JPH0440295A - Waste water treatment device - Google Patents

Waste water treatment device

Info

Publication number
JPH0440295A
JPH0440295A JP2143740A JP14374090A JPH0440295A JP H0440295 A JPH0440295 A JP H0440295A JP 2143740 A JP2143740 A JP 2143740A JP 14374090 A JP14374090 A JP 14374090A JP H0440295 A JPH0440295 A JP H0440295A
Authority
JP
Japan
Prior art keywords
water
reactor
treated
pressure
wastewater 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.)
Pending
Application number
JP2143740A
Other languages
Japanese (ja)
Inventor
Chiaki Niwa
千明 丹羽
Katsumi Iwasaki
岩崎 克己
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.)
Shimizu Construction Co Ltd
Shimizu Corp
Proterial Ltd
Original Assignee
Shimizu Construction Co Ltd
Hitachi Metals Ltd
Shimizu 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 Shimizu Construction Co Ltd, Hitachi Metals Ltd, Shimizu Corp filed Critical Shimizu Construction Co Ltd
Priority to JP2143740A priority Critical patent/JPH0440295A/en
Publication of JPH0440295A publication Critical patent/JPH0440295A/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

  • Physical Water Treatments (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。
(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 「産業上の利用分野」 本発明は、生活廃水、産業廃水等を生物学的に処理する
廃水処理装置に関する。
DETAILED DESCRIPTION OF THE INVENTION "Field of Industrial Application" The present invention relates to a wastewater treatment device for biologically treating domestic wastewater, industrial wastewater, and the like.

「従来技術および発明が解決しようとする課題」廃水処
理装置の一種に超深層曝気法を実施する装置がある。こ
の装置は、第4図に示すように、流動床型バイオリアク
ター1に浮上層2が連設されてなるものである。流動床
型リアクター二は、上部が大気と連通した開放型のもの
でその深さは20〜25(lIllである。このリアク
ター1内には、下向流領域3と上向流領域4とが形成さ
れている。
"Prior Art and Problems to be Solved by the Invention" One type of wastewater treatment equipment is equipment that implements an ultra-deep aeration method. As shown in FIG. 4, this device consists of a fluidized bed bioreactor 1 and a floating layer 2 connected thereto. The fluidized bed reactor 2 is an open type with an upper part communicating with the atmosphere, and its depth is 20 to 25 mm. Inside the reactor 1, there are a downward flow region 3 and an upward flow region 4. It is formed.

有機性廃水はこの流動床型リアクター1内で循環されつ
つ曝気処理される。そしてこの流動床型リアクター1で
処理された被処理水は、浮上槽2に送られて活性汚泥を
分離されたあと放流される。
Organic wastewater is circulated and aerated within this fluidized bed reactor 1. The water to be treated in this fluidized bed reactor 1 is sent to a flotation tank 2, where activated sludge is separated, and then released.

このような従来の廃水処理装置では、浮上槽2で十分に
汚泥を分離できない問題があった。
In such a conventional wastewater treatment apparatus, there was a problem that sludge could not be sufficiently separated in the flotation tank 2.

本発明は前記事情に鑑みてなされたもので、浮上槽での
汚泥分離を良好に行える上に、円滑に運転できる廃水処
理装置を提供することを目的とする。
The present invention has been made in view of the above-mentioned circumstances, and an object of the present invention is to provide a wastewater treatment device that can perform sludge separation in a flotation tank well and can operate smoothly.

「課題を解決するための手段」 本発明の廃水処理装置では、加圧状態の密閉空間内で被
処理水を曝気循環させつつ生物学的に処理する加圧流動
床型バイオリアクターに、当該リアクターで処理された
被処理水から懸濁物質を分離する浮上槽を、通過する被
処理水を減圧する機構を備えた送液路を介して連設する
と共に、前記加圧流動床型バイオリアクターに、リアク
ター内の水位をコントロールする機構と、リアクター内
の圧力をコントロールする機構とを設けることによって
、前記目的を達成した。
"Means for Solving the Problems" The wastewater treatment apparatus of the present invention includes a pressurized fluidized bed bioreactor that biologically processes water to be treated while aerating and circulating it in a pressurized closed space. A flotation tank for separating suspended solids from the water to be treated is connected to the pressurized fluidized bed bioreactor through a liquid feed path equipped with a mechanism to reduce the pressure of the water to be treated passing through. The above object was achieved by providing a mechanism for controlling the water level within the reactor and a mechanism for controlling the pressure within the reactor.

