JP3461676B2 - Sewage treatment equipment - Google Patents

Sewage treatment equipment

Info

Publication number
JP3461676B2
JP3461676B2 JP02988197A JP2988197A JP3461676B2 JP 3461676 B2 JP3461676 B2 JP 3461676B2 JP 02988197 A JP02988197 A JP 02988197A JP 2988197 A JP2988197 A JP 2988197A JP 3461676 B2 JP3461676 B2 JP 3461676B2
Authority
JP
Japan
Prior art keywords
liquid level
aeration
filtration
tank
membrane
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
Application number
JP02988197A
Other languages
Japanese (ja)
Other versions
JPH10225686A (en
Inventor
清司 和泉
山田  豊
雅治 塗師
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 JP02988197A priority Critical patent/JP3461676B2/en
Publication of JPH10225686A publication Critical patent/JPH10225686A/en
Application granted granted Critical
Publication of JP3461676B2 publication Critical patent/JP3461676B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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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

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、生活排水などの有
機性汚水を処理する汚水処理装置に関する。
TECHNICAL FIELD The present invention relates to a sewage treatment apparatus for treating organic sewage such as domestic wastewater.

【0002】[0002]

【従来の技術】生活排水などの有機性汚水を処理する従
来の汚水処理装置として、たとえば図4に示したよう
な、前処理槽1と膜分離装置2を設置した曝気槽3と処
理水槽4とを備えた小型合併浄化槽がある。
2. Description of the Related Art As a conventional sewage treatment apparatus for treating organic sewage such as domestic wastewater, for example, an aeration tank 3 and a treated water tank 4 having a pretreatment tank 1 and a membrane separator 2 as shown in FIG. There is a small combined septic tank equipped with.

【0003】膜分離装置2はたとえば、上下が開口した
ケース2a内の上部に、上下方向に配置する平板状の膜
カートリッジ2bを一定間隔で平行に配列したものであ
り、膜カートリッジ2bは、図示を省略するが、濾板の
両表面に濾過膜を配置し、濾板と濾過膜との間、あるい
は濾板の内部に形成される膜透過液流路に連通する膜透
過液取出口を形成したものである。
The membrane separation device 2 is, for example, a flat plate-like membrane cartridge 2b arranged in the up-down direction and arranged in parallel at a constant interval in the upper part of a case 2a which is open at the top and bottom. Although omitted, the membrane permeate is arranged on both surfaces of the filter plate to form a membrane permeate outlet that communicates between the filter plate and the membrane or between the membrane permeate channels formed inside the filter plate. It was done.

【0004】このような小型合併浄化槽では、汚水5を
前処理槽1へ導入して、図示を省略したスクリーンなど
できょう雑物を除去し、次いで壁部6,7により曝気槽
3へ案内して、曝気槽3内の活性汚泥混合液8と混合
し、ブロワ9により曝気装置10を通じて膜カートリッ
ジ2bの下方より曝気する状態において、活性汚泥の作
用によって汚水5中に含まれている有機物や窒素分を除
去している。
In such a small combined septic tank, sewage 5 is introduced into the pretreatment tank 1 to remove impurities such as a screen (not shown) and then guided to the aeration tank 3 through the walls 6 and 7. And mixed with the activated sludge mixed liquid 8 in the aeration tank 3 and aerated by the blower 9 through the aeration device 10 from below the membrane cartridge 2b, organic substances and nitrogen contained in the sewage 5 by the action of the activated sludge. Minutes have been removed.

【0005】このとき、曝気槽3内の活性汚泥混合液8
をその自然水頭を駆動圧として膜カートリッジ2bによ
り重力濾過し、膜カートリッジ2bの膜透過液取出口に
チューブ11,集水管12を介して連通した透過液管1
3により透過液14を処理水槽4へ取り出している。
At this time, the activated sludge mixed liquid 8 in the aeration tank 3
Is subjected to gravity filtration by the membrane cartridge 2b using its natural head as a driving pressure, and the permeate pipe 1 is connected to the membrane permeate outlet of the membrane cartridge 2b via the tube 11 and the water collecting pipe 12.
The permeated liquid 14 is taken out to the treated water tank 4 by 3.

【0006】処理水槽4内の透過液14は、消毒部15
に導いて消毒した後、浄化処理水16として装置外部へ
流出させている。
The permeated liquid 14 in the treated water tank 4 is the disinfection section 15
After being guided to and disinfected, the purified treated water 16 is allowed to flow out of the apparatus.

