meter signal X C measured by the sludge concentration meter 5 are also taken into the arithmetic processing device 100 .
一方、演算処理装置100の出力信号PS,PR
が流量調節弁制御装置110および120に加え
られ、このうち、流量調節弁制御装置110が流
量調節弁31,32,33の開度を制御し、流量
調節弁制御装置120が流量調節弁41,42,
43の開度を制御するようになつている。 On the other hand, the output signals P S and P R of the arithmetic processing unit 100
are added to the flow rate control valve control devices 110 and 120, of which the flow rate control valve control device 110 controls the opening degrees of the flow rate control valves 31, 32, and 33, and the flow rate control valve control device 120 controls the opening degrees of the flow rate control valves 41, 33, and 42,
The opening degree of 43 is controlled.
ここで、管路1を通して送り込まれる被処理水
は流量調節弁31,32,33の開度に応じて曝
気槽11,12,13に分配され、同時に、沈殿
池21,22,23より引き抜かれた汚泥の一
部、すなわち、管路2を通して返送される返送汚
泥は流量調節弁41,42,43の開度に応じて
曝気槽11,12,13に分配され、この曝気槽
内で両者が混合される。次いで、この混合液は各
汚水処理系列の沈殿池21,22,23に流れ込
み、汚泥と上澄水とに分離され、汚泥は沈殿池下
部より引き抜かれ、上澄水が放流される。 Here, the water to be treated sent through the pipe 1 is distributed to the aeration tanks 11, 12, 13 according to the opening degrees of the flow rate control valves 31, 32, 33, and at the same time is drawn out from the settling tanks 21, 22, 23. A part of the sludge returned through the pipe line 2 is distributed to the aeration tanks 11, 12, 13 according to the opening degree of the flow rate control valves 41, 42, 43, and both are mixed in the aeration tank. mixed. Next, this mixed liquid flows into the settling tanks 21, 22, and 23 of each sewage treatment system, and is separated into sludge and supernatant water.The sludge is pulled out from the lower part of the settling tank, and the supernatant water is discharged.
一方、演算処理装置100は、少なくとも、被
処理水および返送汚泥を曝気槽11,12,13
に分配する分配比に対応した流量係数を設定する
機能と、被処理水の総流量信号QS、返送汚泥の
総流量信号QRおよびその濃度信号XC、ならびに、
曝気槽の汚泥濃度信号を記憶するとともに、その
記憶データに基いて曝気槽の被処理水と汚泥との
混合状態をシミユレートし、ポンプ51,52,
53が設置された位置に対応する汚泥濃度の時系
列データを算出する機能と、この時系列データお
よび汚泥濃度計6によつて実測された汚泥濃度デ
ータとを比較して各汚水処理系列の曝気槽に流入
する被処理水および返送汚泥の分配比を探索する
機能と、この分配比および流量係数を比較してそ
のずれが最も大きい汚水処理系列の流量調節弁を
制御する信号PS,PRとを出力する機能とを備え
ている。 On the other hand, the arithmetic processing device 100 at least sends the water to be treated and the returned sludge to the aeration tanks 11, 12, 13.
A function to set a flow rate coefficient corresponding to the distribution ratio to be distributed to, a total flow rate signal Q S of treated water, a total flow rate signal Q R of returned sludge and its concentration signal X C , and
The sludge concentration signal of the aeration tank is stored, and the mixed state of the water to be treated and the sludge in the aeration tank is simulated based on the stored data, and the pumps 51, 52,
The function calculates time series data of sludge concentration corresponding to the location where 53 is installed, and compares this time series data with the sludge concentration data actually measured by sludge concentration meter 6 to determine the aeration of each sewage treatment line. A function to search the distribution ratio of treated water flowing into the tank and return sludge, and a signal P S , P R that compares this distribution ratio and flow coefficient and controls the flow rate control valve of the sewage treatment line with the largest deviation. and a function to output.
なお、ポンプ51,52,53を、被処理水の
流下方向より見て、曝気槽長の略1/3の位置に設
けた理由は、これが被処理水の入口付近にあると
混合状態が不十分な混合液の汚泥濃度を測定する
ことになり、反対に、これより後方に持つてくる
と応答が遅れることにある。 The reason why the pumps 51, 52, and 53 are installed at approximately 1/3 of the length of the aeration tank when viewed from the downstream direction of the water to be treated is that if they are located near the inlet of the water to be treated, the mixing state will be unstable. This means measuring a sufficient sludge concentration of the mixed liquid; on the other hand, if it is brought further back than this, the response will be delayed.