前記送液路は、例えばリアクターと浮上槽とを連通ずる
管路に減圧弁を取り付けて構成することができる。この
ように送水路を構成した場合、減圧弁は、浮上槽の直前
、浮上槽の直下、浮上槽中など、できるだけ懸濁物質を
分離する場所の近傍に配置されることが望ましい。
The liquid feeding path can be configured by, for example, attaching a pressure reducing valve to a pipe line that communicates the reactor and the flotation tank. When the water supply channel is configured in this way, it is desirable that the pressure reducing valve be placed as close as possible to the location where suspended solids are to be separated, such as immediately before the flotation tank, directly below the flotation tank, or inside the flotation tank.

「作用」 この廃水処理装置では、リアクター内が加圧状態なので
、被処理水に酸素等の気体が多量に溶解する。この結果
、微生物による浄化速度が向上する。第3図は本発明者
らが「リアクター内圧力の処理能力に及ぼす影響」に付
いて実験した結果を示すものである。この図から判るよ
うに、2 kg/cCGの加圧下では処理速度がほぼ5
倍になり、加圧による処理効率向上の効果か顕著である
ことが判る。一般的な標準活性汚泥法では、BOD容積
負荷が0 、6 kg/m’/日であることを考えると
、2 kg/ cm”Gの加圧下では同容積のりアクタ
−の処理能力が約30倍になると言える。
"Function" In this wastewater treatment device, the inside of the reactor is in a pressurized state, so a large amount of gas such as oxygen is dissolved in the water to be treated. As a result, the rate of purification by microorganisms is improved. FIG. 3 shows the results of an experiment conducted by the present inventors regarding the "influence of reactor internal pressure on processing capacity." As can be seen from this figure, under a pressure of 2 kg/cCG, the processing speed is approximately 5
It can be seen that the effect of increasing the processing efficiency due to pressurization is remarkable. Considering that in the general standard activated sludge process, the BOD volume load is 0.6 kg/m'/day, the processing capacity of the same volume glue actor under a pressure of 2 kg/cm'G is approximately 30 kg/m'/day. You can say it doubles.

前記のように、加圧状態のりアクタ−で処理された被処
理水が送水路で減圧されて浮上槽に送られると、減圧に
より被処理水に溶解し得る気体の量が減少するので、溶
解しきれない気体が細かい泡となり、被処理水中に含ま
れる余剰汚泥や懸濁固形物(以下、88分と記す)に付
着する。この結果、浮上槽において88分が浮上分離さ
れる。
As mentioned above, when the water to be treated in the pressurized water tank is depressurized in the water supply channel and sent to the flotation tank, the amount of gas that can be dissolved in the water to be treated decreases due to the depressurization. The gas that cannot be drained becomes fine bubbles and adheres to excess sludge and suspended solids (hereinafter referred to as 88 minutes) contained in the water to be treated. As a result, 88 minutes were floated and separated in the flotation tank.

このリアクター内の圧力は、被処理水の水位の変動の影
響を受けるが、このリアクターには水位コントロール機
構が設けられており、液面の高さが一定範囲に保たれる
ので、リアクター内圧力への水位変動の影響を抑制でき
る。この廃水処理装置は、前記のようにリアクターの水
位を一定に保つた状態で圧力コントロール機構による圧
力制御を行うので、リアクター内圧力が適正範囲に安定
に保たれる。
The pressure inside this reactor is affected by fluctuations in the water level of the water to be treated, but this reactor is equipped with a water level control mechanism that keeps the liquid level within a certain range, so the pressure inside the reactor is The impact of water level fluctuations on water level can be suppressed. Since this wastewater treatment apparatus performs pressure control using the pressure control mechanism while keeping the water level in the reactor constant as described above, the pressure inside the reactor is stably maintained within an appropriate range.

「実施例」 以下、図面を参照して本発明の廃水処理装置を詳しく説
明する。
"Example" Hereinafter, the wastewater treatment apparatus of the present invention will be described in detail with reference to the drawings.

(実施例1) 第1図は本発明の廃水処理装置の一実施例を示すもので
、図中符号IOはりアクタ−1符号11は浮上槽、符号
12は送液路である。
(Embodiment 1) FIG. 1 shows an embodiment of the wastewater treatment apparatus of the present invention, in which reference numeral IO beam actor 1 11 is a flotation tank, and 12 is a liquid feeding path.

リアクター10は、加圧状態で被処理水を曝気循環させ
つつ生物学的に処理する加圧流動床型の処理槽である。
The reactor 10 is a pressurized fluidized bed type treatment tank that biologically processes the water while aerating and circulating the water under pressure.