【0007】[0007]

【発明が解決しようとする課題】上記したような膜分離
装置2では通常、透過液管13の終端部13aを処理水
槽4内において膜分離装置2の上端位置またはそれより
上方位置で開口させており、これにより、曝気槽3内の
液位が透過液管13の終端部13aに相応する位置まで
低下した時に濾過が停止し、また曝気槽3内の液位が終
端部13aより上昇して、膜分離装置2の膜面の両側に
必要な水頭差が生じた時に、直ちに濾過が開始されるよ
うになっている。
In the membrane separation device 2 as described above, the end portion 13a of the permeate pipe 13 is normally opened in the treated water tank 4 at the upper end position of the membrane separation device 2 or at a position higher than it. Therefore, when the liquid level in the aeration tank 3 is lowered to a position corresponding to the terminal end 13a of the permeated liquid pipe 13, the filtration is stopped, and the liquid level in the aeration tank 3 is raised above the terminal end 13a. The filtration is started immediately when the required head difference occurs on both sides of the membrane surface of the membrane separation device 2.

【0008】したがって、膜分離装置2は、曝気槽3内
への汚水5の流入が開始されたら直ちに濾過を行える状
態にする必要がある。濾過を行える状態とは、膜カート
リッジ2bの下方に設置された曝気装置10を通じて曝
気が行われていて、膜カートリッジ2bの膜面に対する
クロスフローが生じている状態をいう。
Therefore, the membrane separation device 2 needs to be ready for filtration immediately after the inflow of the dirty water 5 into the aeration tank 3 is started. The state in which filtration is possible refers to a state in which aeration is performed through the aeration device 10 installed below the membrane cartridge 2b, and a cross flow occurs on the membrane surface of the membrane cartridge 2b.

【0009】このためには、曝気装置10を通じて連続
曝気する場合は別として、曝気槽3内への汚水5の流入
と曝気装置10の駆動とを連動させる必要があるが、曝
気槽3内への汚水5の流入を検知することは実用上は非
常に難しい。(ただし、ポンプ等で汚水が流入される場
合はポンプの起動を汚水の流入と解釈できる。)しか
し、連続曝気を行うと、動力費が高くなるだけでなく、
過剰曝気によって生物処理に悪影響が及ぼされる。
For this purpose, apart from the case of continuous aeration through the aeration device 10, it is necessary to interlock the inflow of the dirty water 5 into the aeration tank 3 and the driving of the aeration device 10. It is very difficult in practice to detect the inflow of the dirty water 5. (However, if sewage is introduced by a pump, etc., starting the pump can be interpreted as sewage inflow.) However, continuous aeration not only increases the power cost but also
Biological treatment is adversely affected by over-aeration.

【0010】一法として、曝気槽3内に液位計を設置す
ることが考えられる。ところが、膜分離装置2は、上記
したように液位が上昇し始めると直ちに濾過が開始され
る構成なので、曝気槽3内へ汚水5がわずかでも流入す
れば濾過が起こる。しかるに、液位計によって検知でき
るのは、液位計の種類にもよるが10cm以上の液位変
動なので、液位計によって液位上昇が検知されるまで
は、曝気のない状態、すなわちクロスフローが供給され
ない状態で濾過が行われることになり、濾過効率がよく
ないだけでなく、膜分離装置2の膜面に目詰まりが生じ
やすいという問題がある。
As one method, it is conceivable to install a liquid level gauge in the aeration tank 3. However, since the membrane separation device 2 is configured to start filtration immediately when the liquid level starts to rise as described above, filtration occurs even if a small amount of the dirty water 5 flows into the aeration tank 3. However, depending on the type of level gauge, the level gauge can detect a level fluctuation of 10 cm or more, so until the level gauge detects a level rise, there is no aeration, that is, cross flow. Since the filtration is performed in a state where the water is not supplied, there is a problem that not only the filtration efficiency is poor, but also the membrane surface of the membrane separation device 2 is likely to be clogged.

【0011】本発明は上記問題を解決するもので、汚水
の流入と連動して曝気を行うことができ、膜分離装置に
おいて効率よく濾過を行えるようにすることを目的とす
るものである。
The present invention is intended to solve the above problems, and it is an object of the present invention to perform aeration in conjunction with the inflow of sewage and to enable efficient filtration in a membrane separation device.

