JPH10249345A - Method and device for controlling filtered water quantity constant - Google Patents

Method and device for controlling filtered water quantity constant

Info

Publication number
JPH10249345A
JPH10249345A JP9055355A JP5535597A JPH10249345A JP H10249345 A JPH10249345 A JP H10249345A JP 9055355 A JP9055355 A JP 9055355A JP 5535597 A JP5535597 A JP 5535597A JP H10249345 A JPH10249345 A JP H10249345A
Authority
JP
Japan
Prior art keywords
water level
water
tank
filtered
level difference
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
JP9055355A
Other languages
Japanese (ja)
Inventor
Hajime Ito
肇 伊藤
Toshikazu Okumura
敏和 奥村
Kanji Tokushima
幹治 徳島
Koichi Okada
公一 岡田
Kazuyuki Honda
和之 本田
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.)
Kubota Corp
Original Assignee
Kubota 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 Kubota Corp filed Critical Kubota Corp
Priority to JP9055355A priority Critical patent/JPH10249345A/en
Publication of JPH10249345A publication Critical patent/JPH10249345A/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)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

PROBLEM TO BE SOLVED: To make it possible to be operated at a fixed amount regard lessly of the change of a membrane performance even by gravity filtering system. SOLUTION: In this method, the water level of a filtered water 9 in a treated water tank 4 is detected at a specified interval, and the variation in the water level between a nitrification tank 3 and a treated water tank 4 is enlarged or reduced by comparing a variation value ΔL' in a measured water level calculated from the detected water level with a previously set variation value ΔL in a standard water level, and actuating and stopping a water discharge pump 10 discharging the filtered water 9 in the treated water tank 4 based on the variation between both variation values.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、槽内に浸漬設置さ
れた膜分離装置における単位時間当たり濾過水量を一定
に制御する濾過水量一定制御方法およびその装置に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and apparatus for controlling the amount of filtrate per unit time in a membrane separation apparatus immersed and installed in a tank.

【0002】[0002]

【従来の技術】従来の浄化槽として、たとえば図3に示
したような、脱窒槽1と膜分離装置2を設置した硝化槽
3と処理水槽4とを備えた合併浄化槽がある。膜分離装
置2は、上下が開口したケース2a内に平板状膜エレメ
ント2bを膜面を上下方向として配列したものであり、
膜エレメント2bの下方に散気装置5が設置され、膜エ
レメント2bの濾過水流路に連通する濾過水導出管2c
は処理水槽4内で開口している。
2. Description of the Related Art As a conventional purification tank, there is, for example, a combined purification tank provided with a nitrification tank 3 provided with a denitrification tank 1, a membrane separation device 2, and a treatment water tank 4, as shown in FIG. The membrane separation device 2 is configured by arranging plate-shaped membrane elements 2b in a case 2a having an open top and bottom with the membrane surface in the up-down direction.
A diffuser 5 is provided below the membrane element 2b, and a filtered water outlet pipe 2c communicating with a filtered water flow path of the membrane element 2b.
Open in the treatment water tank 4.

【0003】このような浄化槽では、原水6を脱窒槽1
内に導入し、脱窒槽1内の活性汚泥混合液7の一部を硝
化槽3へ移送しつつ、硝化槽3内の活性汚泥混合液8を
脱窒槽1へ越流させている。そして、脱窒槽1内で嫌気
条件下に脱窒処理し、硝化槽3内で、散気装置5により
散気される好気条件下に硝化処理するとともに、槽内の
一定水位に維持された活性汚泥混合液8を膜エレメント
2bで濾過して、濾過水9を濾過水導出管2を通じて処
理水槽4内へ導出し、処理水槽9内の濾過水9を排水ポ
ンプ10により適宜排出している。
In such a septic tank, the raw water 6 is supplied to the denitrification tank 1
The activated sludge mixture 8 in the nitrification tank 3 is allowed to flow into the denitrification tank 1 while a part of the activated sludge mixture 7 in the denitrification tank 1 is transferred to the nitrification tank 3. Then, denitrification treatment was performed in the denitrification tank 1 under anaerobic conditions, and nitrification treatment was performed in the nitrification tank 3 under aerobic conditions where air was diffused by the diffuser 5, and the water level in the tank was maintained at a constant level. The activated sludge mixed liquid 8 is filtered by the membrane element 2b, and the filtered water 9 is led out into the treated water tank 4 through the filtered water outlet pipe 2, and the filtered water 9 in the treated water tank 9 is appropriately discharged by the drain pump 10. .