このリアクター10は密閉された略筒状の外槽13と、
その中央に配置された内筒14と、内筒14の下方に配
置された散気管15とによって構成されており、リアク
ター10内の被処理水中には粒子表面に微生物膜が担持
されてなるバイオパーティクルが分散されている。この
バイオパーティクルが分散された被処理水は、送風機1
8から前記散気管15を通じてリアクター10内部に送
入される空気のエアーリフト効果により、内筒14の内
側を上昇し外側を下降しつつ。
This reactor 10 includes a sealed substantially cylindrical outer tank 13,
It is composed of an inner cylinder 14 placed in the center and an aeration pipe 15 placed below the inner cylinder 14, and the water to be treated in the reactor 10 contains bio-organisms in which a microbial film is supported on the particle surface. Particles are dispersed. The water to be treated in which the bioparticles are dispersed is supplied to the blower 1.
Due to the air lift effect of the air introduced into the reactor 10 from 8 through the aeration pipe 15, the air rises on the inside of the inner cylinder 14 and descends on the outside.

生物学的に処理される。Biologically processed.

外槽13の上部は拡径されており、この拡径された部分
には仕切筒16によって中央部側から仕切られたバイオ
パーティクル分離部17か形成されている。
The upper part of the outer tank 13 is enlarged in diameter, and a bioparticle separation section 17 partitioned from the center by a partition tube 16 is formed in this enlarged diameter portion.

このリアクター10には、原水タンク19に収集貯留さ
れた有機性廃水がポンプ20によって供蛤されるように
なっている。前記バイオパーティクル分離部17には液
面計21か設けられている。
Organic wastewater collected and stored in a raw water tank 19 is supplied to this reactor 10 by a pump 20. A liquid level gauge 21 is provided in the bioparticle separation section 17.

これらポンプ20と液面計21は、水位コントロール機
構を構成している。
These pump 20 and liquid level gauge 21 constitute a water level control mechanism.

このリアクター10の外槽13の上部は蓋部22によっ
て密閉されており、この蓋部22には、流量調整弁27
を有する定常ガス抜き管28が設けられている。この定
常ガス抜き管28は、リアクター10の上部空間からバ
ルブ開度一定で定常的にガス抜きを行うものである。
The upper part of the outer tank 13 of this reactor 10 is sealed by a lid part 22, and this lid part 22 has a flow rate regulating valve 27.
A stationary gas venting pipe 28 is provided. The steady gas vent pipe 28 is used to steadily vent gas from the upper space of the reactor 10 with a constant valve opening.

このリアクター10の蓋部22には、さらに、逆比弁2
3と電磁弁24を備えた抜気管25が取り付けられてい
る。またこのリアクターIOの上部には圧力計26が取
り付けられている。これら抜気管25と圧力計26はこ
のリアクターlOの圧力コントロール機構を構成してお
り、リアクター10内の圧力が上限圧力〔所定圧力(例
えば2kg/cm″G)の10%増し〕に達したとき電
磁弁24が開かれて抜気が行なわれ、所定圧力に戻った
とき電磁弁24が閉じられるようになっている。
The lid portion 22 of the reactor 10 further includes a reverse ratio valve 2.
A vent pipe 25 having a solenoid valve 24 and a solenoid valve 24 is attached. Moreover, a pressure gauge 26 is attached to the upper part of this reactor IO. These vent pipes 25 and pressure gauges 26 constitute a pressure control mechanism for this reactor lO, and when the pressure inside the reactor 10 reaches the upper limit pressure [10% increase over a predetermined pressure (for example, 2 kg/cm''G)]. The solenoid valve 24 is opened to vent air, and when the predetermined pressure returns, the solenoid valve 24 is closed.

前記浮上槽11は、リアクター10で処理された被処理
水から懸濁物質を分離する槽である。この浮上槽ll内
は、隔壁29によって懸濁物質分離部30と処理水導水
部31とに仕切らでいる。
The flotation tank 11 is a tank that separates suspended matter from the water to be treated that has been treated in the reactor 10. The inside of this flotation tank 11 is partitioned by a partition wall 29 into a suspended solid separation section 30 and a treated water introduction section 31.

懸濁物質分離部30と処理水導水部31とは、浮上槽l
Oの下部側で連通されている。処理水導水部31には、
越流基32が設けられており、懸濁物質の除去された処
理水はこの越流基32から放流されるようになっている
The suspended solids separation section 30 and the treated water introduction section 31 are connected to a flotation tank l.
They are connected at the bottom side of O. The treated water conveyance section 31 includes
An overflow base 32 is provided, and the treated water from which suspended solids have been removed is discharged from this overflow base 32.

