JPS5834192B2 - Gensuijiyoukaseigiyosouchi - Google Patents
GensuijiyoukaseigiyosouchiInfo
- Publication number
- JPS5834192B2 JPS5834192B2 JP50115528A JP11552875A JPS5834192B2 JP S5834192 B2 JPS5834192 B2 JP S5834192B2 JP 50115528 A JP50115528 A JP 50115528A JP 11552875 A JP11552875 A JP 11552875A JP S5834192 B2 JPS5834192 B2 JP S5834192B2
- Authority
- JP
- Japan
- Prior art keywords
- turbidity
- signal
- raw water
- coefficient
- flow rate
- 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
Links
Landscapes
- Treatment Of Sludge (AREA)
Description
【発明の詳細な説明】
本発明は浄水場等において原水を浄化する原水浄化制御
装置に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a raw water purification control device for purifying raw water in a water purification plant or the like.
河川水等を原水とする上水道の浄水場では汚れた原水を
使用目的に適合するまで浄化する必要がある。In water treatment plants for waterworks that use river water as raw water, it is necessary to purify contaminated raw water until it is suitable for the intended use.
そして従来より原水を浄化するため浮遊しているコロイ
ド物質を硫酸アルミニュームやポリ塩化アルミニューム
等の多価金属の凝集剤を注入することにより凝集沈澱さ
せ、砂流過等を行なって原水を浄化している。Conventionally, in order to purify raw water, floating colloidal substances are coagulated and precipitated by injecting coagulants of polyvalent metals such as aluminum sulfate or polyaluminum chloride, and the raw water is purified by sand flow etc. ing.
このとき原水を使用目的に適合した状態にするため、前
述の多価金属の凝集剤を原水に注入する注入率は原水の
濁度、アルカリ度、pH値水温等の変化によって異なる
が、その中でも濁度によって最も影響を受ける。At this time, in order to make the raw water suitable for the purpose of use, the injection rate at which the polyvalent metal coagulant mentioned above is injected into the raw water varies depending on changes in the turbidity, alkalinity, pH value, water temperature, etc. of the raw water. Most affected by turbidity.
例えば降雨などによって原水が濁ってくる場合、第1図
のようになる。For example, when raw water becomes cloudy due to rain, it becomes as shown in Figure 1.
つまり降雨によって濁度が次第に上昇し、雨が止んで濁
度が下降する。In other words, the turbidity gradually increases due to rainfall, and when the rain stops, the turbidity decreases.
このとき上昇時と下降時に同一濁度Aをとるが従来では
特別、濁度上昇時と下降時に注入率を変化させることな
く、一定注入率で凝集剤を注入していた。At this time, the same turbidity A is taken when the turbidity rises and when it falls, but in the past, flocculant was injected at a constant injection rate without changing the injection rate when the turbidity rose and fell.
しかし、濁度が上昇する場合と、下降する場合とでは同
一濁度があっても原水中の粒子の大きさが異なるため浄
化時間等が異なり同一注入率では浄化効率が悪かった。However, when the turbidity increases and when it decreases, even if the turbidity is the same, the size of the particles in the raw water is different, so the purification time etc. are different and the purification efficiency is poor at the same injection rate.
本発明ではこの欠点を除去するため濁度の上昇時と下降
時とでは注入率を変えて凝集剤を原水に注入することに
より原水の浄化効率を高め最適化された原水浄化制御装
置の提供にある。In order to eliminate this drawback, the present invention aims to improve the purification efficiency of raw water by injecting flocculant into raw water at different injection rates when the turbidity increases and decreases, thereby providing an optimized raw water purification control device. be.
本発明ではこの目的を達成するため濁度の上昇時と下降
時では同一濁度でも凝集剤の注入率を変えることにより
行なう。In the present invention, in order to achieve this objective, the injection rate of the flocculant is changed when the turbidity increases and when the turbidity decreases even when the turbidity is the same.
つまり第2図のように濁度と時間の曲線において濁度変
化量JTB=TB(tn)−’I’B(tn−t )が
0以上のときの注入率と0より小さいときの注入率とを
変化させることにより行なう。In other words, as shown in Figure 2, in the turbidity vs. time curve, the injection rate when the turbidity change JTB = TB (tn) - 'I'B (tn - t) is greater than 0 and the injection rate when it is less than 0. This is done by changing the
以下本発明を一実施例について図を参照して説明する。DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described below with reference to the drawings.