以下、演算処理装置100の作用をさらに詳し
く説明する。 Hereinafter, the operation of the arithmetic processing device 100 will be explained in more detail.
先ず、演算処理装置100は流量計3の流量信
号QS、流量計4の流量信号QR、汚泥濃度計5の
汚泥濃度XCおよび汚泥濃度計6の汚泥濃度信号
Xaを一定の時間間隔で読み込み、一制御周期間
のデータを時系列データとして記憶しておく。 First, the processing unit 100 receives the flow rate signal Q S of the flow meter 3 , the flow rate signal Q R of the flow meter 4 , the sludge concentration X C of the sludge concentration meter 5 , and the sludge concentration signal of the sludge concentration meter 6 .
Read X a at regular time intervals and store the data for one control cycle as time series data.
次に、曝気槽シミユレータはこの時系列データ
を入力として、例えば、流量係数探索プログラム
と組合わせて、各曝気槽に流入する被処理水およ
び返送汚泥の流量係数を求める。 Next, the aeration tank simulator uses this time series data as input and combines it with a flow coefficient search program, for example, to find the flow coefficients of the treated water flowing into each aeration tank and the returned sludge.
なお、ここで言う流量係数とは第2図に示すよ
うに、被処理水の総流量QSと各曝気槽に流入す
る被処理水の流量との比、および、返送汚泥の総
流量QRと各曝気槽に流入する返送汚泥流量との
比であり、曝気槽11,12,13に流入する被
処理水の流量係数をAS1,AS2,AS3とし、返送汚
泥の流量係数をAR1,AR2,AR3とすると、次式の
関係が成立する。 The flow coefficient referred to here is the ratio of the total flow rate of treated water Q S to the flow rate of treated water flowing into each aeration tank, and the total flow rate of returned sludge Q R as shown in Figure 2. and the return sludge flow rate flowing into each aeration tank.The flow coefficients of the water to be treated flowing into the aeration tanks 11, 12, and 13 are A S1 , A S2 , A S3 , and the flow coefficient of return sludge is A When R1 , A R2 , and A R3 , the following relationship holds true.
AS1+AS2+AS3=1 …(1)
AR1+AR2+AR3=1 …(2)
しかして、曝気槽11,12,13にそれぞれ
流入する被処理水の流量はAS1・QS,AS2・QS,
AS3・QSとなり、返送汚泥の流量はAR1・QR,
AR2・QR,AR3・QRとなる。 A S1 +A S2 +A S3 =1...(1) A R1 +A R2 +A R3 =1...(2) Therefore, the flow rate of the treated water flowing into the aeration tanks 11, 12, and 13, respectively, is A S1・Q S , A S2・Q S ,
A S3・Q S , and the flow rate of the returned sludge is A R1・Q R ,
A R2・Q R and A R3・Q R.
ここで、演算処理装置100が流量係数AS1,
AS2,AS3およびAR1,AR2,AR3を求める手順とし
ては、先ずこれらの流量係数が全て等しいものと
して、演算処理装置内の時系列データを用いて、
各汚水処理系列のシミユレーシヨンを行い、シミ
ユレータで演算した実測点に対応する位置の汚泥
濃度と、実測された汚泥濃度の時系列データとの
差をとる。次に、流量係数の刻み幅を1/10として
最大勾配山登り探索法によつてシミユレーシヨン
値と実測値との差が最小となる流量係数を探す。
さらに、刻み幅を1/10として同様な探索を必要な
桁数がでるまで繰返す。 Here, the arithmetic processing unit 100 calculates the flow coefficient A S1 ,
The procedure for finding A S2 , A S3 , A R1 , A R2 , and A R3 is as follows: First, assuming that these flow coefficients are all equal, use time series data in the arithmetic processing unit.
A simulation is performed for each sewage treatment series, and the difference between the sludge concentration at the position corresponding to the actual measurement point calculated by the simulator and the time series data of the actually measured sludge concentration is calculated. Next, the step size of the flow coefficient is set to 1/10, and a maximum gradient hill climbing search method is used to find the flow coefficient that minimizes the difference between the simulation value and the actual measurement value.
Furthermore, the same search is repeated with the step width set to 1/10 until the required number of digits is obtained.
