JP2000279984A - Biological treatment equipment - Google Patents

Biological treatment equipment

Info

Publication number
JP2000279984A
JP2000279984A JP9344599A JP9344599A JP2000279984A JP 2000279984 A JP2000279984 A JP 2000279984A JP 9344599 A JP9344599 A JP 9344599A JP 9344599 A JP9344599 A JP 9344599A JP 2000279984 A JP2000279984 A JP 2000279984A
Authority
JP
Japan
Prior art keywords
water
sludge
tank
treated
floating
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
JP9344599A
Other languages
Japanese (ja)
Inventor
Mikio Sato
三生男 佐藤
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.)
Sumitomo Heavy Industries Ltd
Original Assignee
Sumitomo Heavy Industries Ltd
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 Sumitomo Heavy Industries Ltd filed Critical Sumitomo Heavy Industries Ltd
Priority to JP9344599A priority Critical patent/JP2000279984A/en
Publication of JP2000279984A publication Critical patent/JP2000279984A/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

Abstract

PROBLEM TO BE SOLVED: To provide a biological treatment equipment capable of sufficiently preventing clogging of a membrane. SOLUTION: This equipment is provided with: a water treatment tank 3 into which water to be treated 2 is allowed to flow; an immersion membrane 4 immersed in the water to be treated 2 in the tank 3; suspended solid matter 8 allowed to exist in the wastewater to be treated 2 in the tank 3; an air diffuser for fluidizing the suspended solid matter 8 in the water to be treated 2 in the tank 3; biological sludge for subjecting the water to be treated 2 to biological treatment; a sludge withdrawal means for withdrawing the sludge 9 and the suspended solid matter 8 in the sludge 9 from the tank 3; a suspended solid matter separation vessel 12 for separating the sludge 9 and the suspended solid matter 8, both of which are withdrawn by the sludge withdrawal means, from each other; and a return means for returning the separated solid matter 8 in the vessel 12 to the tank 3; wherein since the sludge 9 is accumulated in the tank 3 by the membrane separation and the suspended solid matter 8 is liable to be incorporated into the sludge 9, the sludge 9 and the suspended solid matter 8 in the tank 3 are withdrawn from the tank 3 by the sludge withdrawal means and the suspended solid matter 8 is separated from the sludge 9 in the suspended solid matter separation vessel 12 and the separated solid matter 8 is returned to the water treatment tank 3 by the return means.

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、例えば下水、工業
用廃水などの有機物含有廃水を生物処理しながら浸漬膜
によって膜分離する生物処理装置に係り、より詳細には
有機性廃水中に投入される浮遊固体によって浸漬膜を洗
浄することも可能な生物処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a biological treatment apparatus for separating a wastewater containing organic substances such as sewage and industrial wastewater by membrane while immersing the wastewater in biological treatment. The present invention relates to a biological treatment apparatus that can also wash an immersion film with suspended solids.

【0002】[0002]

【従来の技術】下水、工業用廃水などの有機性廃水を生
物汚泥によって生物処理しながら浸漬膜によって膜分離
する生物処理装置は公知である。こうした生物処理装置
の一例として、特開平7−328624号公報に開示さ
れるものが知られている。この装置は、処理水槽の被処
理水中に中空糸膜を浸漬配置し、中空糸膜によって被処
理水を膜分離するものであり、さらに被処理水に微生物
固定化担体や微細な活性炭等を投入し、曝気によって微
生物固定化担体や微細な活性炭等を流動化させて、中空
糸膜の閉塞の防止を図っている。
2. Description of the Related Art A biological treatment apparatus for subjecting organic wastewater, such as sewage or industrial wastewater, to biological separation with biological sludge and separating the organic wastewater with a submerged membrane is known. As an example of such a biological treatment apparatus, one disclosed in Japanese Patent Application Laid-Open No. 7-328624 is known. This device immerses and arranges a hollow fiber membrane in the water to be treated in a treatment tank, and separates the water to be treated with the hollow fiber membrane. Further, a microorganism-immobilized carrier, fine activated carbon, and the like are added to the water to be treated. Then, the microorganism-immobilized carrier and the fine activated carbon are fluidized by aeration to prevent the hollow fiber membrane from being clogged.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、前述し
た従来の公報に記載の生物処理装置においては、中空糸
膜が比較的短期間で閉塞し、膜分離処理を長時間にわた
って継続することができなくなる場合があった。
However, in the biological treatment apparatus described in the above-mentioned conventional publication, the hollow fiber membrane is closed in a relatively short period of time, and the membrane separation cannot be continued for a long time. There was a case.

【0004】そこで、本発明は、上記事情に鑑み、膜の
閉塞を十分に防止することができる生物処理装置を提供
することを目的とする。
[0004] In view of the above circumstances, an object of the present invention is to provide a biological treatment apparatus capable of sufficiently preventing membrane blockage.

【0005】[0005]

【課題を解決するための手段】本発明者らは、上記問題
点について検討した結果、膜分離を行っているうちに担
体等が処理水槽底部の余剰汚泥中に取り込まれる場合が
あり、このため、被処理水中で流動化する担体が少なく
なり、中空糸膜の洗浄効果が次第に低下するために中空
糸膜が比較的短期間で閉塞することを見出した。そこ
で、本発明者らは、鋭意研究を進めた結果、余剰汚泥と
その中に取り込まれる担体とを分離して担体を処理水槽
内に戻すことにより、膜の洗浄効果の低下を十分に防止
できることを見出した。
Means for Solving the Problems The present inventors have studied the above problems, and as a result, during the membrane separation, carriers and the like may be taken into excess sludge at the bottom of the treated water tank. It has been found that the amount of the carrier fluidized in the water to be treated decreases, and the hollow fiber membrane is clogged in a relatively short period of time because the cleaning effect of the hollow fiber membrane gradually decreases. Thus, the present inventors have conducted intensive studies and as a result, by separating the excess sludge and the carrier taken into the sludge and returning the carrier to the treatment water tank, it is possible to sufficiently prevent the reduction of the membrane washing effect. Was found.

