JPH08243585A - Aerator - Google Patents

Aerator

Info

Publication number
JPH08243585A
JPH08243585A JP7054827A JP5482795A JPH08243585A JP H08243585 A JPH08243585 A JP H08243585A JP 7054827 A JP7054827 A JP 7054827A JP 5482795 A JP5482795 A JP 5482795A JP H08243585 A JPH08243585 A JP H08243585A
Authority
JP
Japan
Prior art keywords
water
treated
pipe
air
oxygen
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
JP7054827A
Other languages
Japanese (ja)
Inventor
Yasuyuki Yoshida
泰之 吉田
Satoshi Oketani
智 桶谷
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 JP7054827A priority Critical patent/JPH08243585A/en
Publication of JPH08243585A publication Critical patent/JPH08243585A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)

Abstract

PURPOSE: To provide an aerator exhibiting high oxygen dissolving efficiency and oxygen moving efficiency, excellent in durability and which is easily maintained and controlled. CONSTITUTION: An aerator 17 is formed with a suction pipe 21 vertically arranged at the definite depth of the water 16 to be treated, an air diffuser pipe 24 opened at the upper part in the suction pipe 21 and supplying air 23 and a pump 25 at the lower part of the suction pipe 21 and allowing the air 23 and water 16 to flow downward in the suction pipe 21. A tap 22 with the diameter gradually decreased downward is furnished at the upper end of the suction pipe 21, and a shaft 30 for driving the impeller of the pump 25 is extended upward through the inside of the suction pipe 21 and connected to a motor 31 above the water 16 surface.

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、下水処理、産業廃水処
理などの水処理に使用するための効率的な曝気装置に関
する。
FIELD OF THE INVENTION The present invention relates to an efficient aerator for use in water treatment such as sewage treatment and industrial wastewater treatment.

【0002】[0002]

【従来の技術】従来、下水処理、産業廃水処理などの水
処理においては活性汚泥法などが行われている。活性汚
泥法では、一般に、沈砂池および最初沈殿池を経た被処
理水を曝気槽に導入し、槽内に設置した散気板などの曝
気装置で曝気を行って、槽内の活性汚泥と攪拌混合しつ
つ酸素を供給することにより、被処理水中のBODや窒
素分などを活性汚泥の作用によって除去している。そし
て、曝気槽内の活性汚泥混合水の一部を最終沈殿池に導
いて活性汚泥を沈降させ、最終沈殿池内の上澄水を消毒
設備に送って消毒したものを処理水として放流してい
る。
2. Description of the Related Art Conventionally, an activated sludge method or the like has been performed in water treatment such as sewage treatment and industrial wastewater treatment. In the activated sludge method, generally, the water to be treated that has passed through the sand basin and the first sedimentation basin is introduced into the aeration tank, and aeration is performed with an aeration device such as a diffuser installed in the tank to agitate the activated sludge in the tank. By supplying oxygen while mixing, BOD and nitrogen content in the water to be treated are removed by the action of activated sludge. Then, a part of the activated sludge mixed water in the aeration tank is guided to the final settling basin to settle the activated sludge, and the supernatant water in the final settling basin is sent to a disinfection facility and discharged as treated water.

【0003】ところで、従来の曝気槽は深さ5m程度で
あったが、容量の増大が必要となった場合は深層化で対
処せざるを得ないことが多く、また、深層化すると酸素
の溶解量が増大することから、最近では、深さ5m以
上、たとえば深さ10〜20mの深層曝気槽と呼ばれる
ものや、深さ100m程度の超深層曝気槽と呼ばれるも
のが見られるようになった。このような深層あるいは超
深層の曝気槽においては、散気板などの従来の曝気装置
では酸素供給能力・攪拌能力とも十分ではなく、また、
ブロワの吐出圧が非常に大きくなって曝気装置の動力効
率が低くなるため、種々の提案がなされている。
By the way, the conventional aeration tank has a depth of about 5 m, but when it is necessary to increase the capacity, it is unavoidable to deal with it by deepening the depth, and when deepening the depth, it dissolves oxygen. Due to the increase in the amount, what is called a deep layer aeration tank having a depth of 5 m or more, for example, a depth of 10 to 20 m, and an ultra deep layer aeration tank having a depth of about 100 m have come to be seen recently. In such a deep or super deep aeration tank, the conventional aeration device such as a diffuser plate does not have sufficient oxygen supply ability and stirring ability.
Various proposals have been made because the discharge pressure of the blower becomes very large and the power efficiency of the aerator becomes low.

