JP3181468B2 - Sewage treatment equipment - Google Patents

Sewage treatment equipment

Info

Publication number
JP3181468B2
JP3181468B2 JP9316294A JP9316294A JP3181468B2 JP 3181468 B2 JP3181468 B2 JP 3181468B2 JP 9316294 A JP9316294 A JP 9316294A JP 9316294 A JP9316294 A JP 9316294A JP 3181468 B2 JP3181468 B2 JP 3181468B2
Authority
JP
Japan
Prior art keywords
chamber
filtrate
membrane
aeration chamber
activated sludge
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 - Fee Related
Application number
JP9316294A
Other languages
Japanese (ja)
Other versions
JPH07299491A (en
Inventor
清司 和泉
山田  豊
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
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Application filed by Kubota Corp filed Critical Kubota Corp
Priority to JP9316294A priority Critical patent/JP3181468B2/en
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Application granted granted Critical
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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]

【産業上の利用分野】本発明は生活排水処理、下水処
理、産業排水処理などに用いられる汚水処理装置に関
し、特に流入汚水量の変動にかかわらず活性汚泥法と膜
分離法とを行える汚水処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a sewage treatment apparatus used for domestic sewage treatment, sewage treatment, industrial sewage treatment, etc., and more particularly to sewage treatment capable of performing an activated sludge method and a membrane separation method regardless of fluctuations in the amount of inflowed sewage. Related to the device.

【0002】[0002]

【従来の技術】生活排水処理、下水処理、産業排水処理
などに用いられる汚水処理装置として、たとえば図2に
示したようなものが知られている。このような汚水処理
装置においては、被処理水供給管31より被処理水を導
入して、スクリーン32などを設けた濾過部33を通過
させる間にきょう雑物を除去し、この被処理水を受入室
34に貯留するとともに、その適当量をエアリフトポン
プ35などにより曝気室36に導いている。
2. Description of the Related Art As a wastewater treatment apparatus used for domestic wastewater treatment, sewage treatment, industrial wastewater treatment and the like, for example, the one shown in FIG. 2 is known. In such a sewage treatment apparatus, water to be treated is introduced from the water to be treated supply pipe 31 and impurities are removed while passing through a filtration unit 33 provided with a screen 32 and the like. While being stored in the receiving chamber 34, an appropriate amount thereof is guided to the aeration chamber 36 by an air lift pump 35 or the like.

【0003】そして、被処理水を曝気室36内の活性汚
泥混合液と混合し、ブロワ37などの給気手段より曝気
装置38を通じて曝気空気を供給する好気的条件下に曝
気空気の気泡流を利用して攪拌しながら、活性汚泥の作
用によって被処理水中の有機物や窒素分を除去してい
る。また、活性汚泥混合液中に浸漬して設けた膜分離装
置39の濾液側にポンプ40により吸引負圧を供給し、
濾過膜の表裏に圧力差を生ぜしめることによって、濾過
膜により固液分離を行い、活性汚泥を室内に残留させる
とともに、濾過膜を透過した濾液を取り出している。
[0003] The water to be treated is mixed with the activated sludge mixture in the aeration chamber 36, and aerated air is supplied under aerobic conditions by supplying aerated air through an aeration device 38 from an air supply means such as a blower 37. The organic sludge and the nitrogen content in the water to be treated are removed by the action of the activated sludge while stirring using the water. Further, suction negative pressure is supplied by the pump 40 to the filtrate side of the membrane separation device 39 provided by immersion in the activated sludge mixture,
By generating a pressure difference between the front and back of the filtration membrane, solid-liquid separation is performed by the filtration membrane, the activated sludge remains in the room, and the filtrate that has passed through the filtration membrane is taken out.

【0004】そして、この濾液を消毒部41に導いて滅
菌器42で衛生上支障のないように消毒し、その後、濾
液室43を経て浄化処理水44として装置の外部へ流出
させている。
[0004] The filtrate is guided to a disinfection unit 41 and disinfected by a sterilizer 42 so as not to impair sanitation. Thereafter, the filtrate is discharged to the outside of the apparatus as a purified water 44 through a filtrate chamber 43.