【0006】ここで、膜の洗浄効果の低下防止を図るた
めに余剰汚泥中に取り込まれる浮遊固体は排出する一方
で、新たな浮遊固体を補充することも考えられるが、こ
れではランニングコストが著しくかかることになる。
Here, in order to prevent the deterioration of the cleaning effect of the membrane, it is conceivable to discharge suspended solids taken into excess sludge while replenishing new suspended solids, but this significantly increases running costs. That would be.

【0007】そこで、請求項1に係る発明は、被処理水
が流入される処理水槽と、処理水槽内の被処理水中に浸
漬配置される浸漬膜と、処理水槽内の被処理水中に存在
する浮遊固体と、浮遊固体を被処理水中で流動化させる
散気装置と、被処理水を生物処理する生物汚泥とを備え
る生物処理装置において、処理水槽から余剰汚泥及び余
剰汚泥中に取り込まれる浮遊固体を引き抜く汚泥引抜き
手段と、汚泥引抜き手段によって引き抜かれた余剰汚泥
及び浮遊固体を分離する浮遊固体分離槽と、浮遊固体分
離槽の浮遊固体を処理水槽に返送する返送手段とを備え
ることを特徴とする。
Therefore, the invention according to claim 1 exists in a treatment water tank into which water to be treated flows, an immersion film immersed and disposed in the treatment water in the treatment water tank, and an immersion film in the treatment water in the treatment water tank. In a biological treatment apparatus including a suspended solid, an aerator for fluidizing the suspended solid in the water to be treated, and a biological sludge for biologically treating the water to be treated, the suspended solid taken in from the treated water tank into excess sludge and excess sludge. Sludge withdrawing means for extracting the sludge, floating solid separation tank for separating excess sludge and suspended solids withdrawn by the sludge withdrawing means, and return means for returning the suspended solids of the suspended solid separation tank to the treatment water tank. I do.

【0008】この発明によれば、散気装置によって、処
理水槽内の被処理水中で浮遊固体が流動化され、被処理
水が生物汚泥によって生物処理されながら浸漬膜によっ
て膜分離される。膜分離を継続すると、処理水槽内に余
剰汚泥が次第に溜まり、また、浮遊固体の一部が余剰汚
泥中に取り込まれる場合が生じる。このため、流動化す
る浮遊固体が減少し、浸漬膜に対する洗浄効果が低下す
る場合がある。そこで、処理水槽内の余剰汚泥及びその
中に取り込まれる浮遊固体は、汚泥引抜き手段によって
引き抜かれ、浮遊固体分離槽内に送られて余剰汚泥と浮
遊固体とが分離される。分離された浮遊固体は返送手段
によって処理水槽へと返送される。従って、処理水槽の
被処理水中で流動化する浮遊固体の量が減少しても、被
処理水中で流動化する浮遊固体の量をほぼ一定にするこ
とが可能となり、浸漬膜に対する洗浄効果をほぼ一定に
保つことが可能となる。
According to the present invention, the suspended solids are fluidized in the water to be treated in the treated water tank by the air diffuser, and the water to be treated is separated by the immersion membrane while being biologically treated by the biological sludge. When the membrane separation is continued, excess sludge gradually accumulates in the treatment water tank, and a part of the suspended solids may be taken into the excess sludge. For this reason, the amount of fluidized floating solids decreases, and the cleaning effect on the immersion film may decrease. Therefore, the excess sludge in the treated water tank and the suspended solids taken therein are withdrawn by the sludge extracting means and sent to the suspended solid separation tank, where the excess sludge and the suspended solids are separated. The separated suspended solids are returned to the treated water tank by the return means. Therefore, even if the amount of suspended solids fluidized in the water to be treated in the treated water tank decreases, the amount of suspended solids fluidized in the treated water can be made substantially constant, and the cleaning effect on the immersion film can be substantially reduced. It can be kept constant.

【0009】請求項2に係る発明においては、浮遊固体
分離槽が余剰汚泥及び浮遊固体を分離する希釈水を備え
ており、希釈水中の余剰汚泥の濃度を0.7重量%以下
とすることが可能であることが好ましい。この場合、余
剰汚泥の濃度が0.7重量%を超える場合に比べて浮遊
固体の浮上速度が向上し、浮遊固体が余剰汚泥から分離
され易くなる傾向がある。
In the invention according to claim 2, the floating solids separation tank is provided with dilution water for separating excess sludge and floating solids, and the concentration of the excess sludge in the dilution water is set to 0.7% by weight or less. Preferably it is possible. In this case, the floating speed of the suspended solids is improved as compared with the case where the concentration of the excess sludge exceeds 0.7% by weight, and the suspended solids tend to be easily separated from the excess sludge.

【0010】また、請求項3に係る発明では、希釈水と
して有機物含有廃水が用いられ、希釈水が被処理水とし
て処理水槽内に流入されることが好ましい。この場合、
有機物含有廃水は希釈水として有効に利用される。
[0010] In the invention according to claim 3, it is preferable that wastewater containing organic matter is used as the diluting water, and the diluting water flows into the treated water tank as the water to be treated. in this case,
Organic matter-containing wastewater is effectively used as dilution water.