【0004】たとえば、図3および図4に示したよう
な、ディープシャフトと呼ばれる曝気槽が知られてい
る。ディープシャフト1は、下降流路2および上昇流路
3からなるシャフト4とヘッドタンク5とにより構成さ
れており、ディープシャフト1内の活性汚泥混合液6
は、下降流路2を下降し、シャフト底部4aで反転し、
上昇流路3を上昇し、ヘッドタンク5を経由して再び下
降流路2に戻る循環流を形成する。7は原水供給管、8
は脱気設備へ至る送水管、9は汚泥返送管である。
For example, an aeration tank called a deep shaft as shown in FIGS. 3 and 4 is known. The deep shaft 1 is composed of a shaft 4 composed of a descending flow path 2 and an ascending flow path 3 and a head tank 5, and an activated sludge mixed liquid 6 in the deep shaft 1 is formed.
Descends through the descending passage 2 and inverts at the shaft bottom 4a,
A circulation flow that rises in the ascending passage 3 and returns to the descending passage 2 via the head tank 5 is formed. 7 is a raw water supply pipe, 8
Is a water supply pipe to the degassing equipment, and 9 is a sludge return pipe.

【0005】図3に示したエアリフト方式のディープシ
ャフトでは、下降流路2の上端は活性汚泥混合液6の液
面下に開口し、給気手段としてのコンプレッサ10に接
続する散気管10a,10bがそれぞれ下降流路2と上
昇流路3の中程まで導かれている。このような構成にお
いて、散気管10bより上昇流路3に空気を吹き込んで
そのエアリフト作用により上昇流路3内に上昇液流を生
起して、この上昇液流とこれに伴い生起される下降流路
2内の下降液流とで、上昇流路3と下降流路2とにわた
る循環液流を生起し、液循環が安定したところで散気管
10aより下降流路2内に水処理用の空気を吹き込んで
いる。
In the air-lift type deep shaft shown in FIG. 3, the upper end of the descending flow path 2 opens below the liquid surface of the activated sludge mixed liquid 6 and is connected to a compressor 10 as an air supply means. Are led to the middle of the descending flow path 2 and the ascending flow path 3, respectively. In such a configuration, air is blown into the ascending flow path 3 from the air diffusing pipe 10b to generate an ascending liquid flow in the ascending flow path 3 by the air lift action, and this ascending liquid flow and the descending flow caused thereby. With the descending liquid flow in the passage 2, a circulating liquid flow extending over the ascending flow path 3 and the descending flow path 2 is generated, and when the liquid circulation is stable, air for water treatment is supplied from the diffuser pipe 10a into the descending flow path 2. It is blowing.

【0006】図4に示したポンプ方式のディープシャフ
トでは、下降流路2はその上端部11がヘッドタンク5
より上方に位置するように配置され、この上端部11と
ヘッドタンク5の内部とを連結する管路12に循環ポン
プ13が介装されている。給気手段としてのブロワ14
に接続する散気管14aは下降流路2の内部に導かれて
いる。このような構成において、循環用ポンプ13によ
りヘッドタンク5内の活性汚泥混合液6を下降流路2の
上端部11に揚水して、上端部11とヘッドタンク5と
の水頭差により循環液流を生起し、液循環が安定したと
ころで散気管14aより下降流路2内に水処理用の空気
を吹き込んでいる。
In the pump type deep shaft shown in FIG. 4, the upper end 11 of the descending passage 2 is the head tank 5.
A circulation pump 13 is disposed in a pipe line 12 which is arranged so as to be positioned higher and which connects the upper end 11 and the inside of the head tank 5. Blower 14 as air supply means
The diffusing pipe 14 a connected to is led to the inside of the descending flow path 2. In such a configuration, the circulation pump 13 pumps up the activated sludge mixed liquid 6 in the head tank 5 to the upper end 11 of the descending flow path 2, and the circulating liquid flow is caused by the head difference between the upper end 11 and the head tank 5. When the liquid circulation is stable, air for water treatment is blown into the descending flow path 2 from the diffuser pipe 14a.