前記送液路12は、この浮上槽11の懸濁物質分離部3
0の底部近傍と前記リアクター10のバイオパーティク
ル分離部17との間に設けられている。この送液路12
は管によって形成されたもので、その中程には減圧弁3
4が取り付けられている。この送水路12には、減圧弁
34よりもリアクター10内の位置に流速計19が取り
付けられており、減圧弁34が目詰まりして流路12内
の流速が低下したとき減圧弁34の開度を増して目詰ま
りの解消を図るようになっている。
The liquid feeding path 12 connects to the suspended solid separation section 3 of the flotation tank 11.
0 and the bioparticle separating section 17 of the reactor 10. This liquid feeding path 12
is formed by a pipe, and there is a pressure reducing valve 3 in the middle of it.
4 is installed. A flow meter 19 is attached to this water supply channel 12 at a position inside the reactor 10 rather than the pressure reducing valve 34, and when the pressure reducing valve 34 is clogged and the flow velocity in the flow channel 12 decreases, the pressure reducing valve 34 is opened. Efforts are being made to eliminate clogging.

この廃水処理装置では、原水タンク19からポンプ20
によってリアクター10に供給された被処理水が、散気
管15から吹き込まれる空気のエアーリフト効果によっ
て、バイオパーティクルと共にリアクター10内を循環
流動されつつ微生物の働きによって浄化される。リアク
ター10内は加圧状態であり、溶存酸素濃度が高いので
、被処理水は速やかに浄化される。吹き込まれた空気の
うち一部の酸素は被処理水中に溶解するが、残部は廃水
処理に伴い発生した炭酸ガス等と共にリアクターlOの
上部空間に放出され、定常ガス抜き管28から大気中に
放出される。この定常ガス抜き管28は、一定速度でガ
ス抜きを行うのでリアクターlO内の圧力が上限圧力に
達する場合があるが、その場合は、前記圧力コントロー
ル機構の電磁弁24を解放して、リアクター10内の圧
力を下げる。
In this wastewater treatment equipment, from the raw water tank 19 to the pump 20
The water to be treated that is supplied to the reactor 10 is circulated through the reactor 10 together with bioparticles due to the air lift effect of the air blown from the aeration pipe 15, and is purified by the action of microorganisms. Since the inside of the reactor 10 is under pressure and the dissolved oxygen concentration is high, the water to be treated is quickly purified. Some of the oxygen in the blown air dissolves in the water to be treated, but the rest is released into the upper space of the reactor IO along with carbon dioxide gas generated during wastewater treatment, and released into the atmosphere from the steady gas vent pipe 28. be done. Since this steady gas vent pipe 28 performs gas venting at a constant speed, the pressure inside the reactor IO may reach the upper limit pressure. In that case, the solenoid valve 24 of the pressure control mechanism is released and the reactor 1 Reduce internal pressure.

リアクターlO内の液面レベルは、ポンプ20と液面計
21とからなる水位コントロール機構および減圧弁34
の開度によって管理されており、液面レヘルが下限水位
に達すると前記ポンプ20かONされて原水タンク19
からリアクターlO内に被処理水が供給され、液面レベ
ルが上限水位に達するとポンプ20がOFFされて被処
理水の供給が停止される。
The liquid level in the reactor IO is controlled by a water level control mechanism consisting of a pump 20 and a liquid level gauge 21 and a pressure reducing valve 34.
When the liquid level reaches the lower limit water level, the pump 20 is turned on and the raw water tank 19 is
The water to be treated is supplied into the reactor 1O, and when the liquid level reaches the upper limit water level, the pump 20 is turned off and the supply of the water to be treated is stopped.

前記のようにしてリアクター10内で処理された被処理
水は、バイオパーティクル分離部17から送液路12を
介して浮上槽11の懸濁物質分離部30の底部に送られ
る。送液路12の減圧弁34を通過した被処理水は加圧
状態から解放されので、圧力低下に伴う溶解度の低下に
より被処理水に溶解し得なくなった一部の気体は微細気
泡となる。そしてこの微細気泡は、懸濁している86分
に付着する。
The water to be treated in the reactor 10 as described above is sent from the bioparticle separation section 17 to the bottom of the suspended matter separation section 30 of the flotation tank 11 via the liquid feed path 12. Since the water to be treated that has passed through the pressure reducing valve 34 of the liquid supply path 12 is released from the pressurized state, some of the gases that cannot be dissolved in the water to be treated due to a decrease in solubility due to the decrease in pressure become fine bubbles. These microbubbles then adhere to the suspended 86 minutes.

そして被処理水が浮上槽11に達すると、被処理水中に
懸濁していた86分は付着した泡の浮力によって懸濁物
質分離部30の水面に浮上する。
When the water to be treated reaches the flotation tank 11, the 86 particles suspended in the water to be treated float to the water surface of the suspended solid separation section 30 due to the buoyancy of the attached bubbles.

浮上した86分は、図示しないかき寄せ機によってかき
寄せられて、引抜汚泥として取り除かれる。
The 86 minutes that floated to the surface are scraped up by a scraper (not shown) and removed as drawn sludge.

