JPS6028889A - Controlling device for activated sludge amount - Google Patents
Controlling device for activated sludge amountInfo
- Publication number
- JPS6028889A JPS6028889A JP58137171A JP13717183A JPS6028889A JP S6028889 A JPS6028889 A JP S6028889A JP 58137171 A JP58137171 A JP 58137171A JP 13717183 A JP13717183 A JP 13717183A JP S6028889 A JPS6028889 A JP S6028889A
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- return
- value
- amount
- aeration tank
- 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.)
- Granted
Links
- 239000010802 sludge Substances 0.000 title claims abstract description 175
- 238000005273 aeration Methods 0.000 claims abstract description 25
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 13
- 238000005259 measurement Methods 0.000 claims abstract description 9
- 238000004062 sedimentation Methods 0.000 claims description 13
- 241000372132 Hydrometridae Species 0.000 claims 1
- 238000000034 method Methods 0.000 description 11
- 238000010586 diagram Methods 0.000 description 7
- 238000000605 extraction Methods 0.000 description 5
- 230000007423 decrease Effects 0.000 description 4
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 230000014759 maintenance of location Effects 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 210000000078 claw Anatomy 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 238000011326 mechanical measurement Methods 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 230000001932 seasonal effect Effects 0.000 description 1
- 238000009958 sewing Methods 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
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)
Abstract
Description
【発明の詳細な説明】
この発明は下水処理システムに使用される活性汚泥縫制
御装置に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an activated sludge sewing control device used in a sewage treatment system.
従来、F水処理システムにおいてtよ余剰汚泥制御方式
が使用されていた。この制御方式を第1図に示すが、こ
の方式は一般に汚泥LJ令(SA)制御として従来から
実施されている。以Fm1図について述べるに、この方
式はエアレーションタンク/内の汚泥量(MA)のある
一定割合を余剰汚泥(MW )として引抜く方法で、汚
泥の沈降特性(汚泥容清指標S V 工)が安定してい
て、且つ処理系内全汚泥j]、がエアレーションタンク
/内の汚泥量にほぼ等しい場合には良い制御結果が得ら
れることが知られている。図中、2は最終沈殿池、3は
最終沈殿池λから返送汚泥を工°アレージョンタンク/
に返送させる返送汚泥ポンプ、lは最終沈殿池コから余
剰汚泥を引抜く余剰汚泥ポンプである。Sはエアレーシ
ョンタンク内汚泥it(MA)と余剰汚泥引抜き@(M
W)とを演r)、する演算制御装置で、この演算制御装
置5には混合浮遊物濃度計(MLS Sil ) 、<
のMLSS値、返送汚泥濃度計7の汚泥日令値(s A
) 、余剰汚泥ポンプ♂の余剰汚泥引抜回数値(川、エ
アレーションタンク容積(m”)(VA)および引抜き
時刻(T)がJj見られる。Conventionally, a surplus sludge control method has been used in F water treatment systems. This control method is shown in FIG. 1, and this method has been conventionally generally implemented as sludge LJ order (SA) control. In the following, referring to the Fm1 diagram, this method is a method in which a certain percentage of the sludge amount (MA) in the aeration tank is extracted as surplus sludge (MW), and the settling characteristics of the sludge (sludge volume index SV) are It is known that good control results can be obtained if the total sludge in the treatment system is stable and is approximately equal to the amount of sludge in the aeration tank. In the figure, 2 is the final sedimentation tank, and 3 is the final sedimentation tank where the sludge is returned from the final sedimentation tank λ.
1 is a return sludge pump that returns excess sludge to the final settling tank. S is the sludge in the aeration tank (MA) and excess sludge extraction @ (M
W) and r), and this arithmetic and control device 5 includes a mixed suspended matter concentration meter (MLS Sil), <
MLSS value of return sludge concentration meter 7 sludge age value (s A
), the number of times the surplus sludge has been pulled out by the surplus sludge pump ♂, the aeration tank volume (m”) (VA), and the time of withdrawal (T) can be seen.
なお、MAどMWはそれぞれ次式で行われる。Note that MA and MW are each performed using the following formulas.
MA=MLSSXVA 、MW−1/NXMA/SA上
記演算制#装置置Sの演η、出力はnij記余剰汚泥づ
(ンプ弘に供給され、そのポンプ≠が制御される。MA=MLSSXVA, MW-1/NXMA/SA The output of the arithmetic control device S is supplied to the surplus sludge pump, and its pump is controlled.