演算処理装置100はこのようにして被処理水
および返送汚泥の流量係数を求めるが、演算処理
装置100には各汚水処理系列に被処理水および
返送汚泥をどのような割合で分配するかを定める
流量係数が設定されており、続いてこの演算処理
装置100は被処理水および返送汚泥のそれぞれ
に対して、演算によつて得られた流量係数と設定
された流量係数とを汚水処理系列毎に比較し、そ
のずれが最も大きい汚水処理系列を選択し、この
汚水処理系列の流量調節弁を制御する信号PS,
PRをそれぞれ流量調節弁制御装置110および
120に加える。 The processing unit 100 calculates the flow rate coefficients of the water to be treated and the returned sludge in this manner, but the processing unit 100 also determines the ratio at which the water to be treated and the returned sludge are to be distributed to each sewage treatment line. A flow rate coefficient is set, and then this processing unit 100 calculates the flow rate coefficient obtained by calculation and the set flow rate coefficient for each of the water to be treated and the returned sludge for each sewage treatment line. The comparison is made, the sewage treatment system with the largest deviation is selected, and a signal P S , which controls the flow rate control valve of this sewage treatment system is selected.
P R is applied to flow control valve controllers 110 and 120, respectively.
これによつて、設定値に対してのずれの最も大
きい汚水処理系列の流量調節弁のみが制御されて
その流量が変化し、これに伴つて他の汚水処理系
列流量も変化することになる。かかる操作が制御
周期ごとに繰返される。 As a result, only the flow rate control valve of the sewage treatment system with the largest deviation from the set value is controlled and its flow rate changes, and the flow rates of the other sewage treatment systems also change accordingly. Such operations are repeated every control cycle.
この場合、演算処理装置100は時系列データ
を用いたシミユレーシヨンを行つて流量係数を探
索するため、制御周期はシミユレーシヨンを行う
に十分な時系列データが集まる時間よりも長くす
る必要がある。この実施例ではデータのサンプリ
ング周期を10分とし、制御周期を数時間とするこ
とによつて、当初の目的を十分に達成することが
できる。 In this case, since the arithmetic processing unit 100 performs simulation using time-series data to search for the flow rate coefficient, the control period needs to be longer than the time required to collect enough time-series data to perform the simulation. In this embodiment, the original purpose can be fully achieved by setting the data sampling period to 10 minutes and the control period to several hours.
一方、汚泥濃度計は前述したように機体差や測
定誤差を伴うため信頼性が低い。従来は汚泥濃度
計の指示値が等しくなるように流量制御弁を制御
していたので機体差および測定誤差が直接影響し
ていた。しかし、この実施例においては、1台の
汚泥濃度計に混合液を切換え送給して各汚水処理
系列の曝気槽の汚泥濃度を測定しているので、機
体差による悪影響を除去できている。さらに、こ
の実施例においては、演算処理装置で混合状態を
シミユレートしているので、汚泥濃度計の測定誤
差も容易に補正できる。その具体的な方法を以下
に簡単に説明する。 On the other hand, as mentioned above, sludge concentration meters have low reliability due to machine differences and measurement errors. Conventionally, flow control valves were controlled so that the indicated values of sludge concentration meters were equal, so machine differences and measurement errors had a direct effect. However, in this embodiment, the mixed liquid is switched and fed to one sludge concentration meter to measure the sludge concentration in the aeration tank of each sewage treatment system, so the adverse effects due to differences in machines can be eliminated. Furthermore, in this embodiment, since the mixing state is simulated by the arithmetic processing unit, measurement errors of the sludge concentration meter can be easily corrected. The specific method will be briefly explained below.
3系列ある曝気槽の汚泥濃度の実測値をX1
(t),X2(t),X3(t)とし、シミユレートによ
る算出値をY1(t),Y2(t),Y3(t)とすると
次式によつて求められる一日の全系列の汚泥濃度
の実測値の平均値および算出値の平均値は、
各系列の分配が一定であろうとなかろうと一定で
あるはずである。 The actual measured value of sludge concentration in the three aeration tanks is x 1
(t), X 2 (t), X 3 (t), and the simulated values are Y 1 (t), Y 2 (t), Y 3 (t). The average value of the measured values and the average value of the calculated values of sludge concentration for all series are:
It should be constant whether the distribution of each series is constant or not.
もし、ここでととが等しくなる場合には、
汚泥濃度計に誤差があることになる。この誤差
は、例えば、複数個のデータ、の相関をとつ
た補正曲線の傾きをA、切片をBとすると=
A・+Bのようにして補正することができる。
これによつて、汚泥濃度計に誤差があつたとして
もその補正ができることになる。 If and are equal here, then
This means that there is an error in the sludge concentration meter. For example, if the slope of a correction curve that correlates multiple pieces of data is A and the intercept is B, then this error is =
It can be corrected as A/+B.
With this, even if there is an error in the sludge concentration meter, it can be corrected.