【0012】[0012]

【課題を解決するための手段】上記問題を解決するため
に、本発明の汚水処理装置は、有機性汚水を活性汚泥処
理する曝気槽の内部に、槽内の自然水頭を駆動圧として
活性汚泥混合液を重力濾過する膜分離装置を浸漬配置
し、膜分離装置の下部に曝気装置を配設した汚水処理装
置であって、前記膜分離装置の膜透過側に連通する透過
液管は、通常運転水位より上方で濾過開始時に曝気槽液
位との間で濾過水頭を確保する所定位置に頂部が位置す
る逆U字状に配置し、その終端部を槽外において前記膜
分離装置の上端と同一高さ位置またはそれより上方で大
気圧下に開放してなり、曝気槽内の液位が透過液管の終
端部に相応する位置に低下するまでサイホン現象によっ
て濾過を継続し、サイホン状態が切れて濾過が停止され
て後に曝気槽内の液位が透過液管の頂部を越えて曝気槽
液位と透過液管の頂部との間で濾過水頭が確保された時
に濾過が開始されるものである。
In order to solve the above problems, the sewage treatment apparatus of the present invention comprises an activated sludge having a natural head in the tank as a driving pressure inside an aeration tank for treating organic sewage with activated sludge. A sewage treatment apparatus in which a membrane separation device for gravity-filtering a mixed solution is immersed, and an aeration device is arranged below the membrane separation device, and the permeate pipe communicating with the membrane permeation side of the membrane separation device is usually Aeration tank liquid above the operating water level at the start of filtration
The inverted U-shape with the top located at a predetermined position to secure the filtration head between the position and the end, and the terminal end thereof is outside the tank at the same height as the upper end of the membrane separation device or above the atmospheric pressure. It is opened downward and continues to filter by the siphon phenomenon until the liquid level in the aeration tank drops to a position corresponding to the end of the permeate pipe. The filtration is started when the liquid level exceeds the apex of the permeate tube and a filtered water head is secured between the aeration tank liquid level and the apex of the permeate tube.

【0013】好ましくは、曝気槽内の液位を測定する液
位測定手段を設け、曝気装置に給気するブロワーを起動
停止する制御装置を前記液位測定手段に接続して設け、
前記制御装置により、液位測定手段によって測定される
液位が、透過液管の終端部より所定距離上方に相応する
下限水位まで低下した時にブロワーを停止し、透過液管
の頂部に相応する上限水位まで上昇した時にブロワーを
起動するように構成する。下限水位は、曝気停止により
生じる液位低下によって、濾過は停止されるが膜面は露
出しない最低水位として設定される。
Preferably, a liquid level measuring means for measuring the liquid level in the aeration tank is provided, and a control device for starting and stopping a blower for supplying air to the aeration device is connected to the liquid level measuring means.
The control device stops the blower when the liquid level measured by the liquid level measuring means falls to a lower limit water level corresponding to a predetermined distance above the terminal end of the permeate pipe, and the upper limit corresponding to the top part of the permeate pipe. Configure the blower to start when the water level rises. The lower limit water level is set as the lowest water level at which filtration is stopped but the membrane surface is not exposed due to the decrease in liquid level caused by stopping aeration.

【0014】また好ましくは、液位測定手段として、液
位計、または曝気装置に給気するブロワーの吐出側圧力
を測定する圧力計を使用する。上記した構成によれば、
膜分離装置の膜透過側に連通する透過液管が、通常運転
水位より上方に頂部が位置する逆U字状に配置され、そ
の終端部が槽外において膜分離装置の上端と同一高さ位
置で大気圧下に開放されているので、透過液管が満管状
態となって濾過が行われている時は、サイホン現象によ
って、曝気槽内の液位が透過液管の終端部に相応する位
置に低下するまで濾過が継続される。
Further, preferably, as the liquid level measuring means, a liquid level gauge or a pressure gauge for measuring the discharge side pressure of the blower for supplying air to the aeration device is used. According to the above configuration,
The permeate pipe, which communicates with the membrane permeation side of the membrane separation device, is arranged in an inverted U shape with the top located above the normal operating water level, and the end portion thereof is located at the same height as the upper end of the membrane separation device outside the tank. Since it is opened to the atmospheric pressure, the liquid level in the aeration tank corresponds to the end of the permeate pipe due to the siphon phenomenon when the permeate pipe is full and filtration is performed. Filtration continues until it is lowered into position.

【0015】一方、一旦サイホン状態が切れて濾過が停
止されると、曝気槽内へ汚水が流入しても濾過はすぐに
は開始されず、曝気槽内の液位が透過液管の頂部を越え
て、曝気槽液位と透過液管の頂部との間で濾過水頭が確
保された時にはじめて濾過が開始される。
On the other hand, once the siphon state is cut off and the filtration is stopped, the filtration does not start immediately even if the sewage flows into the aeration tank, and the liquid level in the aeration tank is set at the top of the permeate pipe. Beyond that, filtration is initiated only when the filtration head is secured between the aeration tank level and the top of the permeate tube.