一方浮上せず底部に沈降したごく一部の汚泥は、沈降引
抜汚泥として底部から引き抜かれる。このように86分
が分離して得られた処理水は、隔壁29の下から処理水
導水部31に流入し越流基32を越えて放流される。
On the other hand, a small portion of the sludge that does not float and settles to the bottom is pulled out from the bottom as settled sludge. The treated water obtained by separating the 86 minutes in this way flows into the treated water introduction section 31 from below the partition wall 29 and is discharged over the overflow base 32.

この廃水処理装置では、加圧されたりアクタ−10内で
被処理水を浄化するので、被処理水の溶存酸素濃度が高
く保たれ、リアクターlO内では好気性微生物による被
処理水の浄化速度が高い効率で行なわれる。従ってこの
廃水処理装置によれば、浄化効率を損なわずにリアクタ
ーlOの容積を小さくでき、装置のコンパクト化等を実
現でる。
In this wastewater treatment equipment, the water to be treated is pressurized or purified in the actor 10, so the dissolved oxygen concentration in the water to be treated is kept high, and the rate of purification of the water to be treated by aerobic microorganisms in the reactor 10 is increased. carried out with high efficiency. Therefore, according to this wastewater treatment apparatus, the volume of the reactor IO can be reduced without impairing the purification efficiency, and the apparatus can be made more compact.

またこの廃水処理装置では、リアクターlOで処理され
た被処理水が減圧弁34を備えた送液路12を介して浮
上槽11に送られるので、加圧状態にあった被処理水が
送液路12の減圧弁34を通過したときに加圧状態から
解放されて、被処理水内には溶解し得なくなった気体の
微細気泡が生じる。そしてこの微細気泡は、被処理水中
に含まれている88分に付着して、これを浮上槽11で
浮上分離させる。従ってこの廃水処理装置では、88分
が十分濃縮された状態で分離される。
In addition, in this wastewater treatment device, the water to be treated that has been treated in the reactor IO is sent to the flotation tank 11 via the liquid sending path 12 equipped with the pressure reducing valve 34, so that the water to be treated that has been in a pressurized state is transferred to the flotation tank 11. When the water passes through the pressure reducing valve 34 in the channel 12, it is released from the pressurized state, and fine bubbles of gas that cannot be dissolved are generated in the water to be treated. These microbubbles adhere to the 88 minute particles contained in the water to be treated, and are floated and separated in the flotation tank 11. Therefore, in this wastewater treatment device, 88 minutes is separated in a sufficiently concentrated state.

さらにこの廃水処理装置では、リアクター10に流量調
整弁27を備えた定常ガス抜き管28が設けられると共
に、液面計21とポンプ20とからなる水位コントロー
ル機構および電磁弁24と圧力計26とを備えた圧力コ
ントロール機構が設けられているので、リアクターlO
に送入された曝気空気のうち被処理水を通過した余剰分
と廃水処理によって生成したガス等は定常ガス抜き管2
8から一定速度で外気に放出されてリアクターlO内の
圧力の急変が防止される。また水位コントロール機構に
よって被処理水の水位が所定範囲に保たれて水位変動に
よるリアクターIO内圧力への影響が防止される。そし
て、この状態で圧力コントロール機構による圧力制御か
行なわれるので、リアクター10の内圧を適正な範囲に
制御できる。
Furthermore, in this wastewater treatment apparatus, the reactor 10 is provided with a steady gas vent pipe 28 equipped with a flow rate adjustment valve 27, and a water level control mechanism consisting of a liquid level gauge 21 and a pump 20, a solenoid valve 24, and a pressure gauge 26. A pressure control mechanism is provided so that the reactor lO
The surplus of the aeration air that has passed through the water to be treated and the gas generated by wastewater treatment are transferred to the stationary gas vent pipe 2.
8 to the outside air at a constant rate to prevent sudden changes in the pressure inside the reactor lO. Furthermore, the water level of the water to be treated is maintained within a predetermined range by the water level control mechanism, thereby preventing the influence of water level fluctuations on the pressure inside the reactor IO. In this state, pressure control is performed by the pressure control mechanism, so that the internal pressure of the reactor 10 can be controlled within an appropriate range.

従ってこの廃水処理装置によれば、リアクター10の圧
力を適正範囲に安定させることができ、装置を円滑に運
転できる。
Therefore, according to this wastewater treatment device, the pressure in the reactor 10 can be stabilized within an appropriate range, and the device can be operated smoothly.

