JP3668358B2 - Structure of bioreactor with carrier - Google Patents

Structure of bioreactor with carrier Download PDF

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JP3668358B2
JP3668358B2 JP12799497A JP12799497A JP3668358B2 JP 3668358 B2 JP3668358 B2 JP 3668358B2 JP 12799497 A JP12799497 A JP 12799497A JP 12799497 A JP12799497 A JP 12799497A JP 3668358 B2 JP3668358 B2 JP 3668358B2
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carrier
oxygen
biological reaction
reaction tank
microorganism
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JPH10296282A (en
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紘一 竹倉
健二 川田
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昭和エンジニアリング株式会社
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    • 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

【0001】
【発明の属する技術分野】
本発明は、都市の生活廃水、工場廃水などBOD含有廃水を活性汚泥法(微生物を用いて水処理を行う。)で処理するための改良された装置に関する。特に微生物濃度を高めるために微生物を付着した担体または微生物を包括した担体(本発明においてはれらを一括して微生物付着担体という。)を用い、酸素または酸素富化空気を用いて高濃度の微生物濃度で効率的に水処理を行う生物反応槽において、微生物付着担体の流出防止ための担体分離装置の点検及び保守の容易な構造を有する担体併用生物反応槽に関する。
【0002】
【従来の技術】
生物を用いた廃水処理方式として、微生物を付着した担体ないし生物を包括した担体を用いて、微生物濃度を高める方式及び特定の微生物の濃度を高める方式が提案されている。
この方法は、図2に示すように生物反応槽1及び沈殿池2を設け、生物反応槽1に供給された廃水7は、好気性条件下で活性汚泥の作用により、BOD分は微生物により消費される。このようにBODが低下した処理水は活性汚泥と共に沈殿槽5に送られ、そこで活性汚泥を分離し、水質が向上した処理水は河川などに放流される。分離された活性汚泥は一部は生物反応槽1に返送汚泥8として戻されるが、残部は余剰汚泥12として処理される。
【0003】
この処理において、生物反応槽1は、オープンで行われることも多いが、好ましくは密閉し、酸素または酸素富化空気雰囲気の好気性条件で行うことが行われる。特に廃水処理の速度が微生物濃度に比例することから、最近では微生物をポリエチレングリコールを主成分とする高分子含水ゲル(担体)などに固定化した微生物付着担体を生物反応槽1中に投入して微生物濃度を高濃度に維持し、反応速度を向上させる方法が提案され盛んに検討が行われている。
【0004】
このような方法においては、生物反応槽1から微生物付着担体の流出を防止することが必要となり、生物反応槽1の内部の処理液出口には微生物付着担体を処理液から分離するためのスクリーン4を設けて流出を防ぎ、微生物濃度の低下を防いでいる。この処理液出口にスクリーン4を設けることは、スクリーン4に微生物付着担体が分離沈積するだけでなく、最初沈殿地で沈降分離できなかった廃水7中に浮遊する各種の固体成分も一緒にここに沈積し、スクリーンの汚れ、目づまりの原因となって、生物反応槽1からの処理液の流出を妨害することになる。これが妨害されると、担体併用生物反応装置全体の操業に支障を起こし、装置全体の処理能力の低下、ひどい時には操業停止まで引き起こすことになる。
このため、スクリーン4の汚れ、目づまりの防止のため、生物反応槽1内に設けた逆洗装置(図示せず。)を設置し、定期的にスクリーン4を逆洗洗浄を行ったり、あるいはスクリーンの下部にスクリーンに向かって気体を噴出する散気装置(図示せず。)を設け、気泡噴出させ、スクリーン4に気泡と担体を衝突させることによりスクリーン4の目づまりを防止する(特許第2579122号)などの提案がなされている。
【0005】
なおこのように生物反応槽1において、生物反応のための微生物濃度が高濃度になると、この濃度に比例して生物反応槽単位容積あたりの酸素の消費速度は上昇することになる。
これまでの微生物付着担体を使用した担体併用生物処理反応において、その多くは空気を曝気することにより酸素の供給と攪拌を行っており、空気曝気のような比較的小さい攪拌力で微生物付着担体の良い分散を要求していたことから、微生物付着担体としては比較的軽い浮遊性の高分子含水ゲル担体などが用いられてきた。これらの担体は、高粘度のゲルであり、攪拌機などの強い攪拌においては破壊されやすく、酸素の消費速度が高くなるに従い、酸素の溶解速度を向上させるために生物反応槽の攪拌力を増加させるのには問題となっており、空気曝気によっては高溶存酸素濃度を維持するのは困難となっている。