また、従来は各汚水処理系列への流量分配はゲ
ートの開度を調節するのが殆どであつた。この場
合、ゲート開度を等しくしても、構造的には終端
の曝気槽の流入量が多くなることが避けられず、
当然のことながら汚水が多く流入した系列では汚
水の曝気槽に滞留する時間が短くなり処理水の水
質が悪化してしまう。この実施例では各汚水処理
系列の流量係数に基づいてその流量を制御してい
るので、処理の限界を知るためにある汚水処理系
列の流量を敢えて増加させるという特殊な場合を
除いて、一般的に要求される流量の均等化が容易
となる。 Furthermore, conventionally, the flow distribution to each sewage treatment line has mostly been done by adjusting the opening degree of the gate. In this case, even if the gate opening degree is the same, it is structurally unavoidable that the amount of inflow into the aeration tank at the end will increase.
Naturally, in lines where a large amount of sewage flows into the system, the time that the sewage remains in the aeration tank becomes shorter and the quality of the treated water deteriorates. In this example, the flow rate is controlled based on the flow rate coefficient of each sewage treatment line, so except for special cases where the flow rate of a certain sewage treatment line is intentionally increased to find out the limits of treatment, general This makes it easier to equalize the flow rates required.
なお、上記実施例では汚泥の濃度を検出するた
めに汚泥濃度計を用いているが、これを電気伝導
度計で代用することも可能である。 In addition, in the above embodiment, a sludge concentration meter is used to detect the concentration of sludge, but it is also possible to use an electrical conductivity meter instead.
また、上記実施例ではポンプを被処理水の流下
方向より見て曝気槽長の略1/3の位置に設けたが、
被処理水と汚泥とが十分に混合されている領域で
あればこれより前でも後でもよく、後方にずらせ
ば応答の遅れが出るだけであり、その位置に限定
されるものではない。 In addition, in the above embodiment, the pump was installed at a position approximately 1/3 of the length of the aeration tank when viewed from the downstream direction of the water to be treated.
As long as it is an area where the water to be treated and sludge are sufficiently mixed, it may be placed before or after this, and if it is moved to the rear, the response will be delayed, but it is not limited to this position.
さらにまた、上記実施例では各汚水処理系列に
被処理水および汚泥を均等に分配する例を示した
が、異なる比率で分配する場合にも適用し得るこ
とは勿論である。 Furthermore, although the above embodiment shows an example in which treated water and sludge are distributed equally to each sewage treatment line, it goes without saying that the present invention can also be applied to cases where the water and sludge are distributed at different ratios.
以上の説明によつて明らかな如く、本発明の曝
気槽流量制御方法によれば、機体差や測定誤差を
伴う汚泥濃度計を用いたとしても、複数の汚水処
理系列に流入する被処理水および返送汚泥を、目
標とする比率で分配し得、かつ、各曝気槽の汚泥
を健全な状態に保ち得、これによつて各汚水処理
系列とも良好な処理水が得られると言う優れた効
果がある。
As is clear from the above explanation, according to the aeration tank flow rate control method of the present invention, even if a sludge concentration meter with machine differences and measurement errors is used, the amount of water to be treated flowing into multiple sewage treatment lines and The return sludge can be distributed in a targeted ratio, and the sludge in each aeration tank can be kept in a healthy condition, which has the excellent effect of providing good treated water in each sewage treatment line. be.
第1図は本発明の曝気槽流量分配制御方法を実
施する装置の一例を、汚水処理系統と併せて示し
たブロツク図、第2図はその作用を説明するため
に、汚水処理系統に流入する被処理水および返送
汚泥の流量係数の関係を示した説明図である。
1,2…管路、3,4…流量計、5,6…汚泥
濃度計、11,12,13…曝気槽、21,2
2,23…沈殿池、31,32,33,41,4
2,43…流量調節弁、51,52,53…ポン
プ、100…演算処理装置、110,120…流
量調節弁制御装置。
Fig. 1 is a block diagram showing an example of an apparatus for implementing the aeration tank flow rate distribution control method of the present invention, together with a sewage treatment system, and Fig. 2 is a block diagram showing an example of an apparatus for implementing the aeration tank flow rate distribution control method of the present invention, together with a sewage treatment system. It is an explanatory diagram showing the relationship between flow coefficients of treated water and returned sludge. 1, 2... Pipe line, 3, 4... Flow meter, 5, 6... Sludge concentration meter, 11, 12, 13... Aeration tank, 21, 2
2, 23... Sedimentation basin, 31, 32, 33, 41, 4
2, 43...Flow rate control valve, 51,52,53...Pump, 100...Arithmetic processing unit, 110,120...Flow rate control valve control device.