またこの廃水処理装置では、リアクターlOの上部側を
拡径して仕切筒16で仕切ることによりバイオパーティ
クル分離部17を設けたので、分離部17では被処理水
の流れが緩やかとなりバイオパーティクルが被処理水か
ら沈降分離される。
In addition, in this wastewater treatment device, a bioparticle separation section 17 is provided by expanding the diameter of the upper part of the reactor IO and partitioning it with a partition tube 16. Therefore, in the separation section 17, the flow of the water to be treated becomes gentle, and the bioparticles are covered. It is separated by sedimentation from the treated water.

従ってこの廃水処理装置では、バイオパーティクルが送
液路12に流入するのを防止でき、浮上槽llから汚泥
(バイオパーティクル)を返送せずに運転できる。
Therefore, this wastewater treatment apparatus can prevent bioparticles from flowing into the liquid feeding path 12, and can operate without returning sludge (bioparticles) from the flotation tank 11.

(実施例2) 第2図は、本発明の廃水処理装置の第2実施例の要部を
示すものである。
(Example 2) FIG. 2 shows the main parts of a second example of the wastewater treatment apparatus of the present invention.

この例の廃水処理装置は、空気の代わりに純酸素または
高濃度酸素ガスを用いて曝気を行うもので、リアクター
lOの上部空間の気体は、脱液滴器36とバルブ38を
有す循環管路37を介して散気管15に返送されるよう
になっている。循環管路37には、バルブ41を介して
酸素タンク(又は酸素ガス発生器)39が取り付けられ
ている。
The wastewater treatment device of this example performs aeration using pure oxygen or high-concentration oxygen gas instead of air, and the gas in the upper space of the reactor IO is supplied to a circulation pipe having a de-dropper 36 and a valve 38. The air is returned to the diffuser pipe 15 via a passage 37. An oxygen tank (or oxygen gas generator) 39 is attached to the circulation pipe 37 via a valve 41 .

そしてリアクター10の上部に設けられた酸素濃度メー
タ40により酸素濃度が下限値(例えば56%)より低
下していることか検知されると酸素タンク39のバルブ
41が開かれるようになっている。またこのリアクター
IOの上部には、実施例1の装置に設けた定常ガス抜き
管28の代わりに、ガス抜き弁22が設けられており、
前記のように酸素タンク39から酸素ガスを補充する前
にガス抜き弁22を短時間解放してリアクターlO内の
炭酸ガス等の生成ガスや不活性ガスを抜く操作が行なわ
れるようになっている。
When the oxygen concentration meter 40 provided at the top of the reactor 10 detects that the oxygen concentration has fallen below a lower limit value (for example, 56%), the valve 41 of the oxygen tank 39 is opened. Furthermore, a gas vent valve 22 is provided at the top of this reactor IO in place of the steady gas vent pipe 28 provided in the device of Example 1.
As mentioned above, before replenishing oxygen gas from the oxygen tank 39, the gas vent valve 22 is opened for a short period of time to vent generated gas such as carbon dioxide gas and inert gas from the reactor lO. .

この実施例の廃水処理装置においても前記実施例1のも
のと同様の作用効果が得られる。
The wastewater treatment apparatus of this embodiment also provides the same effects as those of the first embodiment.

なおこの実施例の廃水処理装置において、リアクター1
0の上部空間に炭酸ガスメータを設置して、炭酸ガス濃
度によってガス抜き弁22の開閉を行う操作方法を採用
することもできる。
In addition, in the wastewater treatment apparatus of this example, reactor 1
It is also possible to adopt an operation method in which a carbon dioxide gas meter is installed in the upper space of the carbon dioxide gas and the gas vent valve 22 is opened and closed depending on the carbon dioxide concentration.

「発明の効果」 以上説明したように本発明の廃水処理装置は、加圧状態
の密閉空間内で被処理水を曝気循環させつつ生物学的に
処理する加圧流動床型バイオリアクターに、当該リアク
ターで処理された被処理水から懸濁物質を分離する浮上
槽が、通過する被処理水を減圧する機構を備えた送液路
を介して連設されると共に、前記加圧流動床型バイオリ
アクターに、リアクター内の水位をコントロールする機
構と、リアクター内の圧力をコントロールする機構とが
設けられた装置である。
"Effects of the Invention" As explained above, the wastewater treatment apparatus of the present invention is a pressurized fluidized bed bioreactor that biologically treats water while aerating and circulating it in a pressurized closed space. A flotation tank that separates suspended solids from the water to be treated that has been treated in the reactor is connected via a liquid feeding path equipped with a mechanism for reducing the pressure of the water to be treated passing through, and the above-mentioned pressurized fluidized bed bio This is a device in which a reactor is provided with a mechanism for controlling the water level within the reactor and a mechanism for controlling the pressure within the reactor.