【0011】また、請求項4に係る発明は、被処理水が
流入される処理水槽と、処理水槽内の被処理水中に浸漬
配置される浸漬膜と、処理水槽内の被処理水中に存在す
る浮遊固体と、浮遊固体を被処理水中で流動化させる散
気装置と、被処理水を生物処理する生物汚泥とを備える
生物処理装置において、処理水槽から余剰汚泥及び余剰
汚泥中の浮遊固体を引き抜く汚泥引抜き手段と、汚泥引
抜き手段によって引き抜かれた余剰汚泥及び浮遊固体を
分離する浮遊固体分離槽と、浮遊固体分離槽で分離され
た浮遊固体を回収する回収槽と、回収槽の浮遊固体を処
理水槽に返送する返送手段とを備えることを特徴とす
る。
Further, the invention according to claim 4 exists in the treatment water tank into which the treatment water flows, the immersion film immersed in the treatment water in the treatment water tank, and the treatment water in the treatment water tank. In a biological treatment apparatus including a floating solid, an aerator for fluidizing the floating solid in the water to be treated, and a biological sludge for biologically treating the water to be treated, withdrawing excess sludge and floating solids in the excess sludge from the treatment water tank. Sludge withdrawal means, floating solids separation tank for separating excess sludge and suspended solids withdrawn by sludge withdrawal means, collection tank for collecting suspended solids separated in suspended solids separation tank, and treatment of suspended solids in the collection tank And returning means for returning to the water tank.

【0012】この発明によれば、散気装置によって、処
理水槽内の被処理水中で浮遊固体が流動化され、被処理
水が生物汚泥によって生物処理されながら浸漬膜によっ
て膜分離される。膜分離を継続すると、処理水槽内に余
剰汚泥が次第に溜まり、また、浮遊固体の一部が余剰汚
泥中に取り込まれる場合が生じる。このため、流動化す
る浮遊固体が減少し、浸漬膜に対する洗浄効果が低下す
る場合がある。そこで、処理水槽内の余剰汚泥及びその
中の浮遊固体は、汚泥抜取り手段によって処理水槽から
引き抜かれ、浮遊固体分離槽内に送られて余剰汚泥と浮
遊固体とが分離される。分離された浮遊固体は回収槽に
回収される。そして、浮遊固体は、浸漬膜の膜差圧等に
応じて又は定期的に、返送手段によって回収槽の浮遊固
体が処理水槽に返送される。従って、浸漬膜の膜差圧等
に応じて、被処理水中で流動化する浮遊固体の量を調節
することが可能となり、浸漬膜に対する洗浄効果の低下
を防止することが可能となる。
According to the present invention, the suspended solids are fluidized in the water to be treated in the treated water tank by the air diffuser, and the water to be treated is separated by the immersion membrane while being biologically treated by the biological sludge. When the membrane separation is continued, excess sludge gradually accumulates in the treatment water tank, and a part of the suspended solids may be taken into the excess sludge. For this reason, the amount of fluidized floating solids decreases, and the cleaning effect on the immersion film may decrease. Therefore, the excess sludge in the treated water tank and the suspended solids therein are withdrawn from the treated water tank by the sludge extracting means and sent into the suspended solids separation tank to separate the excess sludge from the suspended solids. The separated suspended solids are collected in a collection tank. Then, the suspended solids are returned to the treated water tank by the return means according to the membrane pressure difference of the immersion membrane or periodically. Therefore, it is possible to adjust the amount of the suspended solids fluidized in the water to be treated in accordance with the differential pressure of the immersion film or the like, and it is possible to prevent a reduction in the cleaning effect on the immersion film.

【0013】[0013]

【発明の実施の形態】以下、本発明の生物処理装置の実
施形態について説明する。なお、全図中、同一又は同等
の構成要素については同一の符号を付し、重複する説明
は省略する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, an embodiment of the biological treatment apparatus of the present invention will be described. In all the drawings, the same or equivalent components are denoted by the same reference numerals, and redundant description will be omitted.

【0014】図1は、本発明の生物処理装置の一実施形
態を示す概略図である。図1に示すように、生物処理装
置30は、被処理水流入ラインL1と、被処理水流入ラ
インL1に設置される流入ポンプ1と、被処理水流入ラ
インL1を通して被処理水2が流入される処理水槽3と
を備えている。従って、処理水槽3内には被処理水2が
収容されており、被処理水2には、被処理水2中の有機
物を生物処理する生物汚泥が投入されるようになってい
る。処理水槽3内には、浸漬膜としての平板状の膜エレ
メント4が適当な間隔で複数並設されている。膜エレメ
ント4としては、被処理水2を処理水と固形物とに分離
するものであれば特に制限されず、例えば逆浸透膜、ナ
ノ膜、限外ろ過又はミクロろ過膜、中空糸膜等が用いら
れる。
FIG. 1 is a schematic view showing an embodiment of the biological treatment apparatus of the present invention. As shown in FIG. 1, the biological treatment device 30 receives the water 2 to be treated through the treated water inflow line L1, the inflow pump 1 installed in the treated water inflow line L1, and the treated water inflow line L1. And a treated water tank 3. Therefore, the treated water 2 is accommodated in the treated water tank 3, and biological sludge for biologically treating the organic matter in the treated water 2 is charged into the treated water 2. In the treatment water tank 3, a plurality of flat membrane elements 4 as immersion membranes are arranged in parallel at appropriate intervals. The membrane element 4 is not particularly limited as long as it separates the water to be treated 2 into treated water and solids. Examples thereof include a reverse osmosis membrane, a nanomembrane, an ultrafiltration or microfiltration membrane, and a hollow fiber membrane. Used.

【0015】膜エレメント4のそれぞれには集水管が接
続され、集水管は1本の排出ラインL2に接続されてい
る。排出ラインL2には吸引ポンプ5が取り付けられて
いる。また、生物処理装置30は散気装置31を備えて
いる。散気装置31は、膜エレメント4のエアスクラビ
ングを行うと共に処理水槽3の被処理水2の槽内循環流
を形成するものである。散気装置31は、例えば膜エレ
メント4の下方に配設されて気泡6を発生させる散気管
7と、散気管7にラインL6を介して接続されるブロワ
19とからなる。
A water collecting pipe is connected to each of the membrane elements 4, and the water collecting pipe is connected to one discharge line L2. A suction pump 5 is attached to the discharge line L2. Further, the biological treatment device 30 includes an air diffuser 31. The air diffuser 31 performs air scrubbing of the membrane element 4 and forms a circulating flow of the water 2 to be treated in the treatment water tank 3. The air diffuser 31 includes, for example, an air diffuser 7 disposed below the membrane element 4 to generate bubbles 6 and a blower 19 connected to the air diffuser 7 via a line L6.