Claims (1)
系列にそれぞれ被処理水の分配量を調節する第1
の流量調節弁と、前記沈殿池から前記曝気槽への
返送汚泥の分配量を調節する第2の流量調節弁と
を設けると共に、前記曝気槽の被処理水と汚泥と
の混合状態をシミユレートし、その結果に基づい
て前記第1および第2の流量調節弁を制御する曝
気槽流量分配制御方法において、 前記被処理水および返送汚泥の分配比に対する
汚水処理系列毎の流量係数を演算処理装置に設定
し、 前記曝気槽に流入する被処理水の総流量、この
曝気槽に流入する返送汚泥の総流量およびその濃
度をそれぞれ測定した信号と、前記各曝気槽内の
被処理水と汚泥との混合液を曝気槽外の1台の濃
度計に順次送り込んで曝気槽毎に汚泥濃度を測定
した信号とを前記演算処理装置に取込み、 前記演算処理装置は、先ずこれらの測定データ
を記憶すると共に、その記憶データに基づいて前
記曝気槽の被処理水と汚泥との混合状態を前記汚
水処理系列毎にシミユレートすることによつて、
前記各曝気槽の汚泥濃度の実測位置に対応する汚
泥濃度の時系列データを算出し、次いでこの時系
列データと実測された汚泥濃度データとを前記汚
水処理系列毎に比較して両データの差が最も小さ
くなる前記各汚水処理系列の曝気槽に流入する被
処理水および返送汚泥の流量係数を探索し、続い
て、この流量係数および前記設定による流量係数
を比較してそのずれが最も大きい汚水処理系列の
前記第1および第2の流量調節弁を調節すること
を特徴とする曝気槽流量分配制御方法。[Claims] 1. The aeration tank and the settling tank are arranged in series, and the first one adjusts the amount of water to be treated to be distributed to each of these series.
and a second flow rate regulating valve for regulating the distribution amount of return sludge from the settling tank to the aeration tank, and simulating the mixing state of the water to be treated and the sludge in the aeration tank. , in the aeration tank flow rate distribution control method of controlling the first and second flow rate control valves based on the results, the flow rate coefficient for each sewage treatment line with respect to the distribution ratio of the water to be treated and the return sludge is determined by an arithmetic processing device. The total flow rate of the water to be treated flowing into the aeration tank, the total flow rate and concentration of return sludge flowing into the aeration tank, and the signal obtained by measuring the concentration of the water to be treated and the sludge in each of the aeration tanks. A signal obtained by sequentially sending the mixed liquid to one concentration meter outside the aeration tank and measuring the sludge concentration for each aeration tank is taken into the arithmetic processing unit, and the arithmetic processing unit first stores these measurement data and , by simulating the mixing state of the water to be treated and sludge in the aeration tank for each of the sewage treatment lines based on the stored data,
The time series data of the sludge concentration corresponding to the actual measurement position of the sludge concentration in each aeration tank is calculated, and then this time series data and the actually measured sludge concentration data are compared for each of the sewage treatment series to determine the difference between both data. Find the flow rate coefficient of the treated water and return sludge flowing into the aeration tank of each sewage treatment system that has the smallest value, and then compare this flow rate coefficient with the flow rate coefficient based on the settings above to find the sewage water with the largest deviation. An aeration tank flow rate distribution control method, comprising adjusting the first and second flow rate control valves of a treatment series.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57105131A JPS58223488A (en) | 1982-06-18 | 1982-06-18 | Control method for distribution of flow rate in aeration tank |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57105131A JPS58223488A (en) | 1982-06-18 | 1982-06-18 | Control method for distribution of flow rate in aeration tank |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS58223488A JPS58223488A (en) | 1983-12-26 |
| JPH0256960B2 true JPH0256960B2 (en) | 1990-12-03 |
Family
ID=14399203
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57105131A Granted JPS58223488A (en) | 1982-06-18 | 1982-06-18 | Control method for distribution of flow rate in aeration tank |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS58223488A (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2007283284A (en) * | 2006-03-23 | 2007-11-01 | Matsushita Electric Ind Co Ltd | Wastewater treatment equipment |
Family Cites Families (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5196171A (en) * | 1975-02-21 | 1976-08-23 | ||
| JPS5264157A (en) * | 1975-11-25 | 1977-05-27 | Hokushin Electric Works | Return sludge controller of waste water treating device |
| JPS5556893A (en) * | 1978-10-25 | 1980-04-26 | Nobutsugu Kato | Controlling method for total outgoing sludge of aeration tank in activated sludge method |
-
1982
- 1982-06-18 JP JP57105131A patent/JPS58223488A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS58223488A (en) | 1983-12-26 |
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