上述のように構成された制御方式を用い°C汚泥の沈降
特性が安定していて、且つ処理系内全汚泥量がエアレー
ションタンク内の汚泥量にt1#χ等しいときは前述の
ように制御は良好に行われる。しかし、汚泥の沈降特性
(SVI)が変動する場合は、この変動に伴って、エア
レーションタンク内汚泥鼠(MA)と最終沈殿池λ内の
汚泥分布状態〃ヌ変動シ、コのため、エアレーションタ
ンク内汚泥爪(MA)で系内汚泥量(エアレーショ/タ
ンク内汚泥量+最終沈殿池内汚泥N)を代表することが
不可能になってくる。Using the control method configured as described above, if the sedimentation characteristics of °C sludge are stable and the total amount of sludge in the treatment system is equal to the amount of sludge in the aeration tank t1#χ, the control is performed as described above. Well done. However, when the settling characteristics (SVI) of sludge fluctuates, the sludge distribution state in the aeration tank (MA) and the final settling tank λ changes due to this fluctuation. It becomes impossible to represent the amount of sludge in the system (aeration/sludge amount in the tank + sludge N in the final settling tank) by the internal sludge claw (MA).
例えば、 SVIが上孔(一般にsvrが200以上の
場ハ、バルギンク汚泥と言われる)するに伴い、最終沈
殿池2では汚泥の沈降速度が低下する。また、沈殿した
汚泥の濃度(圧密濃度)も低下し、定量返送時では汚泥
界面が上杵する。この結果、最終沈殿池λ内の滞留汚泥
量は増加し、この増加分だけエアレーションタンク内汚
泥f!t、(MA)が減少する。このようなとき、余剰
汚泥引抜き縫(MW)はsv■の上昇前よシも減少する
ため、汚泥日令(SA)は設定値よりも長くなってしま
う。上記のことがらSVZが変動するときけ前記SA制
御方式では汚泥日令(SA)を一定に制御できなくなる
。夜た、返送汚泥只(または返送汚泥率:返送汚泥量/
流入汚水糾)が変動したときも、SVIが変動する。鴨
合と同様に、エアレーションタンクl内と最終沈殿池λ
内の汚泥分布がsh制御方式では汚泥日令(sA)を一
定に保つことはできなくなる。For example, as the SVI increases to the upper hole (generally speaking, if the svr is 200 or more, it is called bulking sludge), the sedimentation rate of the sludge in the final settling tank 2 decreases. In addition, the concentration of the settled sludge (consolidated concentration) also decreases, and the sludge interface becomes upper punch during quantitative return. As a result, the amount of accumulated sludge in the final settling tank λ increases, and the sludge in the aeration tank f! t, (MA) decreases. In such a case, the excess sludge drawing stitch (MW) decreases even before sv■ rises, so the sludge daily age (SA) becomes longer than the set value. As a result of the above, when the SVZ fluctuates, the SA control method cannot control the sludge age (SA) at a constant level. At night, return sludge only (or return sludge rate: return sludge amount /
SVI also changes when the inflow sewage concentration changes. Similar to Kamoai, the inside of the aeration tank l and the final settling tank λ
With the sh control method, it becomes impossible to keep the sludge age (sA) constant.
上記SA制御方式では汚泥の平均滞留時間が−にに保持
できない場合が生じたがこの原因は次の如くである。す
なわち、返送汚泥率の変化や活性汚泥の沈降特性(Bv
工)の変化によシェアレーションタンク/内と最終沈殿
池コ内の汚泥量の分布状態が変化し、その結果、エアレ
ーションタンク/内の汚泥NCMA)から余剰汚泥!t
(MW)を演算するSA制御であるために1平均滞留時
間を設定値に維持することができないためである。In the SA control method described above, there were cases where the average residence time of sludge could not be maintained at -2, and the reason for this is as follows. In other words, changes in the return sludge rate and sedimentation characteristics of activated sludge (Bv
The distribution of sludge in the sharing tank and the final settling tank changes due to changes in the sludge NCMA) in the aeration tank. t
This is because the SA control calculates (MW), so one average residence time cannot be maintained at the set value.