【0016】被処理水2中には浮遊固体8が投入され
る。浮遊固体8としては、被処理水2中で流動化し易く
かつ比重が1より小さいものが用いられる。これは、後
述する浮遊固体分離槽12で浮遊固体8を浮上分離する
ためである。浮遊固体8の粒径は、隣り合う膜エレメン
ト4間での閉塞を起こさない大きさであれば特に制限さ
れないが、回収や流出防止の点からは1〜3mm程度が
好ましい。浮遊固体8の形状は、例えばビーズ状、粒
状、柱状、中空状でもよいが、膜表面の損傷を小さくす
る観点からはビーズ状であることが好ましい。浮遊固体
8の材質としては、例えばポリプロピレン、ポリエチレ
ン等のプラスチックが用いられる。また、浮遊固体8の
処理水槽3への添加量は例えば容積比で3〜10%程度
である。
A suspended solid 8 is introduced into the water 2 to be treated. As the suspended solid 8, a substance which is easily fluidized in the water to be treated 2 and has a specific gravity smaller than 1 is used. This is because the floating solids 8 are floated and separated in the floating solid separation tank 12 described later. The particle size of the suspended solid 8 is not particularly limited as long as it does not cause blockage between the adjacent membrane elements 4, but is preferably about 1 to 3 mm from the viewpoint of recovery and prevention of outflow. The shape of the floating solid 8 may be, for example, a bead, a grain, a column, or a hollow, but is preferably a bead from the viewpoint of reducing damage to the film surface. As a material of the floating solid 8, for example, a plastic such as polypropylene or polyethylene is used. The amount of the suspended solids 8 added to the treated water tank 3 is, for example, about 3 to 10% by volume.

【0017】また、生物処理装置30は、処理水槽3に
接続され処理水槽3内の余剰汚泥を引き抜く汚泥引抜き
ラインL3と、汚泥引抜きラインL3に設置される汚泥
引抜きポンプ10と、被処理水2の水位を調節するレベ
ル調節計(LS)11とを備えており、汚泥引抜きポン
プ10により汚泥引抜きラインL3を通して余剰汚泥が
処理水槽3から引き抜かれるようになっている。余剰汚
泥は、処理水槽3内の被処理水2中の余剰汚泥濃度を一
定値(例えば1.5〜2重量%)に保つように引き抜か
れる。なお、汚泥引抜きラインL3と、汚泥引抜きポン
プ10とによって汚泥引抜き手段が構成されている。
The biological treatment apparatus 30 includes a sludge withdrawal line L3 connected to the treatment water tank 3 for removing excess sludge in the treatment water tank 3, a sludge withdrawal pump 10 installed on the sludge withdrawal line L3, And a level controller (LS) 11 for adjusting the water level of the wastewater. The sludge withdrawal pump 10 allows excess sludge to be withdrawn from the treated water tank 3 through the sludge withdrawal line L3. Excess sludge is extracted so as to maintain the concentration of excess sludge in the water 2 to be treated in the treatment water tank 3 at a constant value (for example, 1.5 to 2% by weight). In addition, the sludge extraction line L3 and the sludge extraction pump 10 constitute sludge extraction means.

【0018】汚泥引抜きラインL3には、余剰汚泥9と
その中の浮遊固体8とを分離する浮遊固体分離槽12が
接続されている。浮遊固体分離槽12の内部は希釈水1
3で満たされ、希釈水13は余剰汚泥9を希釈し、余剰
汚泥9と浮遊固体8とを分離するものである。希釈水1
3としては、工業用水等を用いてもよいが、下水、工業
用廃水等の原水(有機物含有廃水)を用いることが好ま
しい。そのためには、浮遊固体分離槽12には、原水を
希釈水13として流入する原水供給ラインL4が接続さ
れ、原水供給ラインL4には原水ポンプ14が設置され
ている。
The sludge withdrawal line L3 is connected to a floating solid separation tank 12 for separating excess sludge 9 and floating solids 8 therein. The inside of the floating solid separation tank 12 contains dilution water 1
3, the dilution water 13 dilutes the excess sludge 9 and separates the excess sludge 9 from the suspended solids 8. Dilution water 1
As 3, industrial water or the like may be used, but it is preferable to use raw water (organic matter-containing wastewater) such as sewage or industrial wastewater. To this end, a raw water supply line L4 for flowing raw water as dilution water 13 is connected to the suspended solid separation tank 12, and a raw water pump 14 is installed in the raw water supply line L4.

【0019】浮遊固体分離槽12内には、原水供給ライ
ンL4及び汚泥引抜きラインL3に接続される混合容器
15が固定されている。混合容器15としては、上部に
開口を有するものを用いることが好ましい。このような
容器15を用いるのは、浮遊固体8が余剰汚泥9中に取
り込まれたまま排出されるのを確実に防止するためであ
る。また、浮遊固体分離槽12の上部12aは、分離さ
れた浮遊固体8を上部に密集させる観点から、浮遊固体
分離槽12の上部12aはコーン状となっていることが
好ましい。
A mixing vessel 15 connected to the raw water supply line L4 and the sludge extraction line L3 is fixed in the suspended solid separation tank 12. As the mixing container 15, it is preferable to use one having an opening at the top. The use of such a container 15 is for surely preventing the suspended solids 8 from being discharged while being taken in the excess sludge 9. In addition, the upper portion 12a of the floating solid separation tank 12 preferably has a cone shape from the viewpoint of densely separating the separated floating solids 8 at the upper portion.