【0006】
一方酸素ガス分離法の技術革新が行われ、比較的安価に高濃度の酸素が入手できるようになったため、酸素または酸素富化空気を廃水の活性汚泥法処理に使用されるようになってきた。この方法は処理帯域の高溶存酸素濃度を維持するのに極めて有効ではあるが、酸素消費量に見合うだけ溶解させるための散気量は少量で十分である。このためこの散気量で微生物付着担体を有効に分散させるためには不十分な量であり、高濃度酸素雰囲気を採用する時は、微生物付着担体の分散には気体攪拌よりは効率的な機械攪拌によることが好ましい。
しかし機械攪拌は、高分子含水ゲルのような柔らかい固体に対してはこれを破壊、粉砕する作用を有しており、このゲルの破壊はより一層、担体分離装置のスクリーンの目づまりを促進するものであり、最初沈殿池で沈殿できなかった固体成分、活性汚泥などの沈積とあいまち、スクリーン4の洗浄の必要頻度が相当高いものとなり、操業の効率低下を来していた。
【0007】
なおこの問題はそれぞれの処理槽ごとに、微生物濃度を高濃度とするために担体を使用し、それぞれの処理槽で馴化した微生物を付着した微生物付着担体を使用し、活性汚泥処理を行う場合において、それぞれの処理槽ごとに設けるスクリーン4についても同様な問題が生起しており、微生物付着担体を使用する活性汚泥法の大きな問題として根本的な解決が求められていた。
【0008】
【発明が解決しようとする課題】
本発明は、酸素または酸素富化空気を用い、かつ微生物濃度を高めるため微生物付着担体を用いる活性汚泥処理装置において、微生物付着担体の流出を防止するため各処理槽ごとに設けられた担体分離装置の、保守及び点検の容易な担体併用生物反応槽の構造の開発を目的とする。
【0009】
【課題を解決するための手段】
本発明は、
(1) 微生物付着担体を流動させながら密閉した生物反応槽で水処理を行う装置において、前記生物反応槽の外部に、底部において連通した状態で大気開放の状態のスクリーンを内蔵した担体分離装置を設ける担体併用生物反応槽の構造、および
(2) 密閉した前記生物反応槽が、酸素または酸素富化空気を用いる曝気槽である(1)記載の担体併用生物反応槽の構造を開発することにより上記の問題を解決した。
【0010】
【発明の実施の形態】
以下図面を参照して本発明を具体的に説明する。
本発明において使用する生物反応装置としては、図1に示すような装置が使用でき、通常の酸素または酸素富化空気を使用する活性汚泥法廃水処理に使用されている担体併用生物反応装置が好ましい。
この装置はスクリーン4を有する生物反応槽1及び沈殿槽5からなり、生物反応槽1はオープンであっても良いが、好ましくは密閉され、酸素または酸素富化空気雰囲気下で生物処理が行える生物処理槽が好ましい。
【0011】
この生物反応槽1は酸素または酸素富化空気雰囲気下で生物反応をさせる必要から、密閉タイプの生物反応槽であり、処理液の上部または液中に酸素または酸素富化空気が供給され、ガスとして生物反応槽の上部を満たしており、酸素濃度を維持するためその一部は排ガスとして廃棄される。生物処理をするためにはこの高濃度酸素ガスを処理水中に溶解させることが必要である。このため酸素を溶解させるとともに微生物付着担体を分散するための攪拌装置2が使用されるが、この形式は表面曝気機または水中ポンプなどを使用した機械攪拌、散気管または散気板を使用したガス攪拌または両者併用のいずれでも良く形式は自由であるが、攪拌エネルギー効率の点から機械攪拌、特に表面曝気機と液相の攪拌が同時にできる攪拌機の使用が好ましい。
【0012】
ここで生物反応処理の済んだ反応液はスクリーン4に送られ、ここで微生物付着担体を分離し、この分離液は次の沈殿槽5に送られる。この担体分離装置は、生物反応槽の底部において連通しており、その上部は大気に解放されている。また内部にはスクリーン4が設けられ、処理液中の微生物付着担体を処理液と分離できるようになっている。
この処理液中には、微生物付着担体のほか、最初沈殿池で分離できなかった固体成分(SS)、生物反応中に副生する活性汚泥などが含まれており、これらがスクリーン4上に沈積することとなる。
【0013】
本発明の担体分離装置は、従来の生物反応槽内にある装置と異なり、汚れたり、目づまりしたりするスクリーン4が大気開放状態にあるため、その保守や点検は容易であって、目づまりした時でも簡単に清掃が可能であり、処理液の流出を妨害するようなことは容易に回避できる。なおここで使用する微生物付着担体が処理水の比重より重い状態とする時は、スクリーンの目づまりを大幅に減らすことが可能となる。更に生物反応槽と連通する底部を、微生物付着担体が生物反応槽の方向に自動的に沈降移動できるようにしておくことが有利である。
【0014】
担体分離装置を通過した活性汚泥などを含む処理液は、沈殿槽5に送られ、活性汚泥などを分離し、上澄液は処理済水11として河川などに放流される。沈殿した活性汚泥は、その一部が返送汚泥8として生物反応槽に送られ、流入水7と混合され生物反応に使用され、残りの活性汚泥は余剰汚泥として処理される。