【0016】このような、濾過が停止してから濾過が再
開されるまでの間は必ずしもクロスフローは必要ではな
いので、曝気を停止することが可能となり、それにより
脱窒素のための嫌気状態を確保することも可能となる。
また、いつ汚水の流入があるかわからない時に不必要な
曝気を行う不経済を防止できる。
Since cross flow is not necessarily required between the time when the filtration is stopped and the time when the filtration is restarted, it is possible to stop the aeration, thereby reducing the anaerobic condition for denitrification. It is possible to secure it.
In addition, it is possible to prevent an uneconomical situation in which unnecessary aeration is performed when the inflow of sewage is unknown.

【0017】また透過液管が上記のように配置された膜
分離装置では、濾過の開始水位と停止水位の差を大きく
とれるので、液位測定手段として液位計を精度にかかわ
りなく使用できる。
Further, in the membrane separation device in which the permeate pipe is arranged as described above, the difference between the starting water level and the stopping water level of filtration can be made large, so that a liquid level gauge can be used as the liquid level measuring means regardless of the accuracy.

【0018】液位測定手段として、曝気装置に給気する
ブロワーの吐出側圧力を測定する圧力計を使用する場合
は、曝気槽内の下限水位と上限水位とに対応するブロワ
ーの吐出側圧力を予め求めておく。
When a pressure gauge for measuring the discharge side pressure of the blower supplying air to the aeration device is used as the liquid level measuring means, the blower discharge side pressure corresponding to the lower limit water level and the upper limit water level in the aeration tank is used. Get in advance.

【0019】[0019]

【発明の実施の形態】以下、本発明の実施形態を図面を
参照しながら説明する。図1〜図3は本発明の一実施形
態における汚水処理装置21を示し、この汚水処理装置
21は、先に図4を用いて説明した前処理槽1と曝気槽
3と処理水槽4とを備えた従来の小型合併浄化槽の一部
を構成することも可能である。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described below with reference to the drawings. 1 to 3 show a sewage treatment apparatus 21 according to an embodiment of the present invention. The sewage treatment apparatus 21 includes the pretreatment tank 1, the aeration tank 3 and the treated water tank 4 which have been described with reference to FIG. It is also possible to form a part of the conventional small combined septic tank provided.

【0020】すなわち、汚水処理装置21は、有機性汚
水を活性汚泥処理する曝気槽22と処理水槽23とを備
えており、曝気槽22には、上部に汚水供給管24が開
口するとともに、内部に、槽内の活性汚泥混合液25を
その自然水頭を駆動圧として重力濾過する膜分離装置2
6が浸漬設置され、膜分離装置26の下部に曝気装置2
7が配設されている。
That is, the sewage treatment apparatus 21 is provided with an aeration tank 22 for treating organic sewage with activated sludge and a treated water tank 23. The aeration tank 22 has a sewage supply pipe 24 opened at the upper part thereof and has an internal structure. In addition, the membrane separation device 2 for gravity-filtering the activated sludge mixed liquid 25 in the tank by using the natural head as a driving pressure.
6 is installed by immersion, and the aeration device 2 is provided below the membrane separation device 26.
7 are provided.

【0021】膜分離装置26は、上下が開口した箱枠状
のケース28内の上部に、上下方向に配置する平板状の
膜カートリッジ29を一定間隔で平行に配列しており、
膜カートリッジ29の下方に、上記曝気装置27が配設
されている。膜カートリッジ29は、図示を省略する
が、濾板の両表面に濾過膜を配置し、濾板と濾過膜との
間、あるいは濾板の内部に形成される膜透過液流路に連
通する膜透過液取出口を形成したものである。ケース2
8の上部には、各膜カートリッジ29の膜透過液取出口
にチューブ30を介して連通する集水管31が設けら
れ、集水管31に連通して透過液管32が設けられてい
る。
The membrane separation device 26 has flat box-shaped membrane cartridges 29 arranged vertically in parallel in the upper part of a box frame-shaped case 28 having an opening at the top and bottom.
The aeration device 27 is arranged below the membrane cartridge 29. Although not shown, the membrane cartridge 29 is a membrane in which filtration membranes are arranged on both surfaces of the filter plate and communicate with the membrane permeate liquid flow path formed between the filter plates or inside the filter plate. A permeated liquid outlet is formed. Case 2
A water collecting pipe 31 that communicates with the membrane permeated liquid outlet of each membrane cartridge 29 via a tube 30 is provided on the upper part of 8, and a permeated liquid pipe 32 that communicates with the water collecting pipe 31 is provided.