【0004】膜分離装置2の濾過方式としては、図2に
示したような、硝化槽3内の活性汚泥混合液8と処理水
槽9内の濾過水9との水位差Lを利用する重力濾過方式
と、図3に示したような、吸引ポンプ11により濾過水
導出管2を通じて膜エレメント2bの濾過水流路内に吸
引圧を作用させる吸引濾過方式とがある。
[0004] As a filtration method of the membrane separation device 2, as shown in FIG. 2, gravity filtration utilizing a water level difference L between the activated sludge mixed liquid 8 in the nitrification tank 3 and the filtered water 9 in the treatment water tank 9. As shown in FIG. 3, there is a suction filtration method in which a suction pressure is applied to the filtered water flow path of the membrane element 2b through the filtered water outlet pipe 2 by the suction pump 11, as shown in FIG.

【0005】[0005]

【発明が解決しようとする課題】ところで、上記したよ
うな膜分離装置2において一定流量の濾過水9を導出す
る安定した濾過運転を行うためには、図2に示した重力
濾過方式の場合、水位差Lを一定にすればよいが、運転
時間が経過するとともに膜に目詰まりが生じ、次第に濾
過水量が減少してくるという問題がある。一方、吸引濾
過方式の場合、図3に示したように濾過水導出管2cに
流量調整弁12を介装することで、膜性能の変化に関係
なく一定量の濾過水9を取り出せるが、流量調整弁12
が高価であるという問題がある。
By the way, in order to carry out a stable filtration operation for drawing out a constant flow rate of the filtered water 9 in the above-mentioned membrane separation device 2, in the case of the gravity filtration system shown in FIG. The water level difference L may be kept constant, but there is a problem that the membrane is clogged as the operation time elapses, and the amount of filtered water gradually decreases. On the other hand, in the case of the suction filtration method, a fixed amount of the filtered water 9 can be taken out regardless of the change in the membrane performance by interposing the flow control valve 12 in the filtered water outlet pipe 2c as shown in FIG. Regulating valve 12
However, there is a problem that it is expensive.

【0006】本発明は上記問題を解決するもので、重力
濾過方式としながら膜性能の変化に関係なく一定処理量
で運転できるようにすることを目的とするものである。
An object of the present invention is to solve the above-mentioned problem, and an object of the present invention is to make it possible to operate at a constant throughput regardless of a change in membrane performance while using a gravity filtration method.

【0007】[0007]

【課題を解決するための手段】上記問題を解決するため
に、本発明の濾過水量一定制御方法は、生物処理槽内の
活性汚泥混合液を槽内に浸漬設置した膜分離装置により
処理水槽との水位差に基づき重力濾過し、膜を透過して
濾過水導出管を通じて処理水槽内に流入した濾過水を、
所定の基準高水位と基準低水位とにおいて起動停止する
ポンプ手段により排出するに際し、前記ポンプ手段の駆
動時あるいは停止時に、処理水槽内の濾過水の水位を所
定時間をおいて検知し、検知した2水位間の水位差を算
出し、算出した水位差を基準水位差値ΔLとして設定
し、その後のポンプ手段の駆動時あるいは停止時に、処
理水槽内の濾過水の水位を所定時間をおいて検知し、検
知した2水位間の水位差を算出し、算出した水位差を測
定水位差値ΔL’となし、この測定水位差値ΔL’を前
記基準水位値差ΔLと比較し、測定水位差値ΔL’<基
準水位差値ΔLの時は、前記ポンプ手段を少なくとも前
記基準低水位より低い水位で停止させて、生物処理槽と
処理水槽との水位差を拡大し、測定水位差値ΔL’>基
準水位差値ΔLの時は、前記ポンプ手段を少なくとも前
記基準低水位より高い水位で停止させて、生物処理槽と
処理水槽との水位差を縮小し、それにより、膜分離装置
における単位時間当たり濾過水量を一定に制御するよう
にしたものである。
Means for Solving the Problems To solve the above problems, the method for controlling the amount of filtered water constant according to the present invention is characterized in that the activated sludge mixed liquid in the biological treatment tank is immersed and installed in the treatment water tank by a membrane separation device. Gravity filtration based on the water level difference of the filtered water that has passed through the membrane and flowed into the treated water tank through the filtered water outlet pipe,
Upon discharging by the pump means that starts and stops at the predetermined reference high water level and the reference low water level, when the pump means is driven or stopped, the water level of the filtered water in the treated water tank is detected after a predetermined time and detected. Calculate the water level difference between the two water levels, set the calculated water level difference as the reference water level difference value ΔL, and detect the water level of the filtered water in the treated water tank at a predetermined time when the pump means is driven or stopped thereafter. The calculated water level difference is calculated as a measured water level difference value ΔL ′, and the measured water level difference value ΔL ′ is compared with the reference water level value difference ΔL to obtain a measured water level difference value. When ΔL ′ <reference water level difference value ΔL, the pump means is stopped at least at a water level lower than the reference low water level, the water level difference between the biological treatment tank and the treatment water tank is enlarged, and the measured water level difference value ΔL ′> When the reference water level difference value ΔL is The pumping means is stopped at least at a water level higher than the reference low water level to reduce the water level difference between the biological treatment tank and the treatment water tank, whereby the amount of filtered water per unit time in the membrane separation device is controlled to be constant. Things.