本発明に用いる微生物付着担体は特に制限がなく、高分子含水ゲルなどであっても良いが、微生物付着担体の機械的強度の点からは、例えば炭酸カルシウムのような無機質充填材で密度を調製した、ポリプロピレン、ポリエチレンのようなポリオレフィンの発泡体で、密度を0.95〜1.10g/cm3 程度に調製した担体を用いることが好ましい。密度が1.0g/cm3 以下であると水中では沈降しないはずであるが、水中に投入攪拌してしばらくすると、意外にも沈降する。これは充填材が吸水し、あるいは微生物が付着するなどの結果、密度として1.0g/cm3 を超えるためでないかと考えている。担体の形状は筒状体、円筒体、球状体、立方体あるいは不定形など特に制限はなく、また担体の大きさも、小さいほど表面積が大きく取れる反面、処理水の流速に大きく影響されるので限定的ではないが、できれば外径5〜30mmφ、厚さ0.5〜5mm、長さが外径の0.8〜1.2倍程度の筒状体が好ましい。
【0015】
このような担体は充填材と発泡材のため表面が荒れ、微生物の付着に好適であり、また筒状であるので、その内部に付着した微生物は担体が破壊されない限り安定した状態で担体に付着しており、処理部内において微生物処理に効力を発揮する。
生物反応槽における微生物付着担体の配合量は相当広範囲に変動させても効果が発揮でき、多いほど効果があるが、通常は生物反応槽の処理容積の15〜20容量%程度が攪拌におけるエネルギー効率の面からは好適である。
また余剰汚泥と返送汚泥の比率は一般の場合とほぼ同様に操業すればよく、50%程度で操業できる。
【0016】
微生物付着担体を使用した生物反応槽1は、微生物付着担体を使用する処理においては溶存酸素濃度に強い依存性を示し、生物反応速度はほぼその濃度に比例する。一般に高溶存酸素濃度で生物反応を行うと、処理水に含まれる活性汚泥の沈降性も良くなるので、限定的ではないが溶存酸素濃度は少なくとも約3mg/リットルで操業することが好ましい。
【0017】
【発明の効果】
廃水の活性汚泥による処理法において、微生物付着担体を使用して処理速度の向上を図ることが行われているが、処理速度の向上にともない、酸素消費速度に対応する酸素の供給法として酸素または酸素富化空気の使用が考えられる。この場合に、これまで微生物付着担体の流出を防止するためにそれぞれの処理槽内にスクリーンを設置してきたが、このスクリーンの目づまり防止の適切な手段がなかった。
本発明においては、生物反応槽内部に設けられていたスクリーンを含む担体分離装置の設置場所を反応槽外に変更することにより、微生物付着担体、活性汚泥、SSなどにより目づまりを起こしやすい担体分離装置のスクリーンは、洗浄、保守、点検の極めて容易にできるようにしたため、処理能力を向上させるために微生物付着担体を併用しても、スクリーンの目づまりによるトラブルによる操業の効率低下を防ぐことができた。
この結果本生物反応装置は、酸素の供給速度が大きく、生物反応速度も大となり、生物反応槽を開けなくともスクリーンの目づまりの予防が可能となったばかりでなく、仮に微生物付着担体などがスクリーンへ沈積しても密閉した生物反応槽を開けることなくその除去が簡単にできる。このため長期の連続運転が可能となったばかりでなく、副生する活性汚泥の密度が大きく分離が容易となるなど極めて有利な廃水処理法が開発できた。
【図面の簡単な説明】
【図1】本発明の微生物付着担体併用生物反応装置の1例の概念図である。
【図2】従来の微生物付着担体併用生物反応槽装置の概念図である。
【符号の説明】
1 生物反応槽
2 攪拌機
4 スクリーン
5 沈殿槽
6 汚泥掻寄機
7 廃水(流入水)
8 返送汚泥
9 酸素(酸素富化空気)
10 排ガス
11 処理済水(排出水)
12 余剰汚泥
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to an improved apparatus for treating BOD-containing wastewater such as urban wastewater and factory wastewater by an activated sludge method (water treatment is performed using microorganisms). In particular, in order to increase the concentration of microorganisms, a carrier attached with microorganisms or a carrier containing microorganisms (in the present invention, these are collectively referred to as a microorganism-attached carrier) and oxygen or oxygen-enriched air is used to increase the concentration. The present invention relates to a bioreactor combined with a carrier having a structure that facilitates inspection and maintenance of a carrier separation device for preventing outflow of a microorganism-adhering carrier in a biological reaction vessel that efficiently performs water treatment at a microorganism concentration.
[0002]
[Prior art]
As a wastewater treatment method using living organisms, a method of increasing the concentration of microorganisms and a method of increasing the concentration of specific microorganisms using a carrier attached with microorganisms or a carrier containing organisms have been proposed.
In this method, as shown in FIG. 2, a biological reaction tank 1 and a sedimentation tank 2 are provided, and the waste water 7 supplied to the biological reaction tank 1 is consumed by microorganisms under the aerobic condition due to the action of activated sludge. Is done. The treated water having a reduced BOD is sent to the sedimentation tank 5 together with the activated sludge, where the activated sludge is separated, and the treated water with improved water quality is discharged into a river or the like. A part of the separated activated sludge is returned to the biological reaction tank 1 as the return sludge 8, but the remainder is treated as excess sludge 12.
[0003]
In this treatment, the biological reaction tank 1 is often performed in an open state, but is preferably sealed and performed under aerobic conditions in an oxygen or oxygen-enriched air atmosphere. In particular, since the speed of wastewater treatment is proportional to the concentration of microorganisms, recently, a microorganism-adhering carrier in which microorganisms are immobilized on a polymer-containing hydrogel (carrier) containing polyethylene glycol as a main component is introduced into the biological reaction tank 1. Methods for maintaining a high microorganism concentration and improving the reaction rate have been proposed and actively studied.
[0004]
In such a method, it is necessary to prevent the microorganism adhesion carrier from flowing out of the biological reaction tank 1, and a screen 4 for separating the microorganism adhesion carrier from the treatment liquid at the treatment liquid outlet inside the biological reaction tank 1. To prevent spillage and prevent a decrease in microbial concentration. The provision of the screen 4 at the outlet of the treatment liquid not only separates and deposits the microorganism-adhering carrier on the screen 4, but also various solid components floating in the waste water 7 that could not be settled and separated at the initial settling site. It deposits, causing the screen to become dirty and clogged, and hinders the outflow of the processing liquid from the biological reaction tank 1. If this is obstructed, the operation of the entire bioreaction apparatus combined with a carrier will be hindered, resulting in a decrease in the processing capacity of the entire apparatus, and in the worst case, even the operation stoppage.
For this reason, in order to prevent the screen 4 from becoming dirty and clogged, a backwashing device (not shown) provided in the biological reaction tank 1 is installed, and the screen 4 is regularly backwashed or screened. An air diffuser (not shown) for ejecting gas toward the screen is provided at the lower part of the screen, and bubbles are ejected to prevent clogging of the screen 4 by causing bubbles and carriers to collide with the screen 4 (Japanese Patent No. 2579122). ) Etc. have been made.
[0005]
In this way, in the biological reaction tank 1, when the microbial concentration for biological reaction becomes high, the consumption rate of oxygen per unit volume of the biological reaction tank increases in proportion to this concentration.
In the conventional biological treatment reaction using a carrier with a microorganism attached, most of them supply oxygen and agitate by aeration of air. Since a good dispersion is required, a relatively light floating polymer-containing gel carrier has been used as a microorganism-adhering carrier. These carriers are high-viscosity gels, and are easily broken by strong stirring such as a stirrer. As the oxygen consumption rate increases, the stirring power of the biological reaction tank is increased to improve the oxygen dissolution rate. This is a problem, and it is difficult to maintain a high dissolved oxygen concentration by air aeration.
[0006]
On the other hand, technological innovations in oxygen gas separation methods have made it possible to obtain high-concentration oxygen at a relatively low cost, so oxygen or oxygen-enriched air has come to be used in wastewater activated sludge treatment. . This method is extremely effective for maintaining a high dissolved oxygen concentration in the treatment zone, but a small amount of air diffused to dissolve the oxygen consumption is sufficient. For this reason, this amount is insufficient to effectively disperse the microorganism-adhering carrier with this amount of aeration, and when a high-concentration oxygen atmosphere is adopted, it is more efficient than gas agitation to disperse the microorganism-adhering carrier. Preferably by stirring.
However, mechanical agitation has the effect of breaking and crushing soft solids such as polymer-containing hydrogels, and this gel breakage further promotes clogging of the screen of the carrier separation device. In other words, the solid components, activated sludge, etc. that could not be settled in the first sedimentation basin were mixed, and the required frequency of cleaning the screen 4 was considerably high, resulting in a decrease in operation efficiency.
[0007]
In addition, this problem is in the case where the activated sludge treatment is performed using a carrier for increasing the microorganism concentration in each treatment tank, and using a microorganism-adhered carrier to which microorganisms acclimatized in each treatment tank are attached. Similar problems have arisen for the screens 4 provided for the respective treatment tanks, and a fundamental solution has been demanded as a major problem of the activated sludge method using a microorganism-adhering carrier.
[0008]
[Problems to be solved by the invention]
The present invention relates to an activated sludge treatment apparatus using oxygen or oxygen-enriched air and using a microorganism-adhering carrier in order to increase the microorganism concentration, and a carrier separation device provided for each treatment tank to prevent the microorganism-adhering carrier from flowing out. The purpose is to develop a structure of a bioreactor with a carrier that is easy to maintain and check.
[0009]
[Means for Solving the Problems]
The present invention
(1) An apparatus for performing water treatment in a sealed biological reaction tank while flowing a microorganism-adhering carrier, wherein a carrier separation apparatus having a screen open to the atmosphere in a state of being communicated at the bottom outside the biological reaction tank. (2) By developing the structure of the biological reaction tank with the carrier according to (1), wherein the sealed biological reaction tank is an aeration tank using oxygen or oxygen-enriched air. Solved the above problem.
[0010]
DETAILED DESCRIPTION OF THE INVENTION
The present invention will be specifically described below with reference to the drawings.
As the bioreactor used in the present invention, an apparatus as shown in FIG. 1 can be used, and a bioreactor combined with a carrier used for activated sludge wastewater treatment using ordinary oxygen or oxygen-enriched air is preferable. .
This apparatus comprises a biological reaction tank 1 having a screen 4 and a sedimentation tank 5, and the biological reaction tank 1 may be open, but is preferably sealed and can be biologically treated in an oxygen or oxygen-enriched air atmosphere. A treatment tank is preferred.
[0011]
This biological reaction tank 1 is a sealed type biological reaction tank because it is necessary to perform a biological reaction in an atmosphere of oxygen or oxygen-enriched air, and oxygen or oxygen-enriched air is supplied to the upper part of the treatment liquid or in the liquid. As the upper part of the biological reaction tank is filled, a part of it is discarded as exhaust gas in order to maintain the oxygen concentration. In order to perform biological treatment, it is necessary to dissolve this high-concentration oxygen gas in the treated water. For this reason, a stirring device 2 for dissolving oxygen and dispersing the microorganism-adhering carrier is used. This type is a mechanical stirring using a surface aerator or a submersible pump, a gas using a diffuser tube or a diffuser plate. Either stirring or a combination of both may be used and the type is arbitrary. However, from the viewpoint of stirring energy efficiency, it is preferable to use a mechanical stirrer, particularly a stirrer capable of simultaneously stirring a surface aerator and a liquid phase.
[0012]
Here, the reaction solution that has undergone the biological reaction treatment is sent to the screen 4 where the microorganism-adhering carrier is separated, and this separated solution is sent to the next sedimentation tank 5. This carrier separation device communicates with the bottom of the biological reaction tank, and the top thereof is open to the atmosphere. In addition, a screen 4 is provided inside, so that the microorganism adhesion carrier in the treatment liquid can be separated from the treatment liquid.
In addition to the microorganism-adhering carrier, this treatment liquid contains solid components (SS) that could not be separated in the sedimentation basin at the beginning, and activated sludge produced as a by-product during the biological reaction. Will be.
[0013]
Unlike the conventional apparatus in the biological reaction tank, the carrier separation apparatus of the present invention is easily maintained and inspected because the screen 4 that is dirty or clogged is open to the atmosphere. In this case, cleaning