【0022】透過液管32は、通常運転水位NLより上
方の所定位置に頂部32aが位置する逆U字状に配置さ
れており、その終端部32bは処理水槽23内において
上記膜カートリッジ29の上端とほぼ同一高さ位置で大
気圧下に開放している。
The permeate pipe 32 is arranged in an inverted U-shape with a top 32a located at a predetermined position above the normal operating water level NL, and its end 32b is the upper end of the membrane cartridge 29 in the treated water tank 23. It is open to atmospheric pressure at the same height as.

【0023】曝気装置27は、槽外のブロワー33に連
通しており、ブロワー33の吐出側に圧力計34が設け
られるとともに、この圧力計34に接続して、ブロワー
33を起動停止する制御装置35が設けられている。
The aeration device 27 is connected to a blower 33 outside the tank, and a pressure gauge 34 is provided on the discharge side of the blower 33, and a controller for connecting to the pressure gauge 34 to start and stop the blower 33. 35 are provided.

【0024】処理水槽23には、排水ポンプ36,排水
管37が設けられている。上記した構成における作用を
説明する。汚水供給管24により有機性汚水38が曝気
槽2へ導入されると、有機性汚水38は槽内の活性汚泥
混合液25と混合され、有機性汚水38中の有機物や窒
素分は活性汚泥の作用によって除去される。
A drainage pump 36 and a drainage pipe 37 are provided in the treated water tank 23. The operation of the above configuration will be described. When the organic sewage 38 is introduced into the aeration tank 2 through the sewage supply pipe 24, the organic sewage 38 is mixed with the activated sludge mixed solution 25 in the tank, and the organic matter and the nitrogen content in the organic sewage 38 are converted into the activated sludge. Removed by action.

【0025】このとき、曝気装置27により後述するよ
うに適宜曝気が行われ、活性汚泥混合液25に酸素が供
給されるとともに、曝気空気の気泡およびそれにより生
起される上昇水流が膜カートリッジ29間の間隙に流入
し、それによって、膜面全体が均一に洗浄され、かつ膜
面における濃度分極が低減されて濾過抵抗が低下し、か
つケース28の内外を循環する槽内循環水流が形成され
る。
At this time, as described later, aeration is appropriately performed by the aeration device 27, oxygen is supplied to the activated sludge mixed liquid 25, and bubbles of aerated air and the rising water flow generated thereby are generated between the membrane cartridges 29. Flowing into the gap of the case 28, thereby uniformly cleaning the entire membrane surface, reducing concentration polarization on the membrane surface to reduce filtration resistance, and forming a circulating water flow in the tank circulating inside and outside the case 28. .

【0026】この状態において、活性汚泥混合液25
は、その液面から透過液管32の開口する終端部32b
までの水頭、すなわち膜カートリッジ29の上端位置ま
での水頭を駆動圧として膜カートリッジ29により重力
濾過され、膜カートリッジ29の膜面を透過した透過液
39は透過液管32により処理水槽23へ導かれる。
In this state, the activated sludge mixed liquid 25
Is a terminal portion 32b where the permeate pipe 32 opens from its liquid surface.
Up to the head of the membrane cartridge 29, that is, the head of the membrane cartridge 29 as a driving pressure, is gravity filtered by the membrane cartridge 29, and the permeate 39 that has permeated the membrane surface of the membrane cartridge 29 is guided to the treated water tank 23 by the permeate pipe 32. .

【0027】このとき、上記したように、透過液管32
が通常運転水位NLより上方の所定位置に頂部32aが
位置する逆U字状に配置され、その終端部32bが膜カ
ートリッジ29の上端と同一高さ位置で大気圧下に開放
されているので、図1に示したように透過液管32が満
管状態となって濾過が行われている時は、サイホン現象
によって濾過が継続され、図2に示したように曝気槽3
2内の液位が透過液管32の終端部32bに相応する位
置まで低下した時に、サイホン状態が切れて濾過が停止
される。
At this time, as described above, the permeated liquid pipe 32
Is arranged in an inverted U shape in which the top portion 32a is located at a predetermined position above the normal operating water level NL, and the end portion 32b thereof is opened under the atmospheric pressure at the same height position as the upper end of the membrane cartridge 29, As shown in FIG. 1, when the permeated liquid pipe 32 is full and filtration is performed, the filtration is continued due to the siphon phenomenon, and as shown in FIG.
When the liquid level in 2 drops to a position corresponding to the terminal end 32b of the permeate pipe 32, the siphon state is cut off and the filtration is stopped.