そこで、エアレーションタンク/内の汚泥fv(MA)
を制御対象とするのではなく、最終沈殿池λを含めた処
理系内全汚泥量を制御対象にすることが必要になる。こ
のためには、最終沈殿r1.lx J内の汚泥tを演算
する必要があるけれども、最終沈殿池λ内の汚泥の挙動
は非常にすy雑であることが知られていることと、内部
に蓄積されている汚泥N′金正確に計9.するためには
F5.’、’jliな数値n1nが必要となシ通′帛の
制御装Ffでは演nすることができなかった。Therefore, the sludge fv (MA) in the aeration tank/
It is necessary to control the total amount of sludge in the treatment system, including the final sedimentation tank λ, rather than the amount of sludge in the final settling tank λ. For this, the final precipitation r1. Although it is necessary to calculate the sludge t in lx J, it is known that the behavior of sludge in the final settling tank λ is very rough, and the sludge N Exactly 9. To do this, use F5. It was not possible to perform the calculation using the conventional control device Ff, which requires a numerical value n1n that is ','jli.
この発明は七〇己の事情に鑑みでなされたもので、汚泥
客用指標nr+1tjt装置i’Y (s v工測定装
置)を用いて活性汚泥の沈降/19性全演111QII
定し、この演算結果、流入木肌および返送汚泥#代金演
算してエアレーションタンクに返送するllノ泥亀を返
送汚泥禁制ぜ111装置道で制御するとともに前fl1
28 V工測定装詩の債り結果、MLSS値、流入水J
ft 、収送汚泥周および余剰汚泥1吐を(Iルて最終
沈殿池から余剰汚泥Iktl−制岬装債制御御して引抜
くようにしたので。This invention was made in view of my own circumstances, and it is possible to measure the sedimentation of activated sludge using the sludge customer index nr+1tjt device i'Y (sv engineering measuring device).
As a result of this calculation, the amount of inflow wood grain and return sludge is calculated, and the return sludge is prohibited.
28 V engineering measurement equipment bond results, MLSS value, inflow water J
ft, collected sludge and surplus sludge are pulled out from the final settling tank under control.
簡単な制御装置で汚泥の平均滞留時間音一定に保持する
制御全可能とした活性汚泥風制御装置を提供することを
目的とする。It is an object of the present invention to provide an activated sludge airflow control device that can control the average residence time of sludge at a constant level using a simple control device.
以下図面ケ参照してこの発明の一実が(i例ケ説明する
に第1図と同一部分は同−t’r号を付して示す。Hereinafter, one embodiment of the present invention will be explained with reference to the drawings (Example 1). Parts that are the same as those in FIG.
第2図において、IOは汚泥量Jet:it (s v
計)10aと汚泥客層指標(S V工)演お一装置In
+1からなるSV工測測定装置ある。前記S V i
’ii/(j aにはポンプ/lにより工Iレーション
タンク/から汚泥が供給され、またSVI演算装Fi、
10bにはM TJ SS ii AからMLSEI値
とSV計/(7aの計測値が供給さJLる。前iピSV
工測定装首10はSV計/(7aによシ後述(第3図)
する汚泥の沈降曲線、測定開始からt分後の汚泥容ri
svt、80分後の汚泥容量sv!l、、とML8Sイ
1NからSViの測定を行う。この測定結果は返送汚泥
回路19.制徊1装置12に人力される。この制御装f
l/コには流入水流膜tit /、?がらの流入水1・
支と返送汚泥回路/’71c設けられた7Fi 、、、
、;Hγυ泥流ji’(11”3がらの返送汚泥#代が
人力さI+、、tiiJ itJ I”I V I 1
lll定結果とともに演−aされてその濱4I出方がリ
ミツタ/6K IJ% 給すれる。In Figure 2, IO is the sludge amount Jet:it (s v
Total) 10a and sludge customer index (SV engineering) performance equipment In
There is an SV construction measuring device consisting of +1. Said S V i
'ii/(j A is supplied with sludge from the construction tank/ by a pump/l, and the SVI computing unit Fi,
10b is supplied with the MLSEI value and the measured value of 7a from M TJ SS ii A.
The mechanical measurement head 10 is an SV meter/(described later in 7a (Fig. 3)).
sludge sedimentation curve, sludge volume ri after t minutes from the start of measurement
svt, sludge volume sv after 80 minutes! SVi is measured from 1, , and ML8S1N. This measurement result is the return sludge circuit 19. The wandering control device 12 is operated manually. This control device f
l/co has an inflow water flow membrane tit/,? Inflow of water 1・
Support and return sludge circuit/'71c installed 7Fi...
,;Hγυ mudflow ji'(11"3 pieces of returned sludge # cost is manual labor I+,, tiiJ itJ I"I V I 1
It is calculated along with the fixed result and the result is given to the limiter/6K IJ%.
