JP2505133Y2 - Water treatment device with integrated reaction tank and precipitation tank - Google Patents

Water treatment device with integrated reaction tank and precipitation tank

Info

Publication number
JP2505133Y2
JP2505133Y2 JP1991037105U JP3710591U JP2505133Y2 JP 2505133 Y2 JP2505133 Y2 JP 2505133Y2 JP 1991037105 U JP1991037105 U JP 1991037105U JP 3710591 U JP3710591 U JP 3710591U JP 2505133 Y2 JP2505133 Y2 JP 2505133Y2
Authority
JP
Japan
Prior art keywords
tank
reaction tank
sludge
treatment device
water treatment
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
JP1991037105U
Other languages
Japanese (ja)
Other versions
JPH0560596U (en
Inventor
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 JP1991037105U priority Critical patent/JP2505133Y2/en
Publication of JPH0560596U publication Critical patent/JPH0560596U/en
Application granted granted Critical
Publication of JP2505133Y2 publication Critical patent/JP2505133Y2/en
Anticipated expiration legal-status Critical
Expired - Lifetime 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

Description

【考案の詳細な説明】[Detailed description of the device]

【0001】[0001]

【産業上の利用分野】この考案は、上水前処理,下水3
次処理,産業廃水処理等に用いられる反応槽及び沈殿槽
の改良に関するものである。
[Industrial field of application] This invention applies to water pretreatment and sewage 3
The present invention relates to the improvement of reaction tanks and precipitation tanks used for secondary treatment, industrial wastewater treatment, etc.

【0002】[0002]

【従来の技術】排水処理の手段として、生物酸化方式の
リアクタの後段に沈殿槽を配置し、前段のリアクタから
排出される汚泥と処理液の混合物を後段の沈殿槽におい
て沈降分離させ、上澄液はオーバーフローし沈降汚泥は
再度前記リアクタに返送することが知られている。
2. Description of the Related Art As a means for treating waste water, a sedimentation tank is arranged at the rear stage of a bio-oxidation reactor, and a mixture of sludge and treated liquid discharged from the reactor at the front stage is settled and separated in the sedimentation tank at the rear stage, and the supernatant is removed. It is known that the liquid overflows and the sedimented sludge is returned to the reactor again.

【0003】前記生物酸化方式のリアクタとして、近
時、超高負荷反応槽と呼ばれる小容量で高性能の反応槽
が開発され、その結果、小型(例えば、1500φ)の
超高負荷反応槽と、大型(例えば、4000φ)の沈殿
槽とを並べて設置するようなケースが増加し、設置面積
のアンバランスのため他に転用不可能な空き地が生じた
り、立地上不釣合いとなって設置場所の選択が困難とな
る等の問題点が生じている。
Recently, a small-capacity, high-performance reaction tank called an ultra-high-load reaction tank has been developed as a bio-oxidation type reactor, and as a result, a small (for example, 1500φ) ultra-high-load reaction tank, The number of cases where large-scale (for example, 4000φ) settling tanks are installed side by side has increased, and due to imbalance of the installation area, vacant land that cannot be diverted is created, or it becomes disproportionate in terms of location and the installation location is selected. There are problems such as difficulty in

【0004】また、上記問題点を避けるため、立地条件
に応じて超高負荷反応槽と沈殿槽とを離して設置する
と、両者を繋ぐ配管が長くなり施設費や所要動力が不経
済となるという別の問題点が生じることになる。
In order to avoid the above problems, if the ultra-high load reaction tank and the precipitation tank are installed separately according to the site conditions, the piping connecting them will become long and the facility cost and required power will be uneconomical. Another problem will arise.

【0005】[0005]

【考案が解決しようとする課題】この考案は、上記2つ
の問題点を同時に解決し、最小の設置面積で効率よく小
容量の超高負荷反応槽と大容量の沈殿槽とを並設するこ
とを可能とし、敷地の有効利用を図ると共に維持管理の
容易な水処理設備を提供することを課題とするものであ
る。
The present invention solves the above two problems at the same time, and efficiently installs a small-capacity ultra-high load reaction tank and a large-capacity sedimentation tank in parallel with a minimum installation area. Therefore, it is an object of the present invention to provide a water treatment facility that enables efficient use of the site and that is easy to maintain and manage.

【0006】[0006]

【課題を解決するための手段】この考案は、上記課題を
解決するための手段を提供するものであって、大径で高
さの低い沈殿槽1の中心部に、小径で高さの高い円筒状
の生物酸化処理反応槽2を同心円状に設置し、前記沈殿
槽1内に前記反応槽2の外周と僅かに間隙Sを置いて下
部が開放された円筒状のセンターウェル3を回転自在に
配設し、前記反応槽2の底部に原水導入管4および空気
導入管5を接続すると共に、該反応槽2の上部から排出
される反応液を配管6を介して前記間隙Sに導き、か
つ、沈殿槽1の上澄液は溢流堰7からオーバーフローさ
せ、沈降汚泥は汚泥返送管8を介して前記反応槽2の底
部に還流させるようにしたことを特徴とするものであ
る。
The present invention provides a means for solving the above-mentioned problems, in which a small diameter and a high height are provided at the center of a settling tank 1 having a large diameter and a low height. A cylindrical bio-oxidation reaction tank 2 is installed concentrically, and a cylindrical center well 3 whose lower part is opened with a slight gap S from the outer circumference of the reaction tank 2 in the precipitation tank 1 is rotatable. The raw water introducing pipe 4 and the air introducing pipe 5 are connected to the bottom of the reaction tank 2, and the reaction liquid discharged from the upper part of the reaction tank 2 is introduced into the gap S through the pipe 6. Moreover, the supernatant of the settling tank 1 overflows from the overflow weir 7, and the settled sludge is returned to the bottom of the reaction tank 2 through the sludge return pipe 8.