【0028】一旦濾過が停止されると、曝気槽32内へ
有機性汚水38が流入してもすぐには重力濾過は開始さ
れず、図3に示したように活性汚泥混合液25の液位が
透過液管32の頂部32bを越えて、曝気槽液位と透過
液管32の頂部32bとの間で濾過水頭が確保された時
にはじめて濾過が開始される。
Once the filtration is stopped, gravity filtration does not start immediately even if the organic sewage 38 flows into the aeration tank 32, and as shown in FIG. The filtration is started only when the filtration head is secured between the aeration tank liquid level and the top 32b of the permeate pipe 32 beyond the top 32b of the permeate pipe 32.

【0029】なおこのとき、圧力計34によってブロワ
ー33の吐出側圧力が測定されており、測定された圧力
が、予め設定した下限圧まで低下した時に制御装置35
によりブロワー33が停止され、上限圧まで上昇した時
に制御装置35によりブロワー33が起動される。ここ
で、下限圧は、透過液管32の終端部32bよりやや上
方に相応する曝気槽下限水位LLにおける圧力であり、
上限圧は、透過液管32の頂部32bに相応する曝気槽
上限水位HLにおける圧力である。
At this time, the pressure on the discharge side of the blower 33 is measured by the pressure gauge 34, and when the measured pressure falls to a preset lower limit pressure, the control device 35
Thus, the blower 33 is stopped, and when the pressure reaches the upper limit pressure, the control device 35 activates the blower 33. Here, the lower limit pressure is the pressure at the lower limit water level LL of the aeration tank, which is slightly above the terminal end 32b of the permeate pipe 32,
The upper limit pressure is the pressure at the aeration tank upper limit water level HL corresponding to the top 32b of the permeate pipe 32.

【0030】このようにして、濾過が停止してから濾過
が再開されるまでの必ずしもクロスフローが必要ない間
は、ブロワー33,曝気装置27を停止することがで
き、効率よく曝気を行えるとともに、脱窒素のための嫌
気状態を確保できる。
In this way, the blower 33 and the aeration device 27 can be stopped while the cross flow is not necessarily required after the filtration is stopped until the filtration is restarted, and the aeration can be performed efficiently. An anaerobic condition for denitrification can be secured.

【0031】処理水槽23内の透過液39は、排水ポン
プ36,排水管37によって、図示を省略した消毒部な
どへ導かれた後、浄化処理水として排出される。なお、
下限水位LLは以下のようにして設定する。
The permeated liquid 39 in the treated water tank 23 is guided to a disinfecting section (not shown) by a drainage pump 36 and a drainage pipe 37 and then discharged as purified treated water. In addition,
The lower limit water level LL is set as follows.

【0032】曝気槽(水深2m)に、ケース(高さ13
0cm)内に膜カートリッジ(長さ100×幅49×厚
さ0.6cm)を0.8cm間隔で配列した膜分離装置
を設置し、曝気装置によって、膜面を洗浄可能な強度で
曝気する場合、曝気停止時には曝気空気の気泡の上昇が
ないため、曝気槽内の液位は曝気時より通常2〜3%程
度低下するものであり、この場合、4〜6cmの液位低
下が生じる。一方、曝気により生起される上昇流が膜カ
ートリッジ間の間隙を通過するときの抵抗は、水頭換算
(すなわち液位換算)で5cm程度となる。
In the aeration tank (water depth 2 m), the case (height 13
When a membrane separator (100 cm in length × 49 in width × 0.6 cm in thickness) arranged at 0.8 cm intervals is installed in 0 cm), and the membrane surface is aerated with a strength sufficient for cleaning by an aeration device. Since the bubbles of the aerated air do not rise when the aeration is stopped, the liquid level in the aeration tank is usually lowered by about 2 to 3% as compared with the aeration, and in this case, the liquid level is lowered by 4 to 6 cm. On the other hand, the resistance when the ascending flow generated by the aeration passes through the gap between the membrane cartridges is about 5 cm in terms of water head (that is, in terms of liquid level).

【0033】したがって、曝気槽内では曝気停止によっ
て10cm程度の液位低下が生じることになり、このこ
とより、曝気停止によって濾過は停止されるが膜面は露
出しない曝気時の下限水位LLとして、膜カートリッジ
の膜上端より10cm程度上方を設定する。
Therefore, in the aeration tank, the liquid level is lowered by about 10 cm due to the stop of the aeration. Therefore, the lower limit water level LL at the time of the aeration in which the filtration is stopped by the stop of the aeration but the membrane surface is not exposed, Set about 10 cm above the upper edge of the membrane of the membrane cartridge.