【0020】さらに、浮遊固体分離槽12の底部12b
には、余剰汚泥9を抜き出す余剰汚泥排出ラインL5が
接続され、余剰汚泥排出ラインL5には抜出し弁16が
設置されている。なお、浮遊固体分離槽12の底部12
bの形状は、余剰汚泥9を下部に密集させる点からコー
ン状であることが好ましい。
Further, the bottom 12b of the floating solid separation tank 12
Is connected to a surplus sludge discharge line L5 for extracting surplus sludge 9, and a discharge valve 16 is installed in the surplus sludge discharge line L5. The bottom 12 of the floating solid separation tank 12
The shape of b is preferably cone-shaped from the point that the excess sludge 9 is concentrated at the lower part.

【0021】また、上述した被処理水流入ラインL1は
浮遊固体分離槽12に接続され、流入ポンプ1によって
浮遊固体分離槽12で分離された浮遊固体8が処理水槽
3内に返送され、希釈水13が被処理水2として処理水
槽3内に流入される。なお、被処理水流入ラインL1
と、流入ポンプ1とによって浮遊固体8の返送手段が構
成されている。
The above-mentioned treated water inflow line L1 is connected to a suspended solid separation tank 12, and the suspended solids 8 separated in the suspended solid separation tank 12 by the inflow pump 1 are returned to the treated water tank 3 to be diluted with dilution water. 13 flows into the treated water tank 3 as the water to be treated 2. In addition, the to-be-processed water inflow line L1
And the inflow pump 1 constitute a means for returning the suspended solids 8.

【0022】次に、前述した構成の生物処理装置30の
動作について説明する。
Next, the operation of the biological treatment apparatus 30 having the above-described configuration will be described.

【0023】まず流入ポンプ1が作動され、被処理水流
入ラインL1を通して被処理水2が処理水槽3内に流入
される。一方、ブロワ19が作動されラインL6に空気
が供給され散気管7から気泡6が発生させられる。これ
により処理水槽3内の被処理水2中では槽内循環流が形
成され、それに伴って浮遊固体8が流動化する。浮遊固
体8は、膜エレメント4間を通過しながら膜面を擦りつ
けて洗浄し、膜面の閉塞を防止する。このとき、被処理
水2は生物汚泥によって生物処理される。他方、吸引ポ
ンプ5が作動され、膜エレメント4によって被処理水2
が膜分離され、膜分離による処理水は、膜エレメント4
から集水管及び排出ラインL2を通して処理水槽3から
排出される。このとき、被処理水2の吸引により処理水
槽3内の液位が下がるため、液位を一定に保つようレベ
ル調節計11で測定された液位に基いて被処理水2が処
理水槽3内に供給される。
First, the inflow pump 1 is operated, and the water to be treated 2 flows into the treated water tank 3 through the treated water inflow line L1. On the other hand, the blower 19 is operated, air is supplied to the line L6, and bubbles 6 are generated from the air diffuser 7. As a result, a circulating flow in the tank is formed in the water to be treated 2 in the treated water tank 3, and the floating solids 8 are fluidized accordingly. The suspended solids 8 are washed by rubbing the membrane surface while passing between the membrane elements 4 to prevent blockage of the membrane surface. At this time, the water to be treated 2 is biologically treated with biological sludge. On the other hand, the suction pump 5 is operated, and the water
Is subjected to membrane separation, and the treated water by the membrane separation is separated into membrane elements 4
From the treated water tank 3 through a water collecting pipe and a discharge line L2. At this time, since the liquid level in the treated water tank 3 is lowered by the suction of the treated water 2, the treated water 2 is stored in the treated water tank 3 based on the liquid level measured by the level controller 11 so as to keep the liquid level constant. Supplied to

【0024】こうして処理水槽3内の被処理水2が生物
汚泥によって生物処理されながら膜エレメント4によっ
て膜分離されると、処理水槽3内に余剰汚泥が次第に溜
まり、浮遊固体8の一部が余剰汚泥中に取り込まれる場
合がある。このため、流動化する浮遊固体8が減少する
場合があり、これでは膜エレメント4の膜面に対する洗
浄効果が低下する。
When the water 2 to be treated in the treated water tank 3 is subjected to membrane separation by the membrane element 4 while being biologically treated by the biological sludge, surplus sludge gradually accumulates in the treated water tank 3, and a part of the suspended solids 8 becomes surplus. May be taken into sludge. For this reason, the amount of the floating solids 8 to be fluidized may decrease, and in this case, the cleaning effect on the membrane surface of the membrane element 4 decreases.

【0025】そこで、汚泥引抜きポンプ10が作動さ
れ、処理水槽3内の余剰汚泥濃度が一定濃度(例えば
1.5〜2重量%)となるように余剰汚泥及びその中に
取り込まれる浮遊固体8が処理水槽3から汚泥引抜きラ
インL3を通して引き抜かれ、浮遊固体分離槽12の混
合容器15内に供給される。このとき、浮遊固体分離槽
12において、希釈水13中の余剰汚泥9の濃度が一定
濃度(好ましくは0.7重量%)以下になるように、抜
出し弁16を開くことで余剰汚泥9が余剰汚泥排出ライ
ンL5を通して抜き出される。抜出し弁16は、汚泥引
抜きポンプ10に連動して開かれる。このとき、浮遊固
体分離槽12から排出される希釈水13を補充するよ
う、混合容器15内には原水供給ラインL4から原水が
供給される。
Then, the sludge withdrawing pump 10 is operated, and the excess sludge and the suspended solids 8 taken into the excess sludge are adjusted so that the concentration of the excess sludge in the treatment water tank 3 becomes constant (for example, 1.5 to 2% by weight). It is withdrawn from the treated water tank 3 through the sludge withdrawal line L3 and supplied into the mixing container 15 of the suspended solids separation tank 12. At this time, in the floating solid separation tank 12, the excess sludge 9 is opened by opening the extraction valve 16 so that the concentration of the excess sludge 9 in the dilution water 13 becomes a certain concentration (preferably 0.7% by weight) or less. It is extracted through the sludge discharge line L5. The extraction valve 16 is opened in conjunction with the sludge extraction pump 10. At this time, raw water is supplied from the raw water supply line L4 into the mixing vessel 15 so as to replenish the dilution water 13 discharged from the floating solid separation tank 12.