第3図は原水浄化制御装置の実施例で原水を配管1を通
して薬品混和池2に送くり、凝集剤タンク3からの凝集
剤で浄化する装置である。FIG. 3 shows an embodiment of a raw water purification control device, in which raw water is sent through a pipe 1 to a chemical mixing pond 2 and purified with a flocculant from a flocculant tank 3.
配管1には流量発信器4が設けられ、この流量発信器4
より2人力を乗算する乗算器5の1人力として乗算器5
に原水の流量信号Fが加えられる。A flow rate transmitter 4 is provided in the pipe 1, and this flow rate transmitter 4
Multiplier 5 as one-manpower of multiplier 5 which multiplies two-manpower
A flow rate signal F of raw water is added to .
凝集剤を凝集剤クンク3から薬品混和池2に注入するた
めに配管6が設けられ、この配管6には凝集剤の流量を
検出する流量発信器7が設けられている。A piping 6 is provided to inject the flocculant from the flocculant tank 3 into the chemical mixing pond 2, and this piping 6 is provided with a flow rate transmitter 7 for detecting the flow rate of the flocculant.
また原水は配管1よりポンプ8によって吸い上げられ、
濁度検出器9に送くられ濁度に比例した濁度信号TBを
発する。In addition, raw water is sucked up from pipe 1 by pump 8,
The turbidity signal TB is sent to the turbidity detector 9 and generates a turbidity signal TB proportional to the turbidity.
この濁度信号TBは比較器10で凝集剤の注入率を変え
なくてはならない基準の濁度つまり第2図に示された濁
度TBHと比較され基準濁度TBH<濁度TBになった
とき出力リレー11を励磁する。This turbidity signal TB is compared with the standard turbidity, which requires changing the flocculant injection rate, ie, the turbidity TBH shown in FIG. When the output relay 11 is energized.
この基準濁度は河川の特性すなわち通常降雨のないとき
の平均濁度を求め、多少の濁度変化で比較器10が出力
リレー11を励磁できないように不感帯を設ける意味で
平均濁度の2〜3倍の値にとるのが普通である。This reference turbidity is determined by determining the river characteristics, that is, the average turbidity when there is no normal rainfall, and providing a dead zone so that the comparator 10 cannot excite the output relay 11 due to a slight change in turbidity. It is common to take three times the value.
また濁度信号TBは2人力を比較する比較器12の1人
力として比較器12に加わり、接点13aを介して信号
記憶器14にも加わる。Further, the turbidity signal TB is applied to the comparator 12 as one-manpower of the comparator 12 that compares the two-manpower, and is also applied to the signal memory 14 via the contact 13a.
接点13aは定周期サンプル信号発生器13によって所
定周期ごとに開閉し、信号記憶器14は入力を次の入力
が加わるまで記憶し、記憶していた信号を比較器12の
他の入力として出力する。The contact 13a is opened and closed at predetermined intervals by the fixed-period sample signal generator 13, and the signal storage 14 stores the input until the next input is applied, and outputs the stored signal as the other input of the comparator 12. .
したがって比較器12は現在の濁度と一周期前の濁度と
の差すなわち濁度の増加或は減少方向かの極性を求め、
現在の濁度より信号記憶器14に記憶していた濁度の方
が大きいときにすなわち濁度が減少方向のときに出力を
出す。Therefore, the comparator 12 determines the difference between the current turbidity and the turbidity one cycle ago, that is, the polarity of increasing or decreasing turbidity.
An output is output when the turbidity stored in the signal storage device 14 is greater than the current turbidity, that is, when the turbidity is decreasing.
すなわちこれらは極性検知回路を形成する。That is, they form a polarity detection circuit.
この出力は基準濁度’l’BH<濁度TBの条件のとき
に閉じる出力リレー11の接点11aを介して出力リレ
ー15を励磁する。This output excites the output relay 15 via the contact 11a of the output relay 11, which closes when the reference turbidity 'l'BH<turbidity TB.
このリレー15は基準濁度TBH<濁度TBでかつ濁度
の変化が減少の傾向のとき励磁状態となり、増加傾向の
とき非励磁状態となる。This relay 15 becomes energized when reference turbidity TBH<turbidity TB and the change in turbidity tends to decrease, and becomes de-energized when the change in turbidity tends to increase.
さらに濁度信号TBは演算器16に加わり、この演算器
16より注入関数f (’I’B)が係数演算器17,
18に加わる。Furthermore, the turbidity signal TB is applied to a computing unit 16, and the injection function f ('I'B) is inputted from this computing unit 16 to a coefficient computing unit 17,
Join 18.