リミツタ/Aの出力L、J: ニアi、 :J汚泥ポン
プ3にJシ見られてポンプが制御さノシ、返送汚泥回路
″1i74への返送汚泥量が制jailされる。Output L, J of limiter/A: Near i, :J is detected by J sludge pump 3, and the pump is not controlled, and the amount of return sludge to return sludge circuit "1i74" is controlled.
/7iり、余N′lj汚泥旦Y4算制す!41装置1゛
lで、この制御装置トイ17にはS V I iljり
定4.q li’j 10 (Q ll1l定出ブJ、
MLFJS計tからのMLBB値、姫入水流I)計73
からの流入水り返送汚泥rl′i度計7がらの汚泥i−
’% jf(値、逅送汚泥流H1旧/3からの汚泥流)
・支および余剰汚泥回路/gK設けられた余4i[11
汚泥v1シトtn1gからの余剰汚泥1辻がそれぞれ供
給され、これら各値全余剰汚泥演算制鐸装誼17で制御
し、その制御出力)fオンオフ回路iqケ介して余剰汚
泥ポンプlに供給してこれを制御する。ユOは最終沈殿
池コから流出される処理水の管路である。/7i, I'm N'lj sludge man Y4 calculation! 41 device 1, and this control device toy 17 has S V I ilj settings 4. q li'j 10 (Q ll1l constant output bu J,
MLBB value from MLFJS total t, Himeiri water flow I) total 73
Sludge returned from inflow water rl'i degree meter 7 sludge i-
'% jf (value, sludge flow from sludge flow H1 old/3)
・Support and excess sludge circuit/gK installed extra 4i [11
Excess sludge from sludge v1 and tn1g is supplied respectively, and each of these values is controlled by the total surplus sludge calculation system 17, and the control output is supplied to the surplus sludge pump l via the on/off circuit iq. Control this. UO is a pipe for treated water flowing out from the final settling tank.
次に」二記実施例の動作についてjlbべろ。まず。Next, let's talk about the operation of the second embodiment. first.
SV計10af用いて、第3図に示す汚泥沈降曲線をめ
、σ1り定開始からt分後の汚泥容量(5Vt)と、3
0分後の汚泥容量(Ov、。)をめる。直置g、’ (
Svt、 ) + (Sv+o )はSVI演詐M [
to bに入力され、この装@tabに入力されるML
SS計AのML13S値とで、SV工を測定する。SV
i測定装置庁10の出力は返送汚泥量演n、制御装置l
コに111給される。このとき、返送汚泥Mj=の制御
では前記svtが使用される。一般に(1)のf+et
tよ20分〜(10分程度である。ここで871.よ
シ汚泥返送率(l−)の目標値を次式により演↓1する
。Using the SV meter 10af, plot the sludge settling curve shown in Figure 3, and calculate the sludge volume (5Vt) after t minutes from the start of σ1 determination, and 3
Measure the sludge volume (Ov, .) after 0 minutes. Directly placed g,' (
Svt, ) + (Sv+o) is SVI fraud M [
ML that is input to to b and input to this device @tab
Measure the SV work with the ML13S value of SS meter A. S.V.
i The output of the measuring device 10 is the return sludge amount calculation n, and the control device l
111 will be paid to Ko. At this time, the above svt is used to control the return sludge Mj=. In general, f+et in (1)
t 20 minutes to (approximately 10 minutes.) Here, the target value of the 871. sludge return rate (l-) is calculated by the following formula.
rコに、 −r′+ k 、・・・・・・・・・・・・
(2)但し、r H汚泥返送率、r′=中間汚泥返送率
、SVl; : E公債の汚泥MM、k1+kll:人
力定数前記(1)式、(2)式に汚泥返送率(r)を演
rfシた後、次に1時間に1回線度p 、rp、される
返送率(rlの合i1”(s ty Xq ) 、回路
(toおよび゛す゛ングリング時間(wT )から、返
送率(r)の移動平均を演算し、その移動平均値(旬か
らトリえは(3)式に基づいて返送率を決定する。この
決定により返送員をイ(Iて(4)式によって返送汚泥
量rIrIIを行う。r, −r′+ k,・・・・・・・・・・・・
(2) However, r H sludge return rate, r'=intermediate sludge return rate, SVl; : E bond sludge MM, k1+kll: human power constant Substitute the sludge return rate (r) into equations (1) and (2) above. After the rf operation, the return rate (rl sum i1''(s ty Calculate the moving average of (r), and determine the return rate based on the moving average value (from season to season) based on equation (3). Perform the amount rIrII.