【0007】上記したエアリフト方式およびポンプ方式
のいずれにおいても、下降流路2内に吹き込まれた空気
は気泡となり、下降流路2内を下降する活性汚泥混合液
6に混じってシャフト底部4aまで引きずり込まれる。
下降流路2内の混合液6の速度は、気泡が静止水中を浮
上する速度より十分速い1〜2m/秒に調節されるの
で、下降流路2内で気泡が上昇することはなく、気泡は
シャフト4内でその深さに応じ大きな静水圧を受け、空
気中の酸素は速やかに混合液6中に溶解する。
In both the air lift system and the pump system described above, the air blown into the descending passage 2 becomes air bubbles, is mixed with the activated sludge mixed liquid 6 descending in the descending passage 2, and is dragged to the shaft bottom 4a. Get caught.
The speed of the mixed liquid 6 in the descending flow path 2 is adjusted to 1 to 2 m / sec, which is sufficiently faster than the speed at which the bubbles float in the still water, so that the bubbles do not rise in the descending flow path 2 and Receives a large hydrostatic pressure in the shaft 4 depending on its depth, and oxygen in the air is quickly dissolved in the mixed liquid 6.

【0008】[0008]

【発明が解決しようとする課題】ところが、このような
曝気槽においても、多量の空気を供給する目的で散気板
を多数配置する場合や反応槽の形状によっては、下降流
路内に十分な混合液流速を確保するのが困難となる場合
がある。また、散気水深を深くするほど、溶解効率を高
くできるものの、コンプレッサやブロワの駆動に大きな
動力を要するため酸素移動動力効率が低くなるという問
題がある。
However, even in such an aeration tank, depending on the case where a large number of diffuser plates are arranged for the purpose of supplying a large amount of air or depending on the shape of the reaction tank, a sufficient amount of air may be present in the descending passage. It may be difficult to secure the flow rate of the mixed solution. Further, although the dissolution efficiency can be increased as the depth of the diffused water is increased, a large amount of power is required to drive the compressor and the blower, which causes a problem that the oxygen transfer power efficiency is reduced.

【0009】このため、下降流路の下部に被処理水を下
降流路内を下向きに流動させるポンプ装置を設置し、下
降流路内の上部に散気手段を配置することが考えられる
が、このような構成では、ポンプ装置を駆動するモータ
が槽の底部かつ被処理水中に位置することになり、その
維持管理が容易でない。また、水深が深くなるほど大き
な水圧がモータにかかるので、摺動部からモータ内部に
浸水したり、摺動部のシールの劣化が早まるという問題
がある。
For this reason, it is conceivable to install a pump device for causing the water to be treated to flow downward in the descending flow passage at the lower part of the descending flow passage, and to arrange an air diffuser at the upper part in the descending flow passage. In such a configuration, the motor that drives the pump device is located at the bottom of the tank and in the water to be treated, and its maintenance is not easy. Further, as the water depth becomes deeper, a larger water pressure is applied to the motor, so that there is a problem that water is flooded into the motor from the sliding portion, and the seal of the sliding portion is deteriorated more quickly.

【0010】本発明は上記問題を解決するもので、反応
槽の形状にかかわらず使用でき、高い酸素溶解効率およ
び酸素移動動力効率が得られるとともに、耐久性が大き
くかつ維持管理が容易な曝気装置を提供することを目的
とするものである。
The present invention solves the above problems, and can be used regardless of the shape of the reaction tank, can obtain high oxygen dissolution efficiency and oxygen transfer power efficiency, and has a large durability and easy maintenance. It is intended to provide.

【0011】[0011]

【課題を解決するための手段】上記問題を解決するため
に、本発明の曝気装置は、反応槽の内部に被処理水の一
定水深下から底部にわたり上下方向に配置される引込管
と、この引込管内の上部に開口して被処理水中に酸素含
有気体を供給する散気手段と、前記引込管の下部に設置
されて、前記散気手段により供給された酸素含有気体と
被処理水とを引込管内を下向きに流動させるポンプ手段
とを備え、前記引込管は下方に向かって漸次縮径する呑
口を上端に形成し、前記ポンプ手段は、前記引込管内の
酸素含有気体と被処理水とを下向きに流動せしめるイン
ペラを有し、このインペラを駆動する駆動軸を引込管内
を挿通して上方に導き、被処理水の水面上で駆動手段に
連結して構成したことを特徴とする。
In order to solve the above-mentioned problems, the aeration apparatus of the present invention comprises a lead-in pipe arranged in the reaction tank in the vertical direction from below a certain depth to the bottom of the water to be treated. An air diffuser for opening the upper part of the intake pipe to supply oxygen-containing gas into the water to be treated, and an oxygen-containing gas supplied by the air diffuser and the water to be treated, which are installed at the lower part of the inlet pipe. And a pump means for causing the inside of the intake pipe to flow downward, wherein the intake pipe has a dovetail that gradually decreases in diameter downward and is formed at the upper end, and the pump means forms the oxygen-containing gas and the water to be treated in the intake pipe. It is characterized in that it has an impeller for making it flow downward, and a drive shaft for driving this impeller is inserted through the lead-in pipe and guided upward, and is connected to the drive means on the surface of the water to be treated.