【0026】こうして余剰汚泥9及びその中に取り込ま
れる浮遊固体8が浮遊固体分離槽12内に供給される
と、余剰汚泥9と浮遊固体8とが分離され、分離された
浮遊固体8は浮上して浮遊固体分離槽12内の最上部に
密集する。密集した浮遊固体8は、希釈水13と共に被
処理水流入ラインL1を通して処理水槽3に返送され
る。従って、余剰汚泥9中に浮遊固体8が取り込まれる
ことにより処理水槽3の被処理水2中で流動化する浮遊
固体8の量が減少しても、被処理水2中で流動化する浮
遊固体8の量をほぼ一定に保つことが可能となり、膜エ
レメント4に対する膜面洗浄効果がほぼ一定に保たれ
る。このため、膜の閉塞が十分に防止され、膜分離処理
を長時間にわたって継続することができる。
When the excess sludge 9 and the floating solids 8 taken in the sludge 9 are supplied into the floating solid separation tank 12, the excess sludge 9 and the floating solids 8 are separated, and the separated floating solids 8 float. To the top of the floating solids separation tank 12. The dense floating solids 8 are returned to the treated water tank 3 through the treated water inflow line L1 together with the dilution water 13. Therefore, even if the amount of floating solids 8 fluidized in the water 2 to be treated in the treated water tank 3 is reduced by the incorporation of the suspended solids 8 into the excess sludge 9, the floating solids fluidized in the water 2 to be treated are reduced. 8 can be kept almost constant, and the membrane surface cleaning effect on the membrane element 4 can be kept almost constant. Therefore, blockage of the membrane is sufficiently prevented, and the membrane separation process can be continued for a long time.

【0027】次に、本発明の生物処理装置の第2実施形
態について説明する。
Next, a second embodiment of the biological treatment apparatus of the present invention will be described.

【0028】図2は、本発明の生物処理装置の第2実施
形態を示す概略図である。図2に示すように、第2実施
形態の生物処理装置40は、次の点で第1実施形態の生
物処理装置と異なる。
FIG. 2 is a schematic view showing a second embodiment of the biological treatment apparatus of the present invention. As shown in FIG. 2, the biological treatment device 40 of the second embodiment differs from the biological treatment device of the first embodiment in the following points.

【0029】即ち、汚泥引抜きラインL3が原水供給ラ
インL4に接続され、被処理水流入ラインL1が浮遊固
体分離槽12の下部12bに接続されている。ここで、
被処理水流入ラインL1は、浮遊固体分離槽12内の液
位を保持するために最上部12aが浮遊固体分離槽12
内の液位とほぼ等しくなっている。さらに、浮遊固体分
離槽12には、回収ラインL8を介して、浮遊固体分離
槽12内の浮遊固体8を回収する回収槽18が接続され
ている。回収槽18には、浮遊固体8を処理水槽3に返
送する返送ラインL7が接続され、返送ラインL7には
返送ポンプ20が設置されている。
That is, the sludge extraction line L 3 is connected to the raw water supply line L 4, and the treated water inflow line L 1 is connected to the lower portion 12 b of the suspended solid separation tank 12. here,
The to-be-processed water inflow line L1 has an uppermost portion 12a in the floating solids separation tank 12 in order to maintain the liquid level in the floating solids separation tank 12.
It is almost equal to the liquid level inside. Furthermore, a recovery tank 18 for recovering the floating solids 8 in the floating solids separation tank 12 is connected to the floating solids separation tank 12 via a recovery line L8. A return line L7 for returning the suspended solids 8 to the treated water tank 3 is connected to the recovery tank 18, and a return pump 20 is installed on the return line L7.

【0030】従って、処理水槽3内の余剰汚泥9及びそ
の中に取り込まれた浮遊固体8は、汚泥引抜きラインL
3を通して原水供給ラインL4に送られ、原水供給ライ
ンL4内で原水によって希釈されながら浮遊固体分離槽
12内の混合容器15内に導入される。すると、浮遊固
体8は余剰汚泥9から分離されて浮上する。浮上した浮
遊固体8は、回収ラインL8を通して回収槽18に送ら
れる。回収槽18に回収された浮遊固体8は、膜エレメ
ント4の膜差圧が一定値以上になったとき又は定期的に
返送ラインL7を通して処理水槽3内に返送される。従
って、被処理水2中で流動化する浮遊固体8の量を調節
することが可能となり、膜エレメント4に対する膜面洗
浄効果の低下を防止することができる。そのため、膜分
離処理を長時間にわたって継続することができる。
Therefore, the excess sludge 9 in the treated water tank 3 and the suspended solids 8 taken in the sludge are converted into the sludge withdrawal line L
The raw water is sent to the raw water supply line L4 through 3 and is introduced into the mixing vessel 15 in the floating solid separation tank 12 while being diluted by the raw water in the raw water supply line L4. Then, the suspended solids 8 are separated from the excess sludge 9 and float. The suspended solids 8 that have floated are sent to the collection tank 18 through the collection line L8. The suspended solids 8 collected in the collection tank 18 are returned to the treated water tank 3 through the return line L7 when the membrane differential pressure of the membrane element 4 becomes equal to or higher than a certain value or periodically. Therefore, it is possible to adjust the amount of the floating solids 8 fluidized in the water 2 to be treated, and it is possible to prevent a reduction in the membrane surface cleaning effect on the membrane element 4. Therefore, the membrane separation process can be continued for a long time.