【0007】[0007]

【実施例】図中1は大径で高さの低いドーナッツ状の沈
殿槽であって、その中心部に小径で高さの高い円筒状の
生物酸化処理反応槽2が同心円状に設置されている。こ
の反応槽2自体の構造は任意であるが、内部に上下動デ
ィスクを備え、底部から原水および空気を導入し、前記
上下動ディスクの働きにより高速に酸化処理された反応
液を上部から排出する形式の、超高負荷反応槽と呼ばれ
る公知の反応槽を用いるのが好ましい。
EXAMPLE 1 In the figure, 1 is a donut-shaped precipitation tank having a large diameter and a low height, and a cylindrical biological oxidation treatment reaction tank 2 having a small diameter and a high height is installed concentrically at the center thereof. There is. Although the structure of the reaction tank 2 itself is arbitrary, a vertical moving disk is provided inside, raw water and air are introduced from the bottom, and the reaction liquid subjected to high-speed oxidation treatment is discharged from the upper part by the function of the vertical moving disk. Preference is given to using the known reactors of the type known as ultra-high load reactors.

【0008】前記沈殿槽1内には、前記反応槽2の外周
と僅かに間隙Sを置いて下部が開放された円筒状のセン
ターウェル3が配設されている。このセンターウェル3
は回転自在であり、モータMによって減速機(図示せ
ず)を介して微速で回転駆動されるようになっている。
Inside the settling tank 1, a cylindrical center well 3 having an open lower portion is arranged with a slight gap S from the outer circumference of the reaction tank 2. This center well 3
Is rotatable, and is driven to rotate at a very low speed by a motor M via a speed reducer (not shown).

【0009】前記反応槽2の底部には原水導入管4およ
び空気導入管5が接続され、また、該反応槽2の上部に
は配管6が接続され、排出される反応液をこの配管6を
介して前記間隙Sに導くようになっている。
A raw water introducing pipe 4 and an air introducing pipe 5 are connected to the bottom of the reaction tank 2, and a pipe 6 is connected to the upper portion of the reaction tank 2 to discharge the reaction liquid through the pipe 6. It is configured to be guided to the gap S through the above.

【0010】前記沈殿槽1の外周上縁には溢流堰7が設
けられ、処理水はこの溢流堰7からオーバーフローし、
一方、沈降汚泥は汚泥返送管8を介して原水と合流し、
前記反応槽2の底部に返送されるようになっている。な
お、Pは汚泥返送用のポンプである。
An overflow weir 7 is provided on the outer peripheral upper edge of the settling tank 1, and the treated water overflows from the overflow weir 7.
On the other hand, the settled sludge merges with the raw water via the sludge return pipe 8,
It is designed to be returned to the bottom of the reaction tank 2. In addition, P is a pump for sludge return.

【0011】9は前記センターウェル3に吊り下げられ
た汚泥掻寄機であって、モータMにより回転駆動される
センターウェル3と共に微速回転し、沈殿槽1の底部に
堆積する汚泥をその傾斜に沿って中心部に掻き寄せるた
めのものであって、その構造自体は公知のとおりであ
る。
Reference numeral 9 denotes a sludge attractor suspended from the center well 3, which is slanted at a slight speed together with the center well 3 which is rotationally driven by a motor M, and sludge accumulated on the bottom of the settling tank 1 is inclined. It is for scraping along the center portion, and the structure itself is known.

【0012】[0012]

【作用】本考案は、以上のような構成を有するため、生
物酸化処理反応槽2の底部から導入される原水は、該反
応槽2内で酸化処理され、反応液は上部配管6から排出
される。
Since the present invention has the above-described structure, the raw water introduced from the bottom of the biological oxidation treatment reaction tank 2 is oxidized in the reaction tank 2 and the reaction solution is discharged from the upper pipe 6. It

【0013】この反応液は、前記反応槽2の外周とセン
ターウェル3との間隙Sに導かれ、該センターウェル3
の回転に伴い円周方向の流れが生じ、次いで下部開放端
で反転して沈殿槽1に導入され、沈降分離される。
This reaction solution is introduced into the gap S between the outer periphery of the reaction tank 2 and the center well 3, and the center well 3
A flow in the circumferential direction is generated with the rotation of, and is then inverted at the lower open end and introduced into the settling tank 1 to be separated by sedimentation.