この注入関数f(TB)はf (TB) =Ct +
C2X T もしくはf (TB)=c3+c、X、
/テ爾等によって表わされる。This injection function f(TB) is f(TB) = Ct +
C2X T or f (TB)=c3+c,X,
/ Represented by Te et al.
ただしC1〜C4は定数)。係数演算器17は係数に1
.18は係数に2を演算器16の出力に乗じそれぞれ接
点15a、15bを介して乗算器5の他の入力として乗
算器5に加わる。However, C1 to C4 are constants). The coefficient calculator 17 sets the coefficient to 1.
.. A coefficient 18 multiplies the output of the arithmetic unit 16 by 2 and is applied to the multiplier 5 as another input to the multiplier 5 via contacts 15a and 15b, respectively.
すなわち各係数演算器17,18によって注入関数f(
TB)かに倍され、演算器の出力の勾配を変化させてい
る。That is, the injection function f(
TB), which changes the slope of the output of the arithmetic unit.
接点15a、15bは出力リレー15によって作動する
互に開閉を異にする接点である。The contacts 15a and 15b are contacts that are operated by the output relay 15 and open and close differently.
そして出力リレー15が動作している間接点15aが閉
じ、接点15bが開いている。Then, the contact point 15a where the output relay 15 operates is closed, and the contact point 15b is open.
つまり濁度の変化量が正(濁度上昇)のときに接点15
bが閉じ、接点15aが開いてに1f(TB)を乗算器
5に加え、変化量が負(濁度下降)のときに接点15a
が閉じ、接点15bが開いてに2 f (TB )を乗
算器5に加える。In other words, when the amount of change in turbidity is positive (turbidity rise), contact 15
When b closes and contact 15a opens, 1f (TB) is added to multiplier 5, and when the amount of change is negative (turbidity decrease), contact 15a
closes, contact 15b opens and adds 2 f (TB) to multiplier 5.
したがって乗算器5からKtf(TB)Fまたはに2
f (TB)Fが出力され、この信号は基準信号として
流量調節計19に加えられ、この流量調節計19で流量
発信器7から流量信号と比較されて調節信号が配管6に
設けられた電磁弁20に加えられる。Therefore from multiplier 5 to Ktf(TB)F or to 2
f (TB)F is output, this signal is applied as a reference signal to the flow rate controller 19, and the flow rate controller 19 compares it with the flow rate signal from the flow rate transmitter 7, and an adjustment signal is sent to the electromagnetic device provided in the piping 6. added to valve 20.
したがって電磁弁20は濁度上昇時と濁度下降時とで異
なった基準信号によって制御される。Therefore, the solenoid valve 20 is controlled by different reference signals when the turbidity increases and when the turbidity decreases.
そのため原水の濁度が上昇し、基準濁度TBHを越える
と比較器10によって出力リレー11が励磁されて接点
11aが閉じ、なお上昇が続けば定周期サンプル信号発
生器13、信号記憶器14、比較器12が動作して濁度
の変化量の極性から上昇を検知する。Therefore, when the turbidity of the raw water increases and exceeds the reference turbidity TBH, the output relay 11 is energized by the comparator 10 and the contact 11a is closed. The comparator 12 operates to detect an increase based on the polarity of the amount of change in turbidity.
このとき比較器12の出力が出ないため接点15bが開
じ、接点15aは開の状態を保つので流量調節計19は
に1f (TB ) Fを基準信号として凝集剤の注入
量を制御する。At this time, since there is no output from the comparator 12, the contact 15b is opened, and the contact 15a remains open, so the flow rate controller 19 controls the injection amount of the flocculant using 1f (TB) F as a reference signal.
濁度が下降のときは比較器12の出力により出力リレー
15が動作し接点15bを開け、接点15aを閉じるの
でに2f(TB)Fを基準信号として凝集剤の注入量を
制御する。When the turbidity is decreasing, the output relay 15 is activated by the output of the comparator 12 to open the contact 15b and close the contact 15a, thereby controlling the injection amount of the flocculant using 2f(TB)F as a reference signal.
以上のように本発明によれば濁度の上昇時と下降時で凝
集剤を注入する際の基準信号を原水流量信号に乗する係
数を変化させることにより変えているので最適制御がで
きるという効果を有し、浄化効率が高まる。As described above, according to the present invention, the reference signal for injecting the flocculant when the turbidity rises and falls is changed by changing the coefficient by which the raw water flow rate signal is multiplied, so that optimal control can be achieved. , which increases purification efficiency.