このような構成を備えた廃水処理装置によれば、加圧さ
れたりアクタ−内で被処理水が浄化されるので、被処理
水の溶存酸素濃度が高く保たれ、高い浄化効率が実現さ
れる。従ってこの廃水処理装置によれば、浄化効率を損
なわずにリアクターの容積を小さくでき、装置のコンパ
クト化等を実現でる。
According to a wastewater treatment device with such a configuration, the water to be treated is pressurized or purified within the actor, so the dissolved oxygen concentration of the water to be treated is kept high and high purification efficiency is achieved. . Therefore, according to this wastewater treatment apparatus, the volume of the reactor can be reduced without impairing purification efficiency, and the apparatus can be made more compact.

また本発明の廃水処理装置では、リアクターで処理され
た被処理水が減圧されて浮上槽に送られるので、加圧状
態にあった被処理水が送液路を通過したときに加圧状態
から解放されて、被処理水中には微細気泡が生じる。そ
してこの微細気泡は、被処理水中に含まれている88分
に付着する。従ってこの廃水処理装置では、浮上槽で8
8分が浮上分離されて十分濃縮された状態で88分が分
離される。
In addition, in the wastewater treatment apparatus of the present invention, the water to be treated that has been treated in the reactor is depressurized and sent to the flotation tank, so when the water to be treated that was in a pressurized state passes through the liquid supply path, it is no longer pressurized. When released, microbubbles are generated in the water to be treated. These microbubbles then adhere to the 88 minute particles contained in the water to be treated. Therefore, in this wastewater treatment equipment, the flotation tank has a
8 minutes are separated by flotation and 88 minutes are separated in a sufficiently concentrated state.

さらに本発明の廃水処理装置では、リアクター水位コン
トロール機構と圧力コントロール機構が設けられている
ので、水位コントロール機構によって被処理水の水位が
所定範囲に保たれて水位変動によるリアクター内圧力へ
の影響を防止した状態でリアクター内圧力を制御できる
。従って本発明の廃水処理装置によれば、処理水質、S
S分分離効率等に大きな影響を及ぼすリアクター内圧力
を安定させることができ、装置を円滑に運転できる。
Furthermore, since the wastewater treatment apparatus of the present invention is provided with a reactor water level control mechanism and a pressure control mechanism, the water level of the water to be treated is maintained within a predetermined range by the water level control mechanism, thereby reducing the influence of water level fluctuations on the pressure inside the reactor. The pressure inside the reactor can be controlled while preventing this. Therefore, according to the wastewater treatment apparatus of the present invention, the treated water quality, S
It is possible to stabilize the pressure inside the reactor, which has a large effect on S component separation efficiency, etc., and the device can be operated smoothly.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は実施例1の廃水処理装置を示す概略構成図、第
2図は実施例2の廃水処理装置の要部を示す概略図、第
3図は本発明者らが実験したりアクタ−内圧力の処理能
力に及ぼす影響」の結果を示すグラフ、第4図は従来の
廃水処理装置を示す概略構成図である。 10・ リアクター 11・・浮上槽、12・送水路、
20・・ポンプ、21・・液面計、24・・電磁弁、2
5・・・抜気管、26・・・圧力計、34・・減圧弁。
FIG. 1 is a schematic configuration diagram showing the wastewater treatment device of Example 1, FIG. 2 is a schematic diagram showing the main parts of the wastewater treatment device of Example 2, and FIG. 3 is a schematic diagram showing the main parts of the wastewater treatment device of Example 2. FIG. 4 is a graph showing the results of ``Influence of Internal Pressure on Processing Capacity'' and is a schematic configuration diagram showing a conventional wastewater treatment device. 10. Reactor 11. Floating tank, 12. Water supply channel,
20...Pump, 21...Liquid level gauge, 24...Solenoid valve, 2
5...Air vent pipe, 26...Pressure gauge, 34...Pressure reducing valve.

Claims (1)

【特許請求の範囲】 加圧状態の密閉空間内で被処理水を曝気循環させつつ生
物学的に処理する加圧流動床型バイオリアクターに、当
該リアクターで処理された被処理水から懸濁物質を分離
する浮上槽を、通過する被処理水を減圧する機構を備え
た送液路を介して連設すると共に、 前記加圧流動床型バイオリアクターに、リアクター内の
水位をコントロールする機構と、リアクター内の圧力を
コントロールする機構とを設けたことを特徴とする廃水
処理装置。
[Claims] A pressurized fluidized bed bioreactor that biologically treats water to be treated while aerating and circulating it in a pressurized closed space contains suspended solids from the water to be treated in the reactor. A flotation tank that separates the water is connected via a liquid feeding path equipped with a mechanism to reduce the pressure of the water to be treated passing therethrough, and the pressurized fluidized bed bioreactor is provided with a mechanism for controlling the water level in the reactor; A wastewater treatment device characterized by being equipped with a mechanism for controlling the pressure inside the reactor.
JP2143740A 1990-06-01 1990-06-01 Waste water treatment device Pending JPH0440295A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2143740A JPH0440295A (en) 1990-06-01 1990-06-01 Waste water treatment device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2143740A JPH0440295A (en) 1990-06-01 1990-06-01 Waste water treatment device