【0014】沈降分離された上澄液は溢流堰7からオー
バーフローして処理水として排出され、底部に沈降した
汚泥は汚泥掻寄機9によって掻き寄せられ、汚泥返送管
8を経て前記反応槽2に返送されて再び生物酸化処理さ
れる。
The supernatant liquid separated by settling overflows from the overflow weir 7 and is discharged as treated water, and the sludge settling at the bottom is scraped by the sludge scraper 9 and passed through the sludge return pipe 8 to the reaction tank. It is returned to No. 2 and bio-oxidized again.

【0015】[0015]

【考案の効果】本考案によれば、大径で高さの低い沈殿
槽1と、小径で高さの高い生物酸化処理反応槽2を一体
化したことにより、最小の設置面積で効率よく小容量の
超高負荷反応槽と大容量の沈殿槽とを並設することが可
能となり、敷地の有効利用を図ることができるばかりで
なく、配管も短くて済み保守点検の維持管理の容易な水
処理設備を提供することができる。
According to the present invention, a large-diameter and low-height sedimentation tank 1 and a small-diameter, high-height biological oxidation treatment reaction tank 2 are integrated, so that a small installation area can be efficiently and compactly installed. An ultra-high-load reactor with a large capacity and a large-capacity sedimentation tank can be installed side by side, which not only enables effective use of the site but also requires short piping and allows easy maintenance for maintenance and inspection. Processing equipment can be provided.

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

【図1】本考案の一実施例の縦断面図である。FIG. 1 is a longitudinal sectional view of one embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 沈殿槽 2 生物酸化処理反応槽 3 センターウェル 4 原水導入管 5 空気導入管 6 配管 7 溢流堰 8 汚泥返送管 9 垂直バッフル板 9 汚泥掻寄機 M モータ P ポンプ S 間隙 1 Precipitation tank 2 Bio-oxidation reaction tank 3 Center well 4 Raw water introduction pipe 5 Air introduction pipe 6 Piping 7 Overflow weir 8 Sludge return pipe 9 Vertical baffle plate 9 Sludge attractor M Motor P Pump S Gap

Claims (2)

(57)【実用新案登録請求の範囲】(57) [Scope of utility model registration request] 【請求項1】 大径で高さの低い沈殿槽(1) の中心部
に、小径で高さの高い円筒状の生物酸化処理反応槽(2)
を同心円状に設置し、前記沈殿槽(1) 内に前記反応槽
(2) の外周と僅かに間隙(S) を置いて下部が開放された
円筒状のセンターウェル(3) を回転自在に配設し、前記
反応槽(2) の底部に原水導入管(4) および空気導入管
(5) を接続すると共に、該反応槽(2) の上部から排出さ
れる反応液を配管(6) を介して前記間隙(S) に導き、か
つ、沈殿槽(1) の上澄液は溢流堰(7)からオーバーフロ
ーさせ、沈降汚泥は汚泥返送管(8) を介して前記反応槽
(2) の底部に還流させるようにしたことを特徴とする反
応槽と沈殿槽を一体化した水処理装置。
1. A large-diameter, low-height settling tank (1) with a small-diameter, high-height cylindrical biooxidation reaction tank (2) at the center.
Are installed concentrically, and the reaction tank is placed in the precipitation tank (1).
A cylindrical center well (3) with an open lower part was rotatably arranged with a slight gap (S) from the outer periphery of (2), and a raw water inlet pipe (4) was installed at the bottom of the reaction tank (2). ) And air inlet pipe
(5) is connected, the reaction solution discharged from the upper part of the reaction tank (2) is introduced into the gap (S) through the pipe (6), and the supernatant of the precipitation tank (1) is The sludge that overflows from the overflow weir (7) and the settling sludge passes through the sludge return pipe (8) to the reaction tank.
A water treatment device in which a reaction tank and a precipitation tank are integrated, wherein the water is refluxed to the bottom of (2).
【請求項2】センターウェル(3) の下部に汚泥掻寄機
(9) を吊り下げたことを特徴とする請求項1記載の反応
槽と沈殿槽を一体化した水処理装置。
2. A sludge scraper at the bottom of the center well (3)
The water treatment device according to claim 1, wherein (9) is suspended.
JP1991037105U 1991-03-29 1991-03-29 Water treatment device with integrated reaction tank and precipitation tank Expired - Lifetime JP2505133Y2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1991037105U JP2505133Y2 (en) 1991-03-29 1991-03-29 Water treatment device with integrated reaction tank and precipitation tank

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1991037105U JP2505133Y2 (en) 1991-03-29 1991-03-29 Water treatment device with integrated reaction tank and precipitation tank

Publications (2)

Publication Number Publication Date
JPH0560596U JPH0560596U (en) 1993-08-10
JP2505133Y2 true JP2505133Y2 (en) 1996-07-24

Family

ID=12488318

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1991037105U Expired - Lifetime JP2505133Y2 (en) 1991-03-29 1991-03-29 Water treatment device with integrated reaction tank and precipitation tank

Country Status (1)

Country Link
JP (1) JP2505133Y2 (en)

Also Published As

Publication number Publication date
JPH0560596U (en) 1993-08-10

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