【0005】このとき、受入室34内の上部と膜分離装
置39の上方とにそれぞれ液位計45,液位計46を設
け、これらの液位計44,45により測定される液位に
基づいて、被処理水31の流入量とポンプ40により引
き抜く濾液量との調整を行うとともに、濾過膜を浸漬状
態に維持する活性汚泥混合液の最低液位Lを確保するよ
うにしている。
At this time, a liquid level gauge 45 and a liquid level gauge 46 are provided above the inside of the receiving chamber 34 and above the membrane separation device 39, respectively, based on the liquid levels measured by these liquid level gauges 44 and 45. Thus, the inflow amount of the water 31 to be treated and the amount of the filtrate to be withdrawn by the pump 40 are adjusted, and the minimum liquid level L of the activated sludge mixed liquid for maintaining the filtration membrane in the immersion state is ensured.

【0006】[0006]

【発明が解決しようとする課題】しかしながら、上記し
たような汚水処理装置を5〜50人規模の小型合併浄化
槽として用いようとすると、コスト・機器の信頼性・維
持管理面の制約から吸引ポンプや液位計の設置は難し
く、実用化されていないのが現状である。
However, if the above-mentioned sewage treatment apparatus is to be used as a small-sized combined clarification tank with a size of 5 to 50 persons, the suction pump or the sewage treatment apparatus is limited due to cost, equipment reliability, and maintenance and management. The installation of a liquid level gauge is difficult and has not been put to practical use at present.

【0007】また、合併浄化槽は、規模が小さくなるほ
ど流入汚水量の変動が大きくなるのが通常なので、膜分
離法を導入するためには流量調整機能が不可欠である。
また、従来の膜分離法においては、濾過膜を洗浄する間
隔を長く保つために一般に定流量濾過を行っており、流
入汚水量が変動する状態において定流量濾過を行うため
には流量調整機能を有する槽が必要である。
[0007] In addition, since the merged septic tank generally has a larger fluctuation in the amount of inflowing sewage as the scale becomes smaller, a flow rate adjusting function is indispensable for introducing a membrane separation method.
In addition, in the conventional membrane separation method, a constant flow rate filtration is generally performed in order to maintain a long interval for washing the filtration membrane, and a flow rate adjustment function is required to perform the constant flow rate filtration in a state where the amount of inflowed sewage fluctuates. Is required.

【0008】本発明は上記問題を解決するもので、簡単
な構成でありながら、流入汚水量の変動にかかわらず活
性汚泥処理と膜分離処理とを行える汚水処理装置を提供
することを目的とする。
An object of the present invention is to solve the above-mentioned problem and to provide a sewage treatment apparatus capable of performing activated sludge treatment and membrane separation treatment irrespective of fluctuations in the amount of inflowed sewage while having a simple structure. .

【0009】[0009]

【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、被処理水供給管より導入
される被処理水を好気条件下で活性汚泥により生物学的
に処理する曝気室を設け、この曝気室の内部に室内の自
然水頭を駆動圧として活性汚泥混合液を固液分離する膜
分離装置を設け、前記曝気室と隔壁を介して分離された
濾液室を設け、前記曝気室と濾液室とを濾液管により連
通し、濾液管の一端を膜分離装置の膜透過側に接続する
とともに、他端を膜分離装置の頂部より下方の適当位置
において濾液室に連通させ、前記濾液管の他端に電磁弁
を設置し、この電磁弁を間欠開閉制御する制御手段を設
け、制御装置で曝気室内における液位を膜分離装置より
上方の一定範囲内に維持して曝気室内の自然水頭を駆動
圧として膜分離装置で活性汚泥混合液を固液分離する
のである。
In order to solve the above-mentioned problems, a sewage treatment apparatus according to the present invention is capable of biologically treating treated water introduced from a treated water supply pipe with activated sludge under aerobic conditions. An aeration chamber for processing is provided, and a membrane separation device for solid-liquid separation of the activated sludge mixed liquid is provided inside the aeration chamber using the natural head of the room as a driving pressure, and the filtrate chamber separated via the partition from the aeration chamber is provided. setting only, connecting the filtrate pipe and the aeration chamber and the filtrate chamber
And one end of the filtrate tube is connected to the membrane permeation side of the membrane separator, and the other end is communicated with the filtrate chamber at an appropriate position below the top of the membrane separator, and an electromagnetic valve is installed at the other end of the filtrate tube. Control means for controlling the intermittent opening and closing of this solenoid valve.
Control, the liquid level in the aeration chamber is controlled by the membrane separation device.
Driving the natural head in the aeration chamber by maintaining it within a certain range above
As the pressure, the activated sludge mixture is solid-liquid separated by a membrane separation device .