【0012】[0012]

【作用】上記構成により、反応槽内の被処理水は、ポン
プ手段のポンプ作用と引込管のガイド作用とにより引込
管内を下向きに流動するが、その際、下方に向かって漸
次縮径する呑口から引込管の内部に流入することにより
乱流を生じる。このため、引込管内の上部において散気
手段より供給される酸素含有気体は、乱流状態の被処理
水に巻き込まれてその気泡が細分化され、引込管内を下
降する間に水深の増大に伴い速やかに被処理水に溶解さ
れるので、被処理水への酸素溶解量および動力効率は大
きなものとなる。
With the above structure, the water to be treated in the reaction tank flows downward in the intake pipe due to the pumping action of the pump means and the guiding action of the intake pipe, but at that time, the diameter of the drinking water is gradually reduced downward. A turbulent flow is generated by flowing from the inside into the lead-in pipe. Therefore, the oxygen-containing gas supplied from the air diffusing means in the upper part of the intake pipe is entrained in the water to be treated in a turbulent state and its bubbles are subdivided, and as the water depth increases while descending in the intake pipe. Since it is rapidly dissolved in the water to be treated, the amount of oxygen dissolved in the water to be treated and the power efficiency are large.

【0013】また、駆動手段が水面上に設置されている
ので、摺動部から被処理水が侵入したり、摺動部のシー
ルが早期に劣化することは防止され、駆動手段の耐久性
が向上する。駆動手段の点検・修理を行う際には、駆動
軸から駆動手段を取り外す作業を槽外において容易に行
うことができる。
Further, since the driving means is installed on the water surface, it is possible to prevent water to be treated from entering the sliding portion and prevent the seal of the sliding portion from being deteriorated at an early stage, so that the durability of the driving means is improved. improves. When inspecting and repairing the drive means, the work of removing the drive means from the drive shaft can be easily performed outside the tank.

【0014】[0014]

【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および図2において、15は水深20
m程度の被処理水を貯留可能に構成された反応槽であ
る。反応槽15の内部には、活性汚泥を混合した被処理
水16が貯留されており、槽15の水平方向ほぼ中央位
置に被処理水16に浸漬して曝気装置17が設置されて
いる。18は原水供給管、19は脱気設備へ至る送水
管、20は汚泥返送管である。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described below with reference to the drawings. In FIGS. 1 and 2, 15 is a water depth of 20.
It is a reaction tank configured to store about m water to be treated. Water to be treated 16 mixed with activated sludge is stored inside the reaction tank 15, and an aeration device 17 is installed at a substantially central position in the horizontal direction of the tank 15 so as to be immersed in the water to be treated 16. Reference numeral 18 is a raw water supply pipe, 19 is a water supply pipe to the degassing equipment, and 20 is a sludge return pipe.

【0015】曝気装置17は、被処理水16の一定水深
下から底部にわたり上下方向に配置された引込管21を
備えており、この引込管21の上端には下方に向かって
漸次縮径する呑口22が形成されている。曝気装置17
はまた、空気23などの酸素含有気体を被処理水16に
供給する散気管24などの散気手段を引込管21内の上
部たとえば液面下約5mに開口させ、散気管24により
供給された空気23と被処理水16とを引込管21内を
下向きに流動させるポンプ装置25を引込管21の下部
に備えている。散気管24は、槽外のブロワー26など
の給気手段に接続されている。
The aeration device 17 is provided with a lead-in pipe 21 which is vertically arranged from below a certain depth of the water 16 to be treated to at the bottom thereof, and the upper end of the lead-in pipe 21 is gradually reduced in diameter downward. 22 is formed. Aeration device 17
Is also supplied by the air diffuser 24 by opening an air diffuser such as an air diffuser 24 for supplying an oxygen-containing gas such as air 23 to the water 16 to be treated 16 to an upper part in the intake pipe 21, for example, about 5 m below the liquid surface. A pump device 25 for causing the air 23 and the water to be treated 16 to flow downward in the intake pipe 21 is provided at the lower portion of the intake pipe 21. The air diffuser 24 is connected to an air supply means such as a blower 26 outside the tank.