【0031】なお、本発明は、前述した実施形態に限定
されるものではない。例えば前述の実施形態では原水を
希釈水13として用い、希釈水13を被処理水2として
用いているが、原水を被処理水2として用いてもよい。
The present invention is not limited to the above embodiment. For example, in the above-described embodiment, the raw water is used as the diluting water 13 and the diluting water 13 is used as the water to be treated 2. However, the raw water may be used as the water 2 to be treated.

【0032】(参考例1)浮遊固体として、比重0.8
5、平均粒径3mmのポリプロピレンからなるビーズ状
の浮遊固体を用いた場合を例として、余剰汚泥を希釈す
ることにより浮遊固体が分離されるか否かを調べた。こ
の浮遊固体は、処理水槽の容量に対し3%添加した。そ
して、処理水槽で得られた合成下水汚泥を水道水で希釈
して汚泥濃度0.1〜2.0重量%の混合液をそれぞれ
作り出し、浮遊固体が浮上する速度を測定した。その結
果を図3に示す。なお、浮上速度は以下のようにして測
定した。即ち、浮遊固体(ビーズ)1個をはさみでつか
んで3lビーカー(高さ20cm)の最下部にもってい
き、浮遊固体を離した時点から20cmの高さを浮上し
てくる時間をストップウォッチで計測し、その時間か
ら、その汚泥濃度における浮遊固体の浮上速度を測定し
た。
Reference Example 1 As a suspended solid, specific gravity 0.8
5. By taking as an example the case of using a bead-shaped floating solid made of polypropylene having an average particle diameter of 3 mm, it was examined whether or not the floating solid was separated by diluting excess sludge. This suspended solid was added in an amount of 3% based on the capacity of the treatment water tank. Then, the synthetic sewage sludge obtained in the treated water tank was diluted with tap water to produce respective mixed solutions having a sludge concentration of 0.1 to 2.0% by weight, and the speed at which the suspended solids floated was measured. The result is shown in FIG. In addition, the floating speed was measured as follows. That is, one floating solid (bead) is grasped with scissors and brought to the bottom of a 3 l beaker (height: 20 cm), and the time of floating from the point at which the floating solid is released to a height of 20 cm is measured with a stopwatch. From that time, the floating speed of the suspended solid at that sludge concentration was measured.

【0033】図3に示すように、1.3重量%以下で
は、浮遊固体は浮上しないで汚泥中に溜まるが、汚泥濃
度が低下するにつれて次第に浮上速度が大きくなり、浮
遊固体が汚泥から分離し易くなることが分かった。特
に、汚泥濃度が0.7重量%以下で浮遊固体が汚泥から
分離しやすくなることが分かった。
As shown in FIG. 3, when the content is less than 1.3% by weight, the suspended solid does not float and accumulates in the sludge, but as the sludge concentration decreases, the floating speed gradually increases, and the suspended solid separates from the sludge. It turned out to be easier. In particular, it was found that when the sludge concentration was 0.7% by weight or less, the suspended solids were easily separated from the sludge.

【0034】[0034]

【発明の効果】以上説明したように本発明の生物処理装
置によれば、処理水槽内の余剰汚泥中に浮遊固体が取り
込まれる場合でも、被処理水中で流動化する浮遊固体の
量の減少が防止される。このため、浸漬膜に対する洗浄
効果の低下が防止され、膜分離処理を長時間にわたって
継続することができる。
As described above, according to the biological treatment apparatus of the present invention, even when the suspended solids are taken into the excess sludge in the treated water tank, the amount of the suspended solids fluidized in the treated water is reduced. Is prevented. For this reason, a decrease in the cleaning effect on the immersion film is prevented, and the membrane separation process can be continued for a long time.

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

【図1】本発明の生物処理装置の一実施形態を示す概略
図である。
FIG. 1 is a schematic view showing an embodiment of the biological treatment device of the present invention.

【図2】本発明の生物処理装置の他の実施形態を示す概
略図である。
FIG. 2 is a schematic view showing another embodiment of the biological treatment device of the present invention.

【図3】実施例1における浮遊固体の浮上速度と汚泥濃
度との関係を示すグラフである。
FIG. 3 is a graph showing the relationship between the floating speed of suspended solids and sludge concentration in Example 1.

【符号の説明】[Explanation of symbols]

1…流入ポンプ(返送手段)、2…被処理水、3…処理
水槽、4…膜エレメント(浸漬膜)、7…散気管(散気
装置)、8…浮遊固体、9…余剰汚泥、10…汚泥引抜
きポンプ(汚泥引抜き手段)、12…浮遊固体分離槽、
13…希釈水、L6…ライン(散気装置)、18…回収
槽、19…ブロワ(散気装置)、20…返送ポンプ(返
送手段)、30…生物処理装置、31…散気装置、L1
…被処理水流入ライン(返送手段)、L3…汚泥引抜き
ライン(汚泥引抜き手段)、L7…返送ライン(返送手
段)。
DESCRIPTION OF SYMBOLS 1 ... Inflow pump (return means), 2 ... Water to be treated, 3 ... Treatment tank, 4 ... Membrane element (immersion membrane), 7 ... Aeration tube (Aerator), 8 ... Floating solid, 9 ... Excess sludge, 10 ... Sludge extraction pump (sludge extraction means), 12 ... Floating solid separation tank,
13: dilution water, L6: line (aerator), 18: recovery tank, 19: blower (aerator), 20: return pump (return means), 30: biological treatment device, 31: air diffuser, L1
... inflow line for treated water (return means), L3 ... sludge extraction line (sludge extraction means), L7 ... return line (return means).