【0010】[0010]

【作用】上記構成により、曝気室に導入された被処理水
は室内の活性汚泥と混合され、好気条件下で活性汚泥の
作用により生物学的に処理されるとともに、この活性汚
泥混合液に浸漬して設けられた膜分離装置により、室内
の自然水頭を駆動圧として固液分離される。このとき、
濾液管の他端が膜分離装置の頂部より下方の適当位置に
おいて濾液室に導かれているので、曝気室内の自然水頭
が大きな駆動圧として利用される。
According to the above construction, the water to be treated introduced into the aeration chamber is mixed with the activated sludge in the room, and is biologically treated by the action of the activated sludge under aerobic conditions. By a membrane separation device provided by immersion, solid-liquid separation is performed using the natural head in the room as a driving pressure. At this time,
Since the other end of the filtrate tube is guided to the filtrate chamber at an appropriate position below the top of the membrane separation device, the natural head in the aeration chamber is used as a large driving pressure.

【0011】そして、曝気室への被処理水の流入量が多
くなり室内の液位が上昇して自然水頭が大きくなると、
濾過速度が大きくなり、逆に、曝気室への被処理水の流
入量が少なくなり室内の液位が低下して自然水頭が小さ
くなると、濾過速度が小さくなる。このようにして被処
理水の流入量の変動に合わせて濾過速度が自動的に変化
する結果、被処理水の流入量の変動の影響が緩和され
る。
[0011] Then, when the inflow of the water to be treated into the aeration chamber increases and the liquid level in the room rises and the natural head increases,
When the filtration rate increases and, conversely, the flow rate of the water to be treated into the aeration chamber decreases, the liquid level in the room decreases, and the natural head decreases, so that the filtration rate decreases. In this way, as a result of the filtration speed automatically changing in accordance with the change in the inflow of the water to be treated, the influence of the change in the inflow of the water to be treated is reduced.

【0012】そして、被処理水の流入量と濾液室へ送ら
れる濾液量とのバランスより、曝気室内の液位が膜分離
装置より上方の一定下限の液位まで低下したときは、制
御手段により電磁弁が閉じられて固液分離は停止され、
その後、曝気室内の液位が上昇して、膜分離装置より上
方の一定上限の液位に達したときに、電磁弁が開かれて
固液分離が再開される。このようにして、膜分離装置を
活性汚泥混合液中に浸漬状態に維持しつつ、さらに制御
手段により電磁弁を間欠開閉しながら、固液分離が行わ
れる。
When the liquid level in the aeration chamber drops to a certain lower limit liquid level above the membrane separation device due to the balance between the inflow amount of the water to be treated and the filtrate volume sent to the filtrate chamber, the control means The solenoid valve is closed, solid-liquid separation is stopped,
Thereafter, when the liquid level in the aeration chamber rises and reaches a certain upper limit liquid level above the membrane separation device, the solenoid valve is opened and solid-liquid separation is restarted. In this way, solid-liquid separation is performed while maintaining the membrane separation device in the activated sludge mixture and further intermittently opening and closing the electromagnetic valve by the control means.