【0034】上記した実施形態では、ブロワー33の吐
出側圧力に基づいてブロワー33を起動停止するように
したが、透過液管32が上記のように配置された膜分離
装置26によれば通常、濾過の開始水位と停止水位の差
を30cm程度と大きくとれるので、液位計を利用して
ブロワー33を起動停止することもできる。また、膜カ
ートリッジは、チューブ形状のものや、セラミック材料
からなるものなど、重力濾過可能なものであれば種々使
用できる。
In the above-described embodiment, the blower 33 is started and stopped based on the discharge side pressure of the blower 33. However, according to the membrane separation device 26 in which the permeate pipe 32 is arranged as described above, Since the difference between the starting water level and the stopping water level of filtration can be as large as about 30 cm, the blower 33 can be started and stopped by using the liquid level gauge. Various membrane cartridges can be used as long as they can be gravity-filtered, such as tube-shaped cartridges and ceramic cartridges.

【0035】[0035]

【発明の効果】以上のように、本発明の汚水処理装置に
よれば、膜分離装置の膜透過側に連通する透過液管を、
通常運転水位より上方に頂部が位置する逆U字状に配置
し、その終端部を槽外において前記膜分離装置の上端と
同一高さ位置で大気圧下に開放したので、一旦濾過が停
止された後は汚水の流入があってもすぐには濾過は開始
されず、曝気槽液位が透過液管の頂部を越えた時にはじ
めて濾過が再開される。したがって、濾過が停止されて
から再開されるまでの間は、曝気装置を停止することが
可能となり、それにより脱窒素のための嫌気状態を確保
することも可能となる。
As described above, according to the sewage treatment apparatus of the present invention, the permeate pipe communicating with the membrane permeation side of the membrane separator is
It was arranged in an inverted U-shape with the top located above the normal operating water level, and its end was opened outside the tank at the same height as the upper end of the membrane separator under atmospheric pressure, so filtration was stopped once. After that, even if there is inflow of sewage, the filtration is not started immediately, and the filtration is restarted only when the liquid level in the aeration tank exceeds the top of the permeate pipe. Therefore, it is possible to stop the aeration device between the time when the filtration is stopped and the time when the filtration is restarted, whereby it is possible to secure the anaerobic state for denitrification.

【0036】曝気装置の起動停止を効率よく行うために
は、液位測定手段と、曝気装置に給気するブロワーを起
動停止する制御装置とを設けて、曝気槽液位が予め設定
した下限水位まで低下した時にブロワーを停止し、上限
水位まで上昇した時にブロワーを起動するようにすれば
よい。
In order to efficiently start and stop the aeration device, a liquid level measuring means and a control device for starting and stopping a blower for supplying air to the aeration device are provided so that the aeration tank liquid level is set at a lower limit water level set in advance. The blower should be stopped when the water level has dropped to the upper limit, and the blower should be started when the water level has reached the upper limit.

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

【図1】本発明の一実施形態における水処理装置の通常
運転時の状態を示した説明図である。
FIG. 1 is an explanatory diagram showing a state during normal operation of a water treatment device according to an embodiment of the present invention.

【図2】図1に示した水処理装置の濾過停止時の状態を
示した説明図である。
FIG. 2 is an explanatory diagram showing a state of the water treatment apparatus shown in FIG. 1 when filtration is stopped.

【図3】図1に示した水処理装置の濾過開始時の状態を
示した説明図である。
FIG. 3 is an explanatory diagram showing a state of the water treatment device shown in FIG. 1 at the start of filtration.

【図4】従来の水処理装置の全体構成を示した縦断面図
である。
FIG. 4 is a vertical cross-sectional view showing the overall configuration of a conventional water treatment device.

【符号の説明】[Explanation of symbols]

21 汚水処理装置 22 曝気槽 23 処理水槽 25 活性汚泥混合液 26 膜分離装置 27 曝気装置 32 透過液管 32a 頂部 32b 終端部 33 ブロワー 34 圧力計(液位測定手段) 35 制御装置 38 有機性汚水 NL 通常運転水位 LL 下限水位 HL 上限水位 21 Sewage treatment equipment 22 Aeration tank 23 Treated water tank 25 Activated sludge mixture 26 Membrane separation device 27 Aeration device 32 Permeate tube 32a top 32b termination 33 blower 34 Pressure gauge (liquid level measuring means) 35 Control device 38 Organic wastewater NL Normal operating water level LL lower water level HL upper limit water level