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D003 AA12 AB01 BA02 CA02 CA04 CA10 DA07 DA09 DA11 DA14 DA21 DA29 DA30 EA01 EA28 EA30 FA05 4D006 GA03 GA06 GA07 HA01 HA41 JA19Z JA53Z KA31 KC02 KC17 KC18 KE14R KE21P KE21Q MA01 MA03 MB02 PA05 PB08 PB70 PC64  ──────────────────────────────────────────────────続 き Continued on front page F-term (reference) 4D003 AA12 AB01 BA02 CA02 CA04 CA10 DA07 DA09 DA11 DA14 DA21 DA29 DA30 EA01 EA28 EA30 FA05 4D006 GA03 GA06 GA07 HA01 HA41 JA19Z JA53Z KA31 KC02 KC17 KC18 KE14R KE21 P03 MB05 PB70 PC64

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 被処理水が流入される処理水槽と、 前記処理水槽内の前記被処理水中に浸漬配置される浸漬
膜と、 前記処理水槽内の前記被処理水中に存在する浮遊固体
と、 前記浮遊固体を前記被処理水中で流動化させる散気装置
と、 前記被処理水を生物処理する生物汚泥と、 を備える生物処理装置において、 前記処理水槽から余剰汚泥及び前記余剰汚泥中に取り込
まれた前記浮遊固体を引き抜く汚泥引抜き手段と、 前記汚泥引抜き手段によって引き抜かれた前記余剰汚泥
及び前記浮遊固体を分離する浮遊固体分離槽と、 前記浮遊固体分離槽で分離された前記浮遊固体を前記処
理水槽に返送する返送手段と、を備えることを特徴とす
る生物処理装置。
A treatment tank into which the treatment water flows, an immersion film immersed in the treatment water in the treatment tank, and a suspended solid present in the treatment water in the treatment water tank. An aeration device for fluidizing the suspended solids in the water to be treated, and a biological sludge for biologically treating the water to be treated, wherein the biological sludge is taken into the excess sludge and the excess sludge from the treated water tank. Sludge withdrawing means for withdrawing the suspended solids, a floating solids separation tank for separating the excess sludge and the floating solids withdrawn by the sludge withdrawing means, and the treatment of the floating solids separated by the floating solids separation tank. A biological treatment apparatus, comprising: a return unit that returns the water to a water tank.
【請求項2】 前記浮遊固体分離槽が前記余剰汚泥及び
前記浮遊固体を分離する希釈水を備えており、前記希釈
水中の前記余剰汚泥の濃度を0.7重量%以下とするこ
とが可能であることを特徴とする請求項1に記載の生物
処理装置。
2. The floating solids separation tank is provided with dilution water for separating the excess sludge and the floating solids, and the concentration of the excess sludge in the dilution water can be 0.7% by weight or less. The biological treatment apparatus according to claim 1, wherein the biological treatment apparatus is provided.
【請求項3】 前記希釈水として有機物含有廃水が用い
られ、前記希釈水が前記被処理水として前記処理水槽内
に流入されることを特徴とする請求項2に記載の生物処
理装置。
3. The biological treatment apparatus according to claim 2, wherein an organic matter-containing wastewater is used as the dilution water, and the dilution water flows into the treatment water tank as the water to be treated.
【請求項4】 被処理水が流入される処理水槽と、 前記処理水槽内の前記被処理水中に浸漬配置される浸漬
膜と、 前記処理水槽内の前記被処理水中に存在する浮遊固体
と、 前記浮遊固体を前記被処理水中で流動化させる散気装置
と、 前記被処理水を生物処理する生物汚泥と、を備える生物
処理装置において、 前記処理水槽から余剰汚泥及び前記余剰汚泥中に取り込
まれた前記浮遊固体を引き抜く汚泥引抜き手段と、 前記汚泥引抜き手段によって引き抜かれた前記余剰汚泥
及び前記浮遊固体を分離する浮遊固体分離槽と、 前記浮遊固体分離槽で分離された前記浮遊固体を回収す
る回収槽と、 前記回収槽の前記浮遊固体を前記処理水槽に返送する返
送手段と、を備えることを特徴とする生物処理装置。
4. A treated water tank into which the treated water flows, an immersion film immersed and disposed in the treated water in the treated water tank, and a floating solid present in the treated water in the treated water tank. In a biological treatment apparatus comprising: an aerator for fluidizing the suspended solids in the water to be treated; and biological sludge for biologically treating the water to be treated, the biological fluid is taken into the excess sludge and the excess sludge from the treated water tank. Sludge withdrawing means for withdrawing the suspended solids, a floating solid separation tank for separating the excess sludge and the floating solids withdrawn by the sludge withdrawing means, and collecting the floating solids separated in the floating solid separation tank. A biological treatment apparatus comprising: a recovery tank; and a return unit that returns the suspended solids in the recovery tank to the treated water tank.
JP9344599A 1999-03-31 1999-03-31 Biological treatment equipment Pending JP2000279984A (en)

Priority Applications (1)

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Country Link
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002113484A (en) * 2000-10-10 2002-04-16 Hitachi Zosen Corp Water cleaning treatment method and apparatus therefor
JP2017104833A (en) * 2015-12-11 2017-06-15 三菱重工環境・化学エンジニアリング株式会社 Biological treatment apparatus

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002113484A (en) * 2000-10-10 2002-04-16 Hitachi Zosen Corp Water cleaning treatment method and apparatus therefor
JP2017104833A (en) * 2015-12-11 2017-06-15 三菱重工環境・化学エンジニアリング株式会社 Biological treatment apparatus
WO2017098941A1 (en) * 2015-12-11 2017-06-15 三菱重工環境・化学エンジニアリング株式会社 Biological treatment device
KR20180017199A (en) * 2015-12-11 2018-02-20 미츠비시 쥬코 칸쿄 카가쿠 엔지니어링 가부시키가이샤 Biological treatment device
CN107848850A (en) * 2015-12-11 2018-03-27 三菱重工环境·化学工程株式会社 Biological treatment device
KR102167816B1 (en) * 2015-12-11 2020-10-20 미츠비시 쥬코 칸쿄 카가쿠 엔지니어링 가부시키가이샤 Biological treatment device

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