但しs rj?l’l @ r瘤 ・・・・・・返送率
上下限値但し、QR艙、 QRゆ・・・・・・返送汚泥
量の上下限値実際の制御においては、前記移動平均は、
例えば24時間移動平均値(′F)などが用いられる。However, srj? l'l @ r lump... Upper and lower limits of the return rate However, QR tank, QR Yu... Upper and lower limits of the amount of returned sludge In actual control, the above moving average is
For example, a 24-hour moving average value ('F) is used.
この返送率(r)の目標値は次の移動平均値が演算され
るまでホールドされる。返送率目やill値が頻繁に変
動しないように前記(3)式のような不感帯をとる場合
もある。前記返送率目標値と流入水量より、目標返送汚
泥量を得て、仁の値となるように返送汚泥ポンプ3の回
転数または制御弁(図示省略)に調節する。実際の返送
汚泥量は前記(4)式によりリミッタ/乙によってその
上−[限値が決定される。This target value of the return rate (r) is held until the next moving average value is calculated. In order to prevent frequent fluctuations in the return rate or the ill value, a dead zone as shown in equation (3) above may be provided. A target return sludge amount is obtained from the return rate target value and the inflow water amount, and the rotation speed of the return sludge pump 3 or a control valve (not shown) is adjusted so as to reach the desired value. The actual amount of returned sludge is determined by the limiter/B according to the above equation (4).
第41eま上述した返送汚泥量演算制御装置12のフロ
ーチャートで、図中、TはOVもの時間、Nは演算回数
、S U M t;J:ailb TS角Tは移動平均
時間でろるつ
次は余剰汚泥T^演算制御について述べる。壕ず。No. 41e is a flowchart of the above-mentioned return sludge amount calculation control device 12. In the figure, T is OV time, N is the number of calculations, SUM t;J:ailb TS angle T is the moving average time, and The surplus sludge T^ calculation control will be described. Trench.
8V工演算装置lObによりSVl値を一定時間間隔で
読み込む。゛ま之、流入水量(Qs)と返送汚泥量(籟
)よシ返送* (r)を次式によって演算する。The SVl value is read at regular time intervals by the 8V engineering calculation device lOb. However, the return * (r) is calculated based on the inflow water volume (Qs) and the return sludge volume (litter) using the following formula.
その後、第5図に示す汚泥分配係数によって分配比(k
lfi−決定するか、#l) 5図の曲数tl−数式化
した(6)式によって(k)を決定する。After that, the distribution ratio (k
lfi - Determine, #l) Number of songs tl in Figure 5 - Determine (k) using formula (6).
k= t (SVI 、 r )−・−−−−・・−(
a)ここで第5図について簡単に」ボベる。、’65図
はSVIが変化したときによるエアレーションタンク内
汚泥曖(MA)に対する最終沈殿池汚泥片(MP)の重
量比(MF/MA )と汚泥返送率(r)の関係を示す
特性図である。このrl! 5図は、SVIが増大する
に従って汚泥返送率(r)に対する増加率(傾き)が大
きくなシ、8Viが上列した場合は汚泥の返送率を増加
して沈殿池におりる汚泥の滞留時間を短縮しなければな
らないことを示したものである。k= t (SVI, r)−・−−−−・・−(
a) Let us now briefly discuss Figure 5. Figure '65 is a characteristic diagram showing the relationship between the weight ratio of final sedimentation tank sludge pieces (MP) to sludge mass (MA) in the aeration tank (MF/MA) and sludge return rate (r) as SVI changes. be. This rl! Figure 5 shows that as SVI increases, the increase rate (slope) for the sludge return rate (r) increases, and when 8Vi rises, the sludge return rate increases and the residence time of sludge in the settling tank increases. This indicates that the term must be shortened.
分配比(k)t−決定した後、エアレーションタンク/
内に設置されたMLSSilAの出力により次式を用い
てエアレーションタンク内汚泥@(Mh)を演n二する
。After determining the distribution ratio (k) t-, the aeration tank/
The sludge in the aeration tank (Mh) is calculated using the following equation based on the output of MLSSilA installed in the aeration tank.