【0016】ポンプ装置25は、図示したような密閉構
造をなすものであり、引込管21の下端に接続する導入
口27と、下方かつ半径方向に周状に形成された吐出口
28とを有し、内部にインペラ29を備えている。イン
ペラ29を駆動する駆動軸30は、引込管21内に挿通
されて上方に導かれ、被処理水の水面上においてモータ
31に連結されている。このインペラ29の駆動によ
り、引込管21内の空気23と被処理水16とが、導入
口27を通じて装置25の内部に導入され、攪拌混合さ
れつつ吐出口28を通じて装置25の外部へ吐出され、
このような導入・吐出に伴い、引込管21内の空気23
と被処理水16とが下向きに約2m/秒の流速で流動さ
れる。
The pump device 25 has a closed structure as shown in the drawing, and has an inlet port 27 connected to the lower end of the lead-in pipe 21 and a discharge port 28 formed in a downward and radial circumferential shape. However, an impeller 29 is provided inside. A drive shaft 30 that drives the impeller 29 is inserted into the lead-in pipe 21 and guided upward, and is connected to a motor 31 on the surface of the water to be treated. By driving the impeller 29, the air 23 in the intake pipe 21 and the water 16 to be treated are introduced into the device 25 through the introduction port 27, are agitated and mixed, and are discharged to the outside of the device 25 through the discharge port 28.
With such introduction / discharge, air 23 in the intake pipe 21
And the water 16 to be treated flow downward at a flow rate of about 2 m / sec.

【0017】32は、ポンプ装置25のメンテナンス時
などにその取出・設置を案内する上下方向のガイド管で
あり、33はポンプ装置25をガイド管32に対して移
動自在に取り付けるガイドである。
Reference numeral 32 is a vertical guide tube for guiding the taking-out and installation of the pump device 25 at the time of maintenance, and 33 is a guide for movably attaching the pump device 25 to the guide pipe 32.

【0018】以下、上記構成による作用を説明する。反
応槽15では、原水供給管18から原水が供給され、汚
泥返送管20から活性汚泥が返送される状態において、
槽15内の被処理水16が活性汚泥により生物学的に処
理されるとともに、活性汚泥を含む被処理水16の一部
が送水管19を通じて槽15外へ流出していく。
The operation of the above configuration will be described below. In the reaction tank 15, raw water is supplied from the raw water supply pipe 18 and activated sludge is returned from the sludge return pipe 20,
The treated water 16 in the tank 15 is biologically treated by the activated sludge, and a part of the treated water 16 containing the activated sludge flows out of the tank 15 through the water supply pipe 19.

【0019】反応槽15内の被処理水16は、引込管2
1の下部に設置されたポンプ装置25のポンプ作用と引
込管21のガイド作用とにより引込管21内に下向きに
引き込まれ、その際、下方に向かって漸次縮径する呑口
22より引込管21の内部に流入することにより乱流を
生じる。このような乱流状態の被処理水16に、引込管
21内の上部において散気管24より空気23が供給さ
れる。
The water 16 to be treated in the reaction tank 15 is the intake pipe 2
1 is pulled downward into the pull-in pipe 21 by the pumping action of the pump device 25 installed in the lower part of 1 and the guide action of the pull-in pipe 21, and at that time, the pull-in pipe 21 is drawn from the dovetail 22 which gradually decreases in diameter downward. Turbulence is generated by flowing into the inside. The air 23 is supplied to the water 16 to be treated in such a turbulent state from the air diffusing pipe 24 in the upper part of the intake pipe 21.

【0020】供給された空気23は、乱流に巻き込まれ
ることでその気泡が細分化されて被処理水16との接触
率が高まり、かつ引込管21内を下降する間に水深の増
大につれてその溶解量が増大するため、速やかに被処理
水16に溶解する。
The supplied air 23 is entrained in a turbulent flow, so that its bubbles are subdivided to increase the contact rate with the water 16 to be treated, and as the water depth increases as it descends in the intake pipe 21, Since the amount of dissolution increases, it dissolves quickly in the water 16 to be treated.