Publications (1)

Publication Number Publication Date
JPH0440295A true JPH0440295A (en) 1992-02-10

Family

ID=15345916

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2143740A Pending JPH0440295A (en) 1990-06-01 1990-06-01 Waste water treatment device

Country Status (1)

Country Link
JP (1) JPH0440295A (en)

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5509955A (en) * 1992-08-17 1996-04-23 The Boc Group Plc Treatment of liquids
AU670530B3 (en) * 1994-11-18 1996-07-18 Agl Gas Company (Act) Ltd Waste water treatment method and plant
JP2002239575A (en) * 2001-02-16 2002-08-27 Ishikawajima Harima Heavy Ind Co Ltd Pressurized fluidized bed wastewater treatment equipment
JP2002346582A (en) * 2001-05-22 2002-12-03 Ishikawajima Harima Heavy Ind Co Ltd Pressurized fluidized bed wastewater treatment equipment
WO2005026062A3 (en) * 2004-08-03 2005-06-09 Lars Ekeroth Process and reactor for intensified and energy-efficient, biological (waste-)water treatment
JP2008259966A (en) * 2007-04-12 2008-10-30 Ihi Corp High pressure fluidized bed type aerobic waste water treatment equipment
JP2008264710A (en) * 2007-04-23 2008-11-06 Ihi Corp High-pressure fluidized bed aerobic wastewater treatment equipment
JP2008264646A (en) * 2007-04-18 2008-11-06 Ihi Corp High-pressure fluidized bed aerobic wastewater treatment equipment
FR2919601A1 (en) * 2007-07-30 2009-02-06 Degremont Sa Purifying wastewater by biological treatment that eliminates sludge such as carbon, nitrogen or phosphorus in the wastewater, comprises fixing a portion of microorganisms on movable solid supports, and treating the activated sludge
JP2018509281A (en) * 2016-02-26 2018-04-05 ジュン ジャエ オウクJUNG, Jae Ouk Atomizing apparatus and fluid processing equipment using the same

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5509955A (en) * 1992-08-17 1996-04-23 The Boc Group Plc Treatment of liquids
AU670530B3 (en) * 1994-11-18 1996-07-18 Agl Gas Company (Act) Ltd Waste water treatment method and plant
JP2002239575A (en) * 2001-02-16 2002-08-27 Ishikawajima Harima Heavy Ind Co Ltd Pressurized fluidized bed wastewater treatment equipment
JP2002346582A (en) * 2001-05-22 2002-12-03 Ishikawajima Harima Heavy Ind Co Ltd Pressurized fluidized bed wastewater treatment equipment
US7422688B2 (en) 2004-08-03 2008-09-09 Lars Ekeroth Biological wastewater treatment process and reactor
JP2008508095A (en) * 2004-08-03 2008-03-21 エケロス,ラルス Processes and reactors for enhanced energy efficient biological (waste) water treatment
WO2005026062A3 (en) * 2004-08-03 2005-06-09 Lars Ekeroth Process and reactor for intensified and energy-efficient, biological (waste-)water treatment
JP2008259966A (en) * 2007-04-12 2008-10-30 Ihi Corp High pressure fluidized bed type aerobic waste water treatment equipment
JP2008264646A (en) * 2007-04-18 2008-11-06 Ihi Corp High-pressure fluidized bed aerobic wastewater treatment equipment
JP2008264710A (en) * 2007-04-23 2008-11-06 Ihi Corp High-pressure fluidized bed aerobic wastewater treatment equipment
FR2919601A1 (en) * 2007-07-30 2009-02-06 Degremont Sa Purifying wastewater by biological treatment that eliminates sludge such as carbon, nitrogen or phosphorus in the wastewater, comprises fixing a portion of microorganisms on movable solid supports, and treating the activated sludge
WO2009047406A3 (en) * 2007-07-30 2009-06-18 Degremont Method and installation for biologically treating waste water
US8382984B2 (en) 2007-07-30 2013-02-26 Degremont Method and installation for biologically treating waste water
JP2018509281A (en) * 2016-02-26 2018-04-05 ジュン ジャエ オウクJUNG, Jae Ouk Atomizing apparatus and fluid processing equipment using the same

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