MA−ML8S・Vt、・・・・旧・・・・・(7)但
シ、vA・・・・・・エアレーションタンク容積この(
7)式によ請求めたMAと前記分配比(klから次式を
用いて最終it殿池内汚泥貝(MF)を演算する。MA-ML8S・Vt,... Old... (7) However, vA... Aeration tank volume (
7) Calculate the final sludge shell (MF) in the IT basin from the MA calculated by the formula and the distribution ratio (kl) using the following formula.
MF=に−MA ・・・・・・・・・・・・(8)この
(8)式にめた)4 Fと前i!(3M Aとの和金次
式よ請求めて処理系内汚泥h’r (ioを算出する。MF=ni-MA ・・・・・・・・・・・・(8) Filled in this equation (8)) 4 F and previous i! (Calculate the sludge h'r (io) in the treatment system using the following equation with 3M A.
M=MA十MF ・・・・・・・・・・・・(9)この
(9)式によりjりめたλイの値は流入水;寸変動など
の外乱ICよって久動が生じるので移動平均値0旬AN
)が一般に使用される。この平均値CM (1) )は
合i1を演算回数(N)で除r゛r したもので、この
平均値(TJXi) )は予め設定した引抜き時刻にな
ったとき、次の0.1式によシ、引抜き目標汚泥Jij
(M W ) 2演1′g6する。M = MA + MF ・・・・・・・・・・・・(9) The value of λi calculated by this equation (9) is the inflow water; Moving average value 0 seasonal AN
) are commonly used. This average value CM (1)) is obtained by dividing the sum i1 by the number of calculations (N), and this average value (TJXi)) is calculated using the following 0.1 formula when the preset extraction time comes Good, target sludge for extraction
(M W ) 2 performances 1'g6.
蒼(1)
MW−□ ・・・・・・・・・・・・(tQn −SE
T
但し、1は引抜開始時刻、nは引抜き回数、SRT社平
均汚泥滞留時間である。Blue (1) MW-□ ・・・・・・・・・・・・(tQn-SE
T However, 1 is the drawing start time, n is the number of drawings, and SRT's average sludge retention time.
上記Q□式によ請求められたMWの値によシ余11汚泥
制御を行う。この制御においては、引抜き開始時刻で余
剰汚泥ボンプルl起動し、余剰汚泥鼠(Qw)と引抜き
汚泥濃度(通常返送汚泥濃度を用いる)より引抜き汚泥
量をめる。この後、この値を積算し、引抜き目標汚泥量
(MW)と等しいか大きくなつ几時点でポンプ金停止さ
せる。このポンプ停止は次式が成立したときに行われる
。The remaining 11 sludge control is performed according to the MW value requested by the above Q□ formula. In this control, the surplus sludge pump l is activated at the withdrawal start time, and the amount of withdrawn sludge is calculated from the surplus sludge (Qw) and the concentration of the withdrawn sludge (normally, the return sludge concentration is used). Thereafter, this value is integrated, and the pump is stopped when the amount becomes equal to or larger than the target sludge amount (MW) to be drawn. This pump stop is performed when the following equation holds.
M W(1)≦ΣQwxOR・・・・・・・・−・・・
OI)但し、Qwは余剰汚泥量%軸は返送汚泥濃度であ
る。M W (1)≦ΣQwxOR・・・・・・・・・−・
OI) However, Qw is the excess sludge amount % axis is the return sludge concentration.
なお、ポンプ弘はT −Ts、T(i)で、オン、オフ
は(11)式の成立でオフさせる。Note that the pump pressure is T - Ts, T(i), and is turned off when the equation (11) is established.
第6図は上述した余剰汚泥量演算制御装置のフローチャ
ートで、図中T、N、5ulvlij第4図と同じ意味
である。上記のように1〜て余ヤj汚泥鼠の演算制御が
行われるが、そのときの移動平均時間間隔は24時間(
1目)や余剰汚泥引抜き間隔等が用いられる。1(1え
#J: l )J n回、等時間間隔で引抜く場合(j
l、引抜き回数(n)によって61記移動平均時間は第
7図に示すようKなる。この第7図を用いてポンプψの
起動停止についてさらに述べるに。FIG. 6 is a flowchart of the above-mentioned surplus sludge amount calculation and control device, and T, N, and 5ulvlij in the figure have the same meaning as FIG. 4. As mentioned above, calculation control of the remaining sludge is performed from 1 to 1, but the moving average time interval at that time is 24 hours (
1), excess sludge removal interval, etc. 1 (1e #J: l ) J When pulling out n times at equal time intervals (j
1, and the number of times of extraction (n), the 61st moving average time becomes K as shown in FIG. Using this Fig. 7, we will further discuss starting and stopping the pump ψ.