【0021】引込管21内を下向きに流動してその下端
に達した被処理水16と空気23は、ポンプ装置25の
導入口27よりその内部に流入し、インペラ29によっ
て攪拌混合されつつ、吐出口28より下方へ向けて放射
状に吐出される。
The water 16 to be treated and the air 23, which have flowed downward in the intake pipe 21 and reached the lower end thereof, flow into the interior thereof through the inlet 27 of the pump device 25 and are agitated and mixed by the impeller 29 while being discharged. It is radially discharged downward from the outlet 28.

【0022】このとき、空気23は、インペラ29によ
ってその気泡がさらに微細化されつつ被処理水16に混
合され、被処理水16との接触率が高められるため、被
処理水16への溶解速度がさらに大きなものとなる。
At this time, the air 23 is mixed with the water 16 to be treated while the bubbles are further miniaturized by the impeller 29, and the contact rate with the water 16 to be treated is increased. Will be even bigger.

【0023】吐出口28から下方へ向けて放射状に吐出
された被処理水16は、反応槽15の底部に達した後に
側壁近傍を上昇する循環流を形成する。このような槽内
全領域を循環する循環流が形成されることによって、空
気と被処理水16との接触率が高められ、被処理水16
への酸素溶解量がさらに増大する。
The water 16 to be treated, which is radially discharged downward from the discharge port 28, forms a circulating flow that rises near the side wall after reaching the bottom of the reaction tank 15. By forming such a circulation flow that circulates in the entire region in the tank, the contact rate between the air and the water 16 to be treated is increased, and the water 16 to be treated is
The amount of oxygen dissolved in is further increased.

【0024】このように、空気23の気泡の微細化およ
び循環流形成により空気23と被処理水16との接触率
が高められるとともに、大きな水頭により被処理水16
への空気23の溶解量が高められるため、被処理水16
への酸素溶解量は大きなものとなり、反応槽15におけ
る酸素溶解効率は高いものとなる。このような曝気装置
17は通常水深5m以上の反応槽に設置され、散気管2
4はブロワ動力が過度に大きくならない水深下に開口さ
れる。また、反応槽15において酸素移動に必要とされ
る動力はポンプ動力とブロワ動力の合算で表されるが、
この動力上昇以上に酸素移動量がアップするため、酸素
移動動力効率も向上することになる。
As described above, the contact ratio between the air 23 and the water 16 to be treated is increased by making the bubbles of the air 23 fine and forming a circulating flow, and the water 16
Since the amount of air 23 dissolved in the water is increased, the treated water 16
The amount of oxygen dissolved therein is large, and the oxygen dissolution efficiency in the reaction tank 15 is high. Such an aeration device 17 is usually installed in a reaction tank having a water depth of 5 m or more, and the aeration pipe 2
No. 4 is opened under the water so that the blower power does not become excessively large. The power required for oxygen transfer in the reaction tank 15 is represented by the sum of pump power and blower power,
Since the oxygen transfer amount is increased more than the power increase, the oxygen transfer power efficiency is also improved.

【0025】なお、モータ31が水面上に設置されてい
るので、摺動部からの被処理水の侵入や、摺動部のシー
ルの早期劣化が防止され、これにより、モータ31の耐
久性が向上する。点検・修理を行う際には、槽外におい
て駆動軸30からモータ31を取り外すことができ、維
持管理が容易である。
Since the motor 31 is installed on the surface of the water, intrusion of water to be treated from the sliding portion and early deterioration of the seal of the sliding portion are prevented, whereby the durability of the motor 31 is improved. improves. At the time of inspection and repair, the motor 31 can be removed from the drive shaft 30 outside the tank, and maintenance is easy.

【0026】[0026]

【発明の効果】以上述べたように、本発明によれば、引
込管の上端部において呑口により乱流を生起し、乱流状
態の被処理水に引込管内の上部において酸素含有気体を
分散させて、この被処理水を引込管内を下降させるよう
にした。これにより、酸素含有気体は、被処理水との接
触率が大きくなるとともに、大きな水頭を受けて被処理
水への溶解量が大きくなり、これらの相乗効果により酸
素溶解効率および酸素移動動力効率が高いものとなる。
As described above, according to the present invention, a turbulent flow is generated at the upper end of the intake pipe by the mouthpiece, and the oxygen-containing gas is dispersed in the turbulent water to be treated in the upper portion of the intake pipe. Then, the water to be treated was made to descend in the intake pipe. As a result, the oxygen-containing gas has a large contact rate with the water to be treated, and receives a large head to increase the amount of dissolution in the water to be treated, and the synergistic effect of these increases the oxygen dissolution efficiency and the oxygen transfer power efficiency. It will be expensive.