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平5−185078(JP,A) 特開 平8−39088(JP,A) 特開 平7−328694(JP,A) (58)調査した分野(Int.Cl.7,DB名) C02F 1/44 ZAB B01D 65/02 520 ─────────────────────────────────────────────────── ─── Continuation of the front page (56) References JP-A-5-185078 (JP, A) JP-A-8-39088 (JP, A) JP-A-7-328694 (JP, A) (58) Field (Int.Cl. 7 , DB name) C02F 1/44 ZAB B01D 65/02 520

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 有機性汚水を活性汚泥処理する曝気槽の
内部に、槽内の自然水頭を駆動圧として活性汚泥混合液
を重力濾過する膜分離装置を浸漬配置し、膜分離装置の
下部に曝気装置を配設した汚水処理装置であって、前記
膜分離装置の膜透過側に連通する透過液管は、通常運転
水位より上方で濾過開始時に曝気槽液位との間で濾過水
頭を確保する所定位置に頂部が位置する逆U字状に配置
し、その終端部を槽外において前記膜分離装置の上端と
同一高さ位置またはそれより上方で大気圧下に開放して
なり、曝気槽内の液位が透過液管の終端部に相応する位
置に低下するまでサイホン現象によって濾過を継続し、
サイホン状態が切れて濾過が停止されて後に曝気槽内の
液位が透過液管の頂部を越えて曝気槽液位と透過液管の
頂部との間で濾過水頭が確保された時に濾過が開始され
ることを特徴とする汚水処理装置。
1. A membrane separator for gravity-filtering an activated sludge mixed solution using a natural head of the tank as a driving pressure is immersed in an aeration tank for treating organic sludge with activated sludge, and is placed below the membrane separator. In the sewage treatment device provided with an aeration device, the permeate pipe communicating with the membrane permeation side of the membrane separation device has a filtered water between the aeration tank liquid level at the start of filtration above the normal operating water level.
It is arranged in an inverted U-shape with the top located at a predetermined position for securing the head, and its end is opened outside the tank at the same height as or above the upper end of the membrane separation device under atmospheric pressure. , The filtration is continued by the siphon phenomenon until the liquid level in the aeration tank drops to a position corresponding to the end of the permeate pipe,
Filtration starts when the liquid level in the aeration tank exceeds the top of the permeate pipe and the filtration head is secured between the liquid level in the aeration tank and the top of the permeate pipe after the siphon condition is cut off and filtration is stopped. A sewage treatment device characterized by being processed.
【請求項2】 曝気槽内の液位を測定する液位測定手段
を設け、曝気装置に給気するブロワーを起動停止する制
御装置を前記液位測定手段に接続して設け、前記制御装
置により、液位測定手段によって測定される液位が、透
過液管の終端部より所定距離上方に相応する下限水位ま
で低下した時にブロワーを停止し、透過液管の頂部に相
応する上限水位まで上昇した時にブロワーを起動するよ
うに構成したことを特徴とする請求項1記載の汚水処理
装置。
2. A liquid level measuring means for measuring the liquid level in the aeration tank is provided, and a control device for starting and stopping a blower for supplying air to the aeration device is provided by being connected to the liquid level measuring means. , When the liquid level measured by the liquid level measuring means is lowered to a lower limit water level corresponding to a predetermined distance above the terminal end of the permeate pipe, the blower is stopped and raised to an upper limit water level corresponding to the top of the permeate pipe. The sewage treatment apparatus according to claim 1, wherein the blower is activated at times.
【請求項3】 液位測定手段が、液位計、または曝気装
置に給気するブロワーの吐出側圧力を測定する圧力計で
あることを特徴とする請求項2記載の汚水処理装置。
3. The sewage treatment apparatus according to claim 2, wherein the liquid level measuring means is a liquid level gauge or a pressure gauge for measuring the discharge side pressure of the blower that supplies air to the aeration device.
JP02988197A 1997-02-14 1997-02-14 Sewage treatment equipment Expired - Lifetime JP3461676B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP02988197A JP3461676B2 (en) 1997-02-14 1997-02-14 Sewage treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP02988197A JP3461676B2 (en) 1997-02-14 1997-02-14 Sewage treatment equipment

Publications (2)

Publication Number Publication Date
JPH10225686A JPH10225686A (en) 1998-08-25
JP3461676B2 true JP3461676B2 (en) 2003-10-27

Family

ID=12288328

Family Applications (1)

Application Number Title Priority Date Filing Date
JP02988197A Expired - Lifetime JP3461676B2 (en) 1997-02-14 1997-02-14 Sewage treatment equipment

Country Status (1)

Country Link
JP (1) JP3461676B2 (en)

Also Published As

Publication number Publication date
JPH10225686A (en) 1998-08-25

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