余剰汚泥引抜き開始時L1]になるき、処理系内汚泥i
〔1t1)〕が決定されs (t’)式により1回目の
引抜き汚泥Jl (M wU )が演1?、されて余剰
汚泥ポンプlが起動される。そしで、00式により積n
、される実際の引抜き汚泥量が目標値MW(1)と等し
くなるかまたは大きくなったときポンプ弘を停止させる
。At the start of excess sludge extraction, the sludge i in the treatment system becomes L1].
[1t1)] is determined, and the first drawn sludge Jl (M wU ) is determined by equation s (t'). , and the excess sludge pump l is started. Then, by formula 00, the product n
When the actual amount of sludge drawn becomes equal to or larger than the target value MW(1), the pump is stopped.
以上述べたように、この発明によれば、次のような効果
が得られる。As described above, according to the present invention, the following effects can be obtained.
(1) 活性汚泥の沈降特性の変化(SV工の変化)に
伴うエアレーションタンク内汚泥量と最終沈殿池内汚泥
負の変化を測定することができる。(1) It is possible to measure the negative changes in the amount of sludge in the aeration tank and the sludge in the final settling tank due to changes in the settling characteristics of activated sludge (changes in SV work).
(2) 余剰汚泥量演算制御装置Nに返送重金パラメー
タとして組込んでいるので、返送汚泥濃度tlluと余
剰汚泥制御との相互干渉が生じない。(2) Since it is incorporated into the surplus sludge amount calculation control device N as a return heavy metal parameter, mutual interference between the return sludge concentration tllu and surplus sludge control does not occur.
(3) 系内汚泥量(エアレーションタンク内汚泥阪と
最終沈殿池内汚泥量金力+In、したfit)全制御対
象としているので、SV工や返送率の変動の影響金堂け
ない。(3) Since the total amount of sludge in the system (the amount of sludge in the aeration tank and the amount of sludge in the final settling tank + In) is subject to control, the influence of fluctuations in the SV process and return rate cannot be ignored.
(4) 従来の汚泥日令制御ではバルキング時(SV工
が200以上の時)汚泥日令が設定値よルも長くなシ、
最終沈殿池から汚泥が越流しやすくなるが、この発明の
制御ではパルギング時でも汚泥滞留時間(BRT)は変
化しない次め、上記のような問題は生じない。(4) With conventional sludge daily control, the sludge daily age during bulking (when SV work is 200 or more) is longer than the set value.
Sludge tends to overflow from the final settling tank, but with the control of the present invention, the sludge retention time (BRT) does not change even during pulging, so the above problem does not occur.
(5) 以」二のことから、lう01)、COD、窒素
、 fiの除去*全向上させることができる。(5) From the above, it is possible to completely improve the removal of COD, nitrogen, and fi.
第1図は従来の汚泥H全制御方式を示す楢成図、第2図
はこの発ツJの一実施例を示すm成図、第3図はSV計
による沈降曲線図、第4図は返送汚泥制御の動作を述べ
るためのフローチャート、第5図は汚泥分配比(1t)
’に決定rるための特性図、弔(1図は余剰汚泥側r
a1+の動作を述べる定めの70−ブーヤート、第7図
tel、汚泥引抜き回数と移動平均時間を述べる説明1
Δである。
/・・・エアレーションタンク、コ・・・最終沈殿池、
3・・・返送汚泥ポンプ、V・・・金利汚泥ポンプ、6
・・・M L S B計、F・・・余剰汚泥回路6F%
IO・・・FIVI測定装@、 io a −・−s
v計、lOb・・・SvI演JT装置、/コ・・・返送
汚泥量演算制御装置、l、?・・・流入水喰バI’s”
・・・返送汚泥回路、/3・・・返送汚泥儂1.ψ計、
/7・・・余情1汚泥量演算制御装置、lざ・・・余剰
汚泥回路。Figure 1 is a diagram showing a conventional sludge H total control system, Figure 2 is a diagram showing an example of this HatsuJ, Figure 3 is a sedimentation curve diagram using an SV meter, and Figure 4 is a diagram showing an example of this method. A flowchart to describe the operation of return sludge control, Figure 5 shows the sludge distribution ratio (1 t)
Characteristic diagram for determining the
Detailed 70-booyat describing the operation of a1+, Figure 7 tel, Explanation 1 describing the number of times of sludge extraction and moving average time
It is Δ. /...Aeration tank, Co...Final sedimentation tank,
3...Return sludge pump, V...Interest rate sludge pump, 6
...MLSB meter, F...excess sludge circuit 6F%
IO...FIVI measurement device @, io a -・-s
v meter, lOb...SvI performance JT device, /co...return sludge amount calculation control device, l,? ... Inflow water eater I's"
... Return sludge circuit, /3 ... Return sludge circuit 1. ψmeter,
/7... Surplus 1 sludge amount calculation control device, lza... Excess sludge circuit.