【0027】また、インペラを駆動する駆動軸を上方に
導いて、水面上に設置した駆動手段に連結するようにし
たため、槽の底部においてはインペラにより必要な流速
を確保でき、水面上においては駆動手段の長寿命化およ
び維持管理の容易化を図ることができる。
Further, since the drive shaft for driving the impeller is guided upward and connected to the drive means installed on the water surface, the impeller can secure a necessary flow velocity at the bottom of the tank, and the drive can be performed on the water surface. The life of the means can be extended and maintenance can be facilitated.

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

【図1】本発明の一実施例の曝気装置を設置した反応槽
を示した説明図である。
FIG. 1 is an explanatory view showing a reaction tank equipped with an aeration device according to an embodiment of the present invention.

【図2】同曝気装置の動作を説明する要部縦断面図であ
る。
FIG. 2 is a longitudinal sectional view of an essential part for explaining the operation of the aeration apparatus.

【図3】従来の超深層曝気槽の一実施例を示した説明図
である。
FIG. 3 is an explanatory view showing an example of a conventional super deep aeration tank.

【図4】従来の超深層曝気槽の他の実施例を示した説明
図である。
FIG. 4 is an explanatory view showing another embodiment of the conventional super deep aeration tank.

【符号の説明】[Explanation of symbols]

15 反応槽 16 被処理水 17 曝気装置 21 引込管 22 呑口 23 空気 24 散気管 25 ポンプ装置 26 ブロワ 29 インペラ 30 駆動軸 31 モータ 15 Reaction tank 16 Treated water 17 Aeration device 21 Intake pipe 22 Dowel 23 Air 24 Air diffuser pipe 25 Pump device 26 Blower 29 Impeller 30 Drive shaft 31 Motor

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 反応槽の内部に被処理水の一定水深下か
ら底部にわたり上下方向に配置される引込管と、この引
込管内の上部に開口して被処理水中に酸素含有気体を供
給する散気手段と、前記引込管の下部に設置されて、前
記散気手段により供給された酸素含有気体と被処理水と
を引込管内を下向きに流動させるポンプ手段とを備え、
前記引込管は下方に向かって漸次縮径する呑口を上端に
形成し、前記ポンプ手段は、前記引込管内の酸素含有気
体と被処理水とを下向きに流動せしめるインペラを有
し、このインペラを駆動する駆動軸を引込管内に挿通し
て上方に導き、被処理水の水面上で駆動手段に連結して
構成したことを特徴とする曝気装置。
1. A lead-in pipe which is vertically arranged from below a certain depth to the bottom of the water to be treated inside the reaction vessel, and a dispersion pipe which is opened at an upper part of the lead-in pipe and supplies an oxygen-containing gas into the water to be treated. An air means, and a pump means installed at the lower part of the intake pipe for causing the oxygen-containing gas supplied by the air diffuser and the water to be treated to flow downward in the intake pipe,
The inlet pipe is formed at its upper end with a dowel that gradually reduces its diameter downward, and the pump means has an impeller for causing the oxygen-containing gas in the inlet pipe and the water to be treated to flow downward, and drives this impeller. An aerating device, characterized in that the drive shaft is inserted into the lead-in pipe and guided upward, and is connected to the drive means on the surface of the water to be treated.
JP7054827A 1995-03-15 1995-03-15 Aerator Pending JPH08243585A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7054827A JPH08243585A (en) 1995-03-15 1995-03-15 Aerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7054827A JPH08243585A (en) 1995-03-15 1995-03-15 Aerator

Publications (1)

Publication Number Publication Date
JPH08243585A true JPH08243585A (en) 1996-09-24

Family

ID=12981510

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7054827A Pending JPH08243585A (en) 1995-03-15 1995-03-15 Aerator

Country Status (1)

Country Link
JP (1) JPH08243585A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010535627A (en) * 2007-08-15 2010-11-25 ユナイテッド・ユーティリティーズ・ピーエルシー Method and apparatus for aeration

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010535627A (en) * 2007-08-15 2010-11-25 ユナイテッド・ユーティリティーズ・ピーエルシー Method and apparatus for aeration

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