【0013】[0013]

【実施例】以下、本発明の一実施例を図面を参照しなが
ら説明する。図1は本発明の一実施例の汚水処理装置を
示し、本体1は、被処理水供給管2より導入される被処
理水を好気条件下で活性汚泥により生物学的に処理する
曝気室3と、この曝気室3と隔壁4を介して分離された
濾液室5とで構成されており、濾液室5には排出管6が
設けられている。
An embodiment of the present invention will be described below with reference to the drawings. FIG. 1 shows a sewage treatment apparatus according to one embodiment of the present invention. A main body 1 is an aeration chamber for biologically treating treated water introduced from a treated water supply pipe 2 with activated sludge under aerobic conditions. 3 and an aeration chamber 3 and a filtrate chamber 5 separated via a partition 4. The filtrate chamber 5 is provided with a discharge pipe 6.

【0014】曝気室3内には、被処理水供給管2の開口
部を覆って、スクリーン7などを備えた濾過部8が設け
られるとともに、上部に室内の活性汚泥混合液の液位を
測定する液位計9が、タイマー機能をも備えた制御装置
9aに接続して設けられている。また、隔壁4の近傍
に、室内の自然水頭を駆動圧として活性汚泥混合液を固
液分離する浸漬型の膜分離装置10が設けられている。
なお、曝気室3は、最大水頭差が2mとなるように構成
されている。
In the aeration chamber 3, there is provided a filtration unit 8 provided with a screen 7 and the like, covering the opening of the water supply pipe 2 to be treated, and measuring the liquid level of the activated sludge mixed liquid in the room at the upper part. The liquid level gauge 9 is connected to a control device 9a having a timer function. In addition, an immersion type membrane separation device 10 is provided in the vicinity of the partition 4 for solid-liquid separation of the activated sludge mixture by using the natural head in the room as a driving pressure.
The aeration chamber 3 is configured such that the maximum head difference is 2 m.

【0015】膜分離装置10は、上下が開口する箱状の
ケーシング11の内部に膜カートリッジ12を適当間隔
で並列に配置しており、各膜カートリッジ12の膜透過
側に連通させて吸引チューブ13と吸引ヘッダー管14
とを順次設けている。そして、吸引ヘッダー管14に一
端を連通させて濾液管15が設けられていて、この濾液
管15の他端は膜カートリッジ12の下部より5〜10
cm下方の適当位置で隔壁4を貫通して濾液室5内に導
かれている。濾液管15の他端部には、制御装置9aに
接続する電磁弁16が設けられている。膜カートリッジ
12の下方には、被処理水に曝気空気を供給する曝気装
置17がブロワ18に接続して設けられている。
In the membrane separation device 10, membrane cartridges 12 are arranged in parallel at an appropriate interval inside a box-shaped casing 11 having an open top and bottom. And suction header tube 14
Are sequentially provided. A filtrate tube 15 is provided so that one end thereof communicates with the suction header tube 14, and the other end of the filtrate tube 15 is 5 to 10 mm below the membrane cartridge 12.
The liquid is guided into the filtrate chamber 5 through the partition wall 4 at an appropriate position below the centrifuge. The other end of the filtrate tube 15 is provided with an electromagnetic valve 16 connected to the control device 9a. Below the membrane cartridge 12, an aeration device 17 for supplying aerated air to the water to be treated is provided connected to a blower 18.

【0016】濾液室5内には、排出管6の開口部を覆っ
て、滅菌器19を備えた消毒部20が設けられるととも
に、室5内の被処理水を消毒部20へ導くポンプ21が
設けられている。
In the filtrate chamber 5, a disinfecting section 20 having a sterilizer 19 is provided so as to cover the opening of the discharge pipe 6, and a pump 21 for guiding the water to be treated in the chamber 5 to the disinfecting section 20 is provided. Is provided.

【0017】また、装置の天部には保守管理のための開
口部22,23が形成され、それぞれに蓋22a,23
aが設けられている。以下、上記構成における作用を説
明する。
Openings 22 and 23 for maintenance management are formed in the top of the apparatus, and lids 22a and 23 are respectively provided.
a is provided. Hereinafter, the operation of the above configuration will be described.