【0008】また本発明の濾過水量一定制御装置は、膜
分離装置を浸漬設置した生物処理槽と、膜分離装置の膜
透過側に連通する濾過水導出管の終端部が槽内で開口し
た処理水槽と、処理水槽内の濾過水を所定の基準高水位
と基準低水位とにおいて起動停止しつつ排出するポンプ
手段とを備えた浄化槽に設けられて、膜分離装置におけ
る単位時間当たり濾過水量を一定に制御する濾過水量一
定制御装置であって、前記処理水槽内の濾過水の水位を
検知する水位検知手段と、前記ポンプ手段の起動停止を
制御する制御手段とを備え、この制御手段により、前記
水位検知手段によって検知された水位より算出される所
定時間当たり測定水位差値ΔL’と、予め設定した所定
時間当たり基準水位差値ΔLとの差に基づき、前記ポン
プ手段を少なくとも前記基準低水位とは異なる水位で停
止させて、生物処理槽と処理水槽との水位差を拡大ある
いは縮小し、膜分離装置における単位時間当たり濾過水
量を一定に制御するように構成したものである。
[0008] The apparatus for controlling a constant amount of filtered water according to the present invention comprises a biological treatment tank in which a membrane separation device is immersed and installed, and an end portion of a filtered water discharge pipe communicating with the membrane permeation side of the membrane separation device being opened in the tank. A water tank and a purifying tank provided with a pump means for starting and stopping the filtered water in the treated water tank at a predetermined reference high water level and a reference low water level and discharging the water therefrom, and the amount of filtered water per unit time in the membrane separation device is kept constant. A constant level control device for filtered water, comprising a water level detecting means for detecting the level of filtered water in the treated water tank, and a control means for controlling the start and stop of the pump means, the control means, Based on a difference between a measured water level difference value ΔL ′ per predetermined time calculated from the water level detected by the water level detection means and a preset reference water level difference value ΔL per predetermined time, the pump means is at least It is configured to stop at a water level different from the reference low water level, expand or reduce the water level difference between the biological treatment tank and the treatment water tank, and control the amount of filtered water per unit time in the membrane separation device to be constant. .

【0009】一般に、処理水槽の横断面積が槽上下方向
のいずれの位置でも一定であるという条件下では、濾過
水量は水位変化に比例するので、測定した所定時間当た
り水位上昇(水位差)を、基準とする所定時間当たり水
位差に比較することで、所定時間当たりの濾過水量が基
準濾過水量より小さいか大きいかを判定できる。
Generally, under the condition that the cross-sectional area of the treated water tank is constant at any position in the vertical direction of the tank, the amount of filtered water is proportional to the change in the water level. By comparing the difference in water level per predetermined time as a reference, it can be determined whether the amount of filtered water per predetermined time is smaller or larger than the reference filtered water amount.