また本発明において、基準濁度TBH以下のときに別の
係数に3を乗じてもよく、濁度の大きさに応じて種々の
係数を乗することによって実施できる。Further, in the present invention, another coefficient may be multiplied by 3 when the reference turbidity TBH or less, and this can be implemented by multiplying various coefficients depending on the magnitude of the turbidity.
また出力リレー、接点を電子スイッチ等に置き換えても
よい。Further, the output relay and contacts may be replaced with electronic switches or the like.
さらにアナログ的演算処理ではなくマイクロコンピュー
タ等を利用したディジタル処理で行なってもよい。Furthermore, instead of analog calculation processing, digital processing using a microcomputer or the like may be used.
第1図は時間に対する濁度の変化を示した図、第2図は
濁度関数を示した図、第3図は本発明の一実施例のブロ
ック図である。
1.6・・・・・・配管、4,7・・・・・・流量発信
器、5・・・乗算器、9・・・・・・濁度検出器、10
,12・・・・・・比較器、11,15・・・・・・出
力リレー、13・・・・・・定周期サンプル信号発生器
、14・・・・・・信号記憶器、17゜18・・・・・
・係数演算器、19・・・・・・流量調節計。FIG. 1 is a diagram showing changes in turbidity over time, FIG. 2 is a diagram showing a turbidity function, and FIG. 3 is a block diagram of an embodiment of the present invention. 1.6... Piping, 4, 7... Flow rate transmitter, 5... Multiplier, 9... Turbidity detector, 10
, 12... Comparator, 11, 15... Output relay, 13... Fixed period sample signal generator, 14... Signal storage, 17° 18...
・Coefficient calculator, 19...Flow rate controller.
Claims (1)
、原水の流量を検出する流量検出器と、原水の濁度を検
出する濁度検出器と、この濁度検出器の濁度信号より濁
度の変化量の極性を求める極性検知回路と、前記濁度信
号と基準濁度信号とを比較する比較器と、前記濁度信号
を入力して前記極性検知回路の極性に対応した係数をそ
れぞれ算出する回路と、前記比較器により前記濁度信号
が前記基準濁度信号以上となったときの前記極性検知回
路の出力により選択された係数を出力する回路と、前記
流量検出器の出力に選択された係数を乗じた信号を出力
する係数回路と、前記係数回路の出力を基準信号として
前記薬剤の原水への注入を調節する調節計とを備え、濁
度の上昇時と下降時によって乗する前記係数を変化させ
ることを特徴とする原水浄化制御装置。1 In a device that purifies raw water by injecting chemicals into raw water, there is a flow rate detector that detects the flow rate of raw water, a turbidity detector that detects the turbidity of raw water, and a turbidity signal from this turbidity detector. a polarity detection circuit that calculates the polarity of the amount of change in turbidity; a comparator that compares the turbidity signal with a reference turbidity signal; a circuit for calculating, a circuit for outputting a coefficient selected by the output of the polarity detection circuit when the turbidity signal becomes equal to or higher than the reference turbidity signal by the comparator, and a coefficient selected for the output of the flow rate detector. a coefficient circuit that outputs a signal multiplied by a coefficient, and a controller that adjusts the injection of the drug into the raw water using the output of the coefficient circuit as a reference signal, and multiplies the signal depending on when the turbidity increases or decreases. A raw water purification control device characterized by changing the coefficient.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP50115528A JPS5834192B2 (en) | 1975-09-26 | 1975-09-26 | Gensuijiyoukaseigiyosouchi |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP50115528A JPS5834192B2 (en) | 1975-09-26 | 1975-09-26 | Gensuijiyoukaseigiyosouchi |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5239955A JPS5239955A (en) | 1977-03-28 |
| JPS5834192B2 true JPS5834192B2 (en) | 1983-07-25 |
Family
ID=14664748
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP50115528A Expired JPS5834192B2 (en) | 1975-09-26 | 1975-09-26 | Gensuijiyoukaseigiyosouchi |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5834192B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS63256108A (en) * | 1987-04-10 | 1988-10-24 | Ebara Infilco Co Ltd | Method for controlling injection of flocculant |
| JPH04338203A (en) * | 1991-05-14 | 1992-11-25 | Fujita Corp | Turbid water treatment |
-
1975
- 1975-09-26 JP JP50115528A patent/JPS5834192B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5239955A (en) | 1977-03-28 |
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