【0018】被処理水供給管2より被処理水を導入する
と、被処理水は濾過部8を通過する間にスクリーン7な
どによってきょう雑物が除去され、次いで曝気室3内の
活性汚泥混合液に混合される。そして、被処理水は、ブ
ロワ18より曝気装置17を通じて曝気空気が供給され
る好気的条件下、曝気空気の気泡流により攪拌されつつ
活性汚泥の作用により生物学的に処理され、被処理水中
に含まれていた有機物や窒素分が除去される。
When the water to be treated is introduced from the water supply pipe 2, foreign matter is removed by a screen 7 or the like while the water to be treated passes through the filtration unit 8, and then the activated sludge mixed liquid in the aeration chamber 3 is removed. Is mixed. The water to be treated is biologically treated by the action of activated sludge while being agitated by the bubble flow of the aerated air under aerobic conditions in which the aerated air is supplied from the blower 18 through the aerator 17. The organic matter and nitrogen contained in are removed.

【0019】また、曝気室3内の活性汚泥混合液は、濾
液管15の他端を膜カートリッジ12の下部より下方の
適当位置において濾液室5に導いたことにより利用でき
る広範な自然水頭を駆動圧として、膜カートリッジ12
により固液分離される。そして、活性汚泥は室内に維持
され、濾過膜を透過した濾液は吸引チューブ13と吸引
ヘッダー管14とを経て濾液管15より濾液室5へ送ら
れる。
Further, the activated sludge mixture in the aeration chamber 3 drives a wide natural water head which can be used by guiding the other end of the filtrate pipe 15 to the filtrate chamber 5 at an appropriate position below the lower portion of the membrane cartridge 12. As pressure, the membrane cartridge 12
Is separated into solid and liquid. Then, the activated sludge is maintained in the room, and the filtrate that has passed through the filtration membrane is sent from the filtrate tube 15 to the filtrate chamber 5 through the suction tube 13 and the suction header tube 14.

【0020】このとき、曝気室3内の液位は液位計9に
より測定されていて、被処理水の流入量と濾液室5へ送
られる濾液量とのバランスより曝気室3内の液位が低下
して、膜カートリッジ12より上方の一定下限の液位L
Lに達したときは、液位計9より送られた電気信号にも
とづいて制御装置9aによって電磁弁16が閉じられ、
固液分離は停止される。そして、曝気室3内の液位が上
昇して、膜カートリッジ12より上方の一定上限の液位
HLに達したときに、制御装置9aによって電磁弁16
が開かれ、固液分離が再開される。このようにして、膜
分離装置10を活性汚泥混合液中に浸漬状態に維持しな
がら、さらに制御装置9aのタイマー機能により電磁弁
16を間欠的に開閉しつつ、固液分離が行われる。
At this time, the liquid level in the aeration chamber 3 is measured by the liquid level meter 9, and the liquid level in the aeration chamber 3 is determined based on the balance between the inflow of the water to be treated and the amount of the filtrate sent to the filtrate chamber 5. And the liquid level L at a certain lower limit above the membrane cartridge 12
When L has been reached, the solenoid valve 16 is closed by the control device 9a based on the electric signal sent from the liquid level meter 9,
The solid-liquid separation is stopped. When the liquid level in the aeration chamber 3 rises and reaches a certain upper limit liquid level HL above the membrane cartridge 12, the electromagnetic valve 16 is controlled by the control device 9a.
Is opened, and the solid-liquid separation is restarted. In this way, solid-liquid separation is performed while maintaining the membrane separator 10 in the activated sludge mixture and intermittently opening and closing the electromagnetic valve 16 by the timer function of the controller 9a.

【0021】なお、このようにして間欠的に固液分離が
行われる間、曝気室3への被処理水の流入量が多くなっ
て自然水頭が大きくなると濾過速度が大きくなり、逆
に、曝気室3への被処理水の流入量が少なくなって自然
水頭が小さくなると濾過速度が小さくなる。この結果、
被処理水の流入量の変動の影響が緩和され、被処理水を
貯留する曝気室3内の空間を小さくできる。
During the intermittent solid-liquid separation as described above, if the flow rate of the water to be treated into the aeration chamber 3 increases and the natural head increases, the filtration rate increases. When the flow rate of the water to be treated into the chamber 3 decreases and the natural head decreases, the filtration rate decreases. As a result,
The effect of the fluctuation of the inflow of the water to be treated is reduced, and the space in the aeration chamber 3 for storing the water to be treated can be reduced.