Claims (1)
を計測開始から所定時間経過後の汚泥容量と混合浮遊胸
部n’−nlの語測値から演n1)111定する汚泥容
賞指標測定装乃□と、この装置からの測定値、前にエア
レーションタンクに流入する流入水成およびエアレーシ
ョンタンクに返送される返送汚泥Rが供給され、これf
:煎31.シて最終沈殿池からエアレーションタンクに
返送する汚泥量金制岬する返送汚泥量演算制御装置と、
前記測定装置からの一111定値、前記エアレーション
タンクに流入する流入水尺、前記混合浮遊物製電r11
のR1測値、返送汚泥風および最終沈殿池から引抜かれ
た余剰汚泥片が供給され、これら各位を演n、シて最終
沈殿池から引抜かれる余剰汚泥量を制御する余剰汚泥景
演Jv、制御装置とを備えたこと?:、 管CRとする
活性汚泥坂制御装置1j0(1) A sludge volume index measurement device that determines the sedimentation characteristics of activated sludge in the aeration tank from the sludge volume and the measured value of mixed suspended chest n'-nl after a predetermined time has elapsed from the start of measurement. , the measured value from this device, the inflow water flowing into the aeration tank and the return sludge R returned to the aeration tank are supplied, and this f
: Roast 31. A return sludge amount calculation control device that controls the amount of sludge returned from the final settling tank to the aeration tank;
1111 constant value from the measuring device, the inflow water measure flowing into the aeration tank, the mixed suspended matter power r11
The R1 measurement value, the return sludge air, and the surplus sludge pieces pulled out from the final settling tank are supplied, and each of these is operated to control the amount of surplus sludge pulled out from the final settling tank. Did you have equipment? :, Activated sludge slope control device 1j0 with pipe CR
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58137171A JPS6028889A (en) | 1983-07-27 | 1983-07-27 | Controlling device for activated sludge amount |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58137171A JPS6028889A (en) | 1983-07-27 | 1983-07-27 | Controlling device for activated sludge amount |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6028889A true JPS6028889A (en) | 1985-02-14 |
| JPH0513720B2 JPH0513720B2 (en) | 1993-02-23 |
Family
ID=15192474
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP58137171A Granted JPS6028889A (en) | 1983-07-27 | 1983-07-27 | Controlling device for activated sludge amount |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6028889A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS58141341A (en) * | 1982-02-12 | 1983-08-22 | Nippon Steel Corp | Preliminary treatment of ore containing limonite for sintering |
| JPH03193828A (en) * | 1989-12-22 | 1991-08-23 | Nippon Steel Corp | Production of sintering raw material and sintered ore |
| WO2000047525A1 (en) * | 1999-02-11 | 2000-08-17 | Zeolite Australia Limited | Process for the removal of suspended and other material from waste water |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS52104358A (en) * | 1976-02-27 | 1977-09-01 | Hitachi Ltd | Method for controlling activated sludge |
| JPS5845795A (en) * | 1981-09-14 | 1983-03-17 | Toshiba Corp | Sewage treatment control equipment |
-
1983
- 1983-07-27 JP JP58137171A patent/JPS6028889A/en active Granted
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS52104358A (en) * | 1976-02-27 | 1977-09-01 | Hitachi Ltd | Method for controlling activated sludge |
| JPS5845795A (en) * | 1981-09-14 | 1983-03-17 | Toshiba Corp | Sewage treatment control equipment |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS58141341A (en) * | 1982-02-12 | 1983-08-22 | Nippon Steel Corp | Preliminary treatment of ore containing limonite for sintering |
| JPH03193828A (en) * | 1989-12-22 | 1991-08-23 | Nippon Steel Corp | Production of sintering raw material and sintered ore |
| WO2000047525A1 (en) * | 1999-02-11 | 2000-08-17 | Zeolite Australia Limited | Process for the removal of suspended and other material from waste water |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0513720B2 (en) | 1993-02-23 |
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