【0010】したがって、その判定結果に基づき、ポン
プ手段を少なくとも基準低水位より低い(あるいは高
い)水位で停止させて、生物処理槽と処理水槽との水位
差を拡大(あるいは縮小)させることにより、所定時間
当たりの濾過水量を基準濾過水量に近付けることがで
き、膜分離装置における単位時間当たり濾過水量を一定
に制御できる。
[0010] Therefore, based on the determination result, the pump means is stopped at least at a water level lower (or higher) than the reference low water level to enlarge (or reduce) the water level difference between the biological treatment tank and the treatment water tank. The amount of filtered water per predetermined time can be made closer to the reference amount of filtered water, and the amount of filtered water per unit time in the membrane separation device can be controlled to be constant.

【0011】[0011]

【発明の実施の形態】以下、本発明の実施の形態を図面
を参照しながら説明する。本発明の濾過水量一定制御装
置は、図2を用いて説明した従来の浄化槽に適用可能な
ので、図1に、従来と同様の構成を有する浄化槽を示
し、図2と同じ符号を付して説明する。
Embodiments of the present invention will be described below with reference to the drawings. Since the filtered water amount constant control device of the present invention can be applied to the conventional septic tank described with reference to FIG. 2, FIG. 1 shows a septic tank having the same configuration as that of the conventional septic tank. I do.

【0012】浄化槽は、脱窒槽1と膜分離装置2を浸漬
設置した硝化槽3と処理水槽4とを備えている。膜分離
装置2は、上下が開口したケース2a内に膜エレメント
2bを膜面を上下方向として配列したものであって、膜
エレメント2bの濾過水流路に連通する濾過水導出管2
cは処理水槽4内で開口しており、槽内の活性汚泥混合
液8が処理水槽4内の濾過水9との水位差に基づき膜エ
レメント2bで重力濾過されるようになっている。槽内
に空気を供給する散気装置5は膜エレメント2bの下方
に設置されている。
The purification tank has a nitrification tank 3 in which a denitrification tank 1 and a membrane separation device 2 are immersed and installed, and a treated water tank 4. The membrane separation device 2 is configured by arranging membrane elements 2b with a membrane surface in a vertical direction in a case 2a that is open at the top and bottom.
c is open in the treatment water tank 4 so that the activated sludge mixed liquid 8 in the tank is gravity-filtered by the membrane element 2b based on the water level difference with the filtered water 9 in the treatment water tank 4. An air diffuser 5 for supplying air into the tank is provided below the membrane element 2b.

【0013】処理水槽4には、膜エレメント2bより濾
過水導出管2cを通じて槽内に流入した濾過水9を、所
定の基準高水位HLと基準低水位LLとにおいて起動停
止しつつ排出する排水ポンプ10が設けられている。ま
た、槽内の濾過水9の水位を検知する水位計12と、排
水ポンプ10の起動停止を制御する制御装置13とが設
けられている。制御装置13は、水位計12と排水ポン
プ10とに電気的に接続しており、図示を省略した計時
手段と演算手段と記憶手段とを備えている。
The treated water tank 4 is a drain pump for discharging the filtered water 9 flowing into the tank from the membrane element 2b through the filtered water outlet pipe 2c while starting and stopping at a predetermined reference high water level HL and a reference low water level LL. 10 are provided. Further, a water level meter 12 for detecting the level of the filtered water 9 in the tank and a control device 13 for controlling the start and stop of the drainage pump 10 are provided. The control device 13 is electrically connected to the water level gauge 12 and the drain pump 10, and includes a timing unit, a calculation unit, and a storage unit (not shown).

【0014】上記したような浄化槽において、図2を用
いて説明した従来の浄化槽と同様に、原水を脱窒槽1内
に導入し、脱窒槽1内の活性汚泥混合液7の一部を硝化
槽3へ移送し、硝化槽3内の活性汚泥混合液8を脱窒槽
1へ越流させる状態において、脱窒槽1内で嫌気条件下
に脱窒処理し、硝化槽3内で散気装置5により散気され
る好気条件下に硝化処理する。
In the above-mentioned septic tank, raw water is introduced into the denitrification tank 1 and a part of the activated sludge mixed solution 7 in the denitrification tank 1 is converted into a nitrification tank in the same manner as in the conventional septic tank described with reference to FIG. In the state where the activated sludge mixture liquid 8 in the nitrification tank 3 is allowed to flow to the denitrification tank 1, denitrification treatment is performed in the denitrification tank 1 under anaerobic conditions, Nitrification treatment is carried out under aerobic conditions in which air is diffused.

【0015】また、上記したようなフローによって一定
水位に維持された硝化槽3内の活性汚泥混合液8を膜エ
レメント2bで重力濾過し、膜面を透過した濾過水9を
濾過水導出管2cを通じて処理水槽4内へ導出する。処
理水槽9内の濾過水9は、排水ポンプ10により間欠的
に排出して基準低水位LLと基準高水位HLとの間に維
持する。
Further, the activated sludge mixed liquid 8 in the nitrification tank 3 maintained at a constant water level by the flow described above is gravity-filtered by the membrane element 2b, and the filtered water 9 that has passed through the membrane surface is filtered out by the filtered water outlet pipe 2c. Through the treatment water tank 4. The filtered water 9 in the treated water tank 9 is intermittently discharged by the drain pump 10 and is maintained between the reference low water level LL and the reference high water level HL.

【0016】このとき、膜分離装置2における濾過水量
を一定に制御するために、次のような操作を行う。排水
ポンプ10の停止時に、水位計12によって処理水槽4
内の濾過水9の水位L0 を検知し、計時手段により計測
される所定時間後に、水位計12によって処理水槽4内
の濾過水9の水位L1 を検知し、検知した2水位L0
1 間の水位差を演算手段により算出し、算出した水位
差を基準水位差値ΔLとして記憶手段に記憶させる。
At this time, the following operation is performed to control the amount of filtered water in the membrane separation device 2 to be constant. When the drain pump 10 is stopped, the water tank 4
Detecting the water level L 0 of the filtered water 9 of the inner, after a predetermined time measured by the time measuring means detects the water level L 1 of the filtered water 9 in the treatment water tank 4 by the water level gauge 12, was detected 2 water level L 0,
The level difference between L 1 calculated by the arithmetic means, and stores the calculated level difference in the storage means as a reference level difference value [Delta] L.

【0017】適当時間後の排水ポンプ10の停止時に、
同様にして、水位計12と計時手段とにより所定時間を
おいて処理水槽4内の濾過水9の水位L0',L1'を検知
し、検知した2水位L0',L1'間の水位差を演算手段に
より算出し、算出した水位差を測定水位差値ΔL’とし
て記憶手段に記憶させる。
When the drain pump 10 is stopped after an appropriate time,
Similarly, water gauge 12 and the time measuring means and the water level L 0 of the filtered water 9 in the treatment water tank 4 at a predetermined time ', L 1' senses, 2 water level L 0 is detected ', L 1' between Is calculated by the calculating means, and the calculated water level difference is stored in the storage means as the measured water level difference value ΔL '.

【0018】次に、制御装置13において、測定水位差
値ΔL’を基準水位差値ΔLと比較する。そして、測定
水位差値ΔL’<基準水位差値ΔLの時は、制御装置1
3により、排水ポンプ10の駆動時間(または駆動力)
を増大して、処理水槽4内の水位を基準低水位より一定
水位だけ低いLL’まで低下させ、その後は排水ポンプ
10を通常通り駆動することにより、処理水槽9内を低
水位LL’と高水位HL’との間に維持し、硝化槽3と
処理水槽4との水位差をそれまでより拡大する。
Next, the control unit 13 compares the measured water level difference value ΔL ′ with the reference water level difference value ΔL. When the measured water level difference value ΔL ′ <the reference water level difference value ΔL, the controller 1
3, the driving time (or driving force) of the drainage pump 10
To lower the water level in the treated water tank 4 to LL ', which is lower than the reference low water level by a fixed water level, and then drive the drainage pump 10 as usual, so that the inside of the treated water tank 9 has a low water level LL'. The water level is maintained between the water level HL ′ and the water level difference between the nitrification tank 3 and the treatment water tank 4 is further increased.

【0019】測定水位差値ΔL’>基準水位差値ΔLの
時は、制御装置13により、排水ポンプ10の駆動時間
(または駆動力)を低減して、処理水槽4内の水位を基
準低水位より一定水位だけ高い水位まで上昇させること
により(図示せず)、硝化槽3と処理水槽4との水位差
をそれまでより縮小する。
When the measured water level difference value ΔL ′> the reference water level difference value ΔL, the control unit 13 reduces the driving time (or driving force) of the drain pump 10 to reduce the water level in the treated water tank 4 to the reference low water level. By raising the water level to a higher level by a certain level (not shown), the water level difference between the nitrification tank 3 and the treated water tank 4 is further reduced.

【0020】上記したような操作を繰り返すことによ
り、膜の目詰まりなどの膜性能の変化に関係なく単位時
間当たり濾過水量を一定に制御できる。逆に、原水の流
入量変動や水質変動に合わせて、濾過水量を大きくした
り、小さくしたりする運転も可能である。
By repeating the above-described operation, the amount of filtered water per unit time can be controlled to be constant regardless of a change in membrane performance such as membrane clogging. Conversely, it is also possible to increase or decrease the amount of filtered water in accordance with fluctuations in the inflow of raw water or fluctuations in water quality.

【0021】上記した実施形態では、測定水位差値Δ
L’と基準水位差値ΔLとの大小によって、排水ポンプ
10を停止させる水位を一定水位ずつ低下(あるいは上
昇)させるようにしたが、測定水位差値ΔL’と基準水
位差値ΔLとの差a0,a1,a2・・に対応する水位
低下幅b0,b1,b2・・を予め設定しておき、差a
0,a1,a2・・に応じて、水位低下幅b0,b1,
b2・・を選択するようにしてもよい。
In the above embodiment, the measured water level difference value Δ
The water level at which the drain pump 10 is stopped is lowered (or raised) by a fixed water level depending on the magnitude of L ′ and the reference water level difference ΔL, but the difference between the measured water level difference ΔL ′ and the reference water level difference ΔL is set. The water level drop widths b0, b1, b2,... corresponding to a0, a1, a2,.
0, a1, a2..., The water level drop width b0, b1,
b2... may be selected.

【0022】また上記した実施形態では、排水ポンプ1
0の停止時に、処理水槽4内の濾過水9の水位を検知し
たが、排水ポンプ10を一定駆動する状態において、処
理水槽4内の濾過水9の水位を検知するようにしてもよ
い。
In the above embodiment, the drain pump 1
Although the water level of the filtered water 9 in the treated water tank 4 is detected at the stop of 0, the water level of the filtered water 9 in the treated water tank 4 may be detected in a state where the drainage pump 10 is driven at a constant speed.

【0023】水位計12に代えて、液圧力計、レーザー
水位計などの水位検知手段を使用してもよい。水位計1
2に警報装置(図示せず)を接続して、水位計12によ
り検知された水位が膜分離装置2で重力濾過するに適当
な範囲を越えた場合、たとえば膜分離装置2が露出する
水位まで低下した時に警報表示させるようにしてもよ
い。
In place of the water level gauge 12, a water level detecting means such as a liquid pressure gauge or a laser water level gauge may be used. Water level meter 1
2 is connected to an alarm device (not shown), and when the water level detected by the water level gauge 12 exceeds a range suitable for gravity filtration in the membrane separation device 2, for example, up to a water level at which the membrane separation device 2 is exposed. An alarm may be displayed when the temperature decreases.

【0024】[0024]

【発明の効果】以上のように本発明によれば、処理水槽
内の濾過水の水位を所定時間をおいて検知し、検知した
2水位より算出される測定水位差値ΔL’を、予め設定
した基準水位差値ΔLと比較し、両者の差に基づき、処
理水槽内の濾過水を排出するポンプ手段を起動停止する
水位を変更して、生物処理槽と処理水槽との水位差を拡
大あるいは縮小するようにしたので、重力濾過方式であ
りながら膜性能の変化に関係なく一定処理運転が可能で
ある。逆に、原水の流入量変動や水質変動に合わせて、
濾過水量を大きくしたり、小さくしたりする運転も可能
である。
As described above, according to the present invention, the water level of the filtered water in the treated water tank is detected after a predetermined time, and the measured water level difference value ΔL ′ calculated from the two detected water levels is set in advance. Compared with the reference water level difference value ΔL, and based on the difference between them, the water level at which the pump means for discharging the filtered water in the treated water tank is started and stopped is changed to increase the water level difference between the biological treatment tank and the treated water tank. Since the size is reduced, a constant processing operation can be performed irrespective of a change in the membrane performance even though the gravity filtration method is used. Conversely, in response to fluctuations in raw water inflow and water quality,
It is also possible to increase or decrease the amount of filtered water.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の一実施形態における濾過水量一定制御
装置を備えた浄化槽の要部縦断面図である。
FIG. 1 is a longitudinal sectional view of a main part of a septic tank provided with a filtered water amount constant control device according to an embodiment of the present invention.

【図2】従来の浄化槽であって、槽内に重力濾過方式の
膜分離装置を設置したものを示した縦断面図である。
FIG. 2 is a longitudinal sectional view showing a conventional septic tank in which a gravity filtration type membrane separation device is installed in the tank.

【図3】従来の浄化槽であって、槽内に吸引濾過方式の
膜分離装置を設置したものを示した要部縦断面図であ
る。
FIG. 3 is a longitudinal sectional view of a main part of a conventional septic tank in which a suction filtration type membrane separation device is installed in the tank.

【符号の説明】[Explanation of symbols]

2 膜分離装置 2c 濾過水導出管 3 硝化槽 4 処理水槽 8 活性汚泥混合液 9 濾過水 10 排水ポンプ 12 水位計 13 制御装置 HL 基準高水位 LL 基準低水位 L0,L1 水位 ΔL 基準水位差値 L0',L1' 水位 ΔL’ 測定水位差値 HL’ 高水位 LL’ 低水位2 Membrane separation device 2c Filtration water outlet pipe 3 Nitrification tank 4 Treatment water tank 8 Activated sludge mixture 9 Filtration water 10 Drain pump 12 Water level gauge 13 Controller HL Standard high water level LL Standard low water level L 0 , L 1 Water level ΔL Standard water level difference Value L 0 ', L 1 ' Water level ΔL 'Measured water level difference value HL' High water level LL 'Low water level

───────────────────────────────────────────────────── フロントページの続き (72)発明者 岡田 公一 兵庫県尼崎市浜一丁目1番1号 株式会社 クボタ技術開発研究所内 (72)発明者 本田 和之 滋賀県甲賀郡甲西町高松2番地の1 株式 会社クボタ滋賀工場内 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Koichi Okada 1-1-1, Hama, Amagasaki-shi, Hyogo Inside Kubota Research and Development Laboratory Co., Ltd. (72) Inventor Kazuyuki Honda 2 Takamatsu, Kosai-cho, Koga-gun, Shiga Prefecture 1 Kubota Shiga Plant

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 生物処理槽内の活性汚泥混合液を槽内に
浸漬設置した膜分離装置により処理水槽との水位差に基
づき重力濾過し、膜を透過して濾過水導出管を通じて処
理水槽内に流入した濾過水を、所定の基準高水位と基準
低水位とにおいて起動停止するポンプ手段により排出す
るに際し、前記ポンプ手段の駆動時あるいは停止時に、
処理水槽内の濾過水の水位を所定時間をおいて検知し、
検知した2水位間の水位差を算出し、算出した水位差を
基準水位差値ΔLとして設定し、その後のポンプ手段の
駆動時あるいは停止時に、処理水槽内の濾過水の水位を
所定時間をおいて検知し、検知した2水位間の水位差を
算出し、算出した水位差を測定水位差値ΔL’となし、
この測定水位差値ΔL’を前記基準水位値差ΔLと比較
し、測定水位差値ΔL’<基準水位差値ΔLの時は、前
記ポンプ手段を少なくとも前記基準低水位より低い水位
で停止させて、生物処理槽と処理水槽との水位差を拡大
し、測定水位差値ΔL’>基準水位差値ΔLの時は、前
記ポンプ手段を少なくとも前記基準低水位より高い水位
で停止させて、生物処理槽と処理水槽との水位差を縮小
し、それにより、膜分離装置における単位時間当たり濾
過水量を一定に制御することを特徴とする濾過水量一定
制御方法。
1. The activated sludge mixed liquid in the biological treatment tank is gravity-filtered by a membrane separation device immersed and installed in the tank based on a difference in water level with the treatment water tank, passes through the membrane, and passes through the filtered water discharge pipe into the treatment water tank. When the filtered water that has flowed in is discharged by the pump means that starts and stops at the predetermined reference high water level and the reference low water level, when the pump means is driven or stopped,
Detects the level of filtered water in the treated water tank after a predetermined time,
The detected water level difference between the two water levels is calculated, the calculated water level difference is set as a reference water level difference value ΔL, and when the pump means is driven or stopped thereafter, the level of the filtered water in the treated water tank is kept for a predetermined time. Calculating a water level difference between the two detected water levels, and determining the calculated water level difference as a measured water level difference value ΔL ′,
The measured water level difference ΔL ′ is compared with the reference water level difference ΔL, and when the measured water level difference ΔL ′ <the reference water level difference ΔL, the pump means is stopped at least at a water level lower than the reference low water level. The water level difference between the biological treatment tank and the treated water tank is enlarged, and when the measured water level difference value ΔL ′> the reference water level difference value ΔL, the pump means is stopped at least at a water level higher than the reference low water level to perform biological treatment. A method for controlling a constant amount of filtered water, characterized in that the difference in water level between a tank and a treated water tank is reduced, thereby controlling the amount of filtered water per unit time in a membrane separation device to be constant.
【請求項2】 膜分離装置を浸漬設置した生物処理槽
と、膜分離装置の膜透過側に連通する濾過水導出管の終
端部が槽内で開口した処理水槽と、処理水槽内の濾過水
を所定の基準高水位と基準低水位とにおいて起動停止し
つつ排出するポンプ手段とを備えた浄化槽に設けられ
て、膜分離装置における単位時間当たり濾過水量を一定
に制御する濾過水量一定制御装置であって、前記処理水
槽内の濾過水の水位を検知する水位検知手段と、前記ポ
ンプ手段の起動停止を制御する制御手段とを備え、この
制御手段により、前記水位検知手段によって検知された
水位より算出される所定時間当たり測定水位差値ΔL’
と、予め設定した所定時間当たり基準水位差値ΔLとの
差に基づき、前記ポンプ手段を少なくとも前記基準低水
位とは異なる水位で停止させて、生物処理槽と処理水槽
との水位差を拡大あるいは縮小し、膜分離装置における
単位時間当たり濾過水量を一定に制御するように構成し
たことを特徴とする濾過水量一定制御装置。
2. A biological treatment tank in which a membrane separation device is immersed and installed, a treatment water tank in which the end of a filtered water outlet pipe communicating with the membrane permeation side of the membrane separation device is open in the tank, and a filtered water in the treatment water tank. Is provided in a purification tank provided with a pump means for discharging while starting and stopping at a predetermined reference high water level and a reference low water level, and a constant filtration water amount control device for controlling a constant amount of filtration water per unit time in the membrane separation device. There is provided a water level detecting means for detecting a water level of the filtered water in the treated water tank, and a control means for controlling start and stop of the pump means, and the control means detects a water level detected by the water level detecting means. Calculated measured water level difference value ΔL 'per predetermined time
And, based on the difference between the preset reference water level difference value ΔL per predetermined time, the pump means is stopped at least at a water level different from the reference low water level to increase the water level difference between the biological treatment tank and the treatment water tank. An apparatus for controlling the amount of filtered water constant, wherein the apparatus is reduced so as to control the amount of filtered water per unit time in the membrane separation device to be constant.
JP9055355A 1997-03-11 1997-03-11 Method and device for controlling filtered water quantity constant Pending JPH10249345A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9055355A JPH10249345A (en) 1997-03-11 1997-03-11 Method and device for controlling filtered water quantity constant

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9055355A JPH10249345A (en) 1997-03-11 1997-03-11 Method and device for controlling filtered water quantity constant

Publications (1)

Publication Number Publication Date
JPH10249345A true JPH10249345A (en) 1998-09-22

Family

ID=12996202

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9055355A Pending JPH10249345A (en) 1997-03-11 1997-03-11 Method and device for controlling filtered water quantity constant

Country Status (1)

Country Link
JP (1) JPH10249345A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002066535A (en) * 2000-09-01 2002-03-05 Togami Electric Mfg Co Ltd Waste water system
JP2018065120A (en) * 2016-10-21 2018-04-26 株式会社日立製作所 Water treatment apparatus and its method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002066535A (en) * 2000-09-01 2002-03-05 Togami Electric Mfg Co Ltd Waste water system
JP2018065120A (en) * 2016-10-21 2018-04-26 株式会社日立製作所 Water treatment apparatus and its method
WO2018074328A1 (en) * 2016-10-21 2018-04-26 株式会社日立製作所 Water treatment apparatus and water treatment method

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