【0022】上記した間欠運転方法において、平均孔径
約0.4μm、同1μm、同3μmの精密濾過膜を使用
し、水頭を変化させて透過流束を測定したところ、運転
する間に徐々に目詰まりを生じて透過流速が低下したも
のの、いずれの濾過膜も自然水頭のみで連続運転方法に
比べて半年以上長く濾過を行うことができた。また、こ
れらの濾過膜を洗浄するに際しても、水頭差を利用して
固液分離を行う方法であるため、ポンプ等により吸引濾
過する従来の方法のように膜面堆積物が堅く緻密になら
ず、洗浄が容易であった。
In the above-mentioned intermittent operation method, the permeation flux was measured while changing the water head using a microfiltration membrane having an average pore diameter of about 0.4 μm, 1 μm and 3 μm. Although the permeation flow rate was reduced due to clogging, all of the filtration membranes were able to perform filtration using the natural head alone for more than half a year as compared with the continuous operation method. Also, when washing these filtration membranes, the solid-liquid separation is performed by utilizing the head difference, so that the membrane surface deposits do not become firm and dense as in the conventional method of suction filtration using a pump or the like. Washing was easy.

【0023】濾液室5に流入した被処理水は適宜、ポン
プ20によって消毒部19へ導かれ、滅菌器18により
消毒された後に排出管6より装置の外部へ排出される。
濾液室5に流入した被処理水が自然流下により消毒部1
9へ導かれるように装置を構成してもよい。装置のメン
テンスが必要になった時は、蓋21a,22aを開い
て、開口部21,22より作業を行う。
The water to be treated that has flowed into the filtrate chamber 5 is guided to a disinfecting section 19 by a pump 20 as appropriate, and after being disinfected by a sterilizer 18, is discharged from the discharge pipe 6 to the outside of the apparatus.
The water to be treated that has flowed into the filtrate chamber 5 is allowed to flow by gravity to the disinfection unit 1
The device may be configured to be directed to 9. When maintenance of the apparatus is required, the lids 21a and 22a are opened and work is performed through the openings 21 and 22.

【0024】[0024]

【発明の効果】以上のように本発明によれば、曝気室内
の活性汚泥混合液を室内の自然水頭を駆動圧として膜分
離装置により固液分離するようにし、その濾液を膜分離
装置の頂部より下方の適当位置において濾液管により濾
液室に送るようにしたため、ポンプを用いることなく、
室内の自然水頭を広範に利用して固液分離できる。この
とき、自然水頭の変動に合わせて濾過速度が自動的に変
化するので、被処理水流入量の変動を調整するために別
途受入槽を設けたり、膜装置の上方に大きな空間を設け
たりすることが不要になる。また、電磁弁によって曝気
室内の液位が膜分離装置より上方の一定範囲の液位に維
持されるので、膜分離装置を浸漬状態に維持できる。さ
らに、電磁弁によって膜分離装置が間欠運転されるの
で、膜面に堅い緻密な堆積物は形成されず、濾過膜の洗
浄間隔を長くできるとともに洗浄が容易になる。
As described above, according to the present invention, the activated sludge mixed liquid in the aeration chamber is solid-liquid separated by the membrane separation device using the natural head in the room as the driving pressure, and the filtrate is collected at the top of the membrane separation device. At the appropriate position below, the filtrate is sent to the filtrate chamber by the filtrate tube, without using a pump.
Solid-liquid separation can be performed using the natural head of the room widely. At this time, since the filtration speed automatically changes in accordance with the fluctuation of the natural head, a separate receiving tank is provided to adjust the fluctuation of the inflow of the water to be treated, or a large space is provided above the membrane device. It becomes unnecessary. Further, the liquid level in the aeration chamber is maintained at a certain level above the membrane separation device by the solenoid valve, so that the membrane separation device can be maintained in the immersion state. Further, since the membrane separator is operated intermittently by the solenoid valve, no hard and dense deposits are formed on the membrane surface, so that the washing interval of the filtration membrane can be lengthened and washing becomes easy.

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

【図1】本発明の一実施例の汚水処理装置の全体構成を
示した説明図である。
FIG. 1 is an explanatory diagram showing an overall configuration of a sewage treatment apparatus according to one embodiment of the present invention.

【図2】従来の汚水処理装置の全体構成を示した説明図
である。
FIG. 2 is an explanatory diagram showing an overall configuration of a conventional sewage treatment apparatus.

【符号の説明】[Explanation of symbols]

1 汚水処理装置 2 被処理水供給管 3 曝気室 4 隔壁 5 濾液室 9 液位計 9a 制御装置 10 膜分離装置 15 濾液管 16 電磁弁 DESCRIPTION OF SYMBOLS 1 Sewage treatment apparatus 2 To-be-processed water supply pipe 3 Aeration chamber 4 Partition wall 5 Filtrate chamber 9 Liquid level meter 9a Control device 10 Membrane separation device 15 Filtrate pipe 16 Solenoid valve

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) C02F 3/12 C02F 3/00 ──────────────────────────────────────────────────続 き Continued on the front page (58) Field surveyed (Int. Cl. 7 , DB name) C02F 3/12 C02F 3/00

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 被処理水供給管より導入される被処理水
を好気条件下で活性汚泥により生物学的に処理する曝気
室を設け、この曝気室の内部に室内の自然水頭を駆動圧
として活性汚泥混合液を固液分離する膜分離装置を設
け、前記曝気室と隔壁を介して分離された濾液室を設
け、前記曝気室と濾液室とを濾液管により連通し、濾液
管の一端を膜分離装置の膜透過側に接続するとともに、
他端を膜分離装置の頂部より下方の適当位置において濾
液室に連通させ、前記濾液管の他端に電磁弁を設置し、
この電磁弁を間欠開閉制御する制御手段を設け、制御装
置で曝気室内における液位を膜分離装置より上方の一定
範囲内に維持して曝気室内の自然水頭を駆動圧として膜
分離装置で活性汚泥混合液を固液分離することを特徴と
する汚水処理装置。
An aeration chamber for biologically treating treated water introduced from a treated water supply pipe with activated sludge under aerobic conditions is provided, and a natural water head in the room is driven inside the aerated chamber by a driving pressure. A membrane separation device for solid-liquid separation of the activated sludge mixed liquid is provided as the above, and the aeration chamber and a filtrate chamber separated via a partition are provided.
The aeration chamber and the filtrate chamber are connected by a filtrate tube.
Connect one end of the tube to the membrane permeation side of the membrane separation device,
The other end is communicated with the filtrate chamber at an appropriate position below the top of the membrane separation device, and an electromagnetic valve is installed at the other end of the filtrate tube,
A control means for intermittently controlling the opening and closing of the solenoid valve is provided.
To maintain the liquid level in the aeration chamber above the membrane separator.
The membrane is maintained within the range and the natural head in the aeration chamber is used as the driving pressure.
A sewage treatment apparatus characterized in that the activated sludge mixed liquid is separated into solid and liquid by a separator .
JP9316294A 1994-05-02 1994-05-02 Sewage treatment equipment Expired - Fee Related JP3181468B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9316294A JP3181468B2 (en) 1994-05-02 1994-05-02 Sewage treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9316294A JP3181468B2 (en) 1994-05-02 1994-05-02 Sewage treatment equipment

Publications (2)

Publication Number Publication Date
JPH07299491A JPH07299491A (en) 1995-11-14
JP3181468B2 true JP3181468B2 (en) 2001-07-03

Family

ID=14074879

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9316294A Expired - Fee Related JP3181468B2 (en) 1994-05-02 1994-05-02 Sewage treatment equipment

Country Status (1)

Country Link
JP (1) JP3181468B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP7016339B2 (en) * 2019-11-25 2022-02-04 Ihi運搬機械株式会社 Coal wastewater treatment method and equipment
JP2021084039A (en) * 2019-11-25 2021-06-03 Ihi運搬機械株式会社 Coal wastewater treatment method and device

Also Published As

Publication number Publication date
JPH07299491A (en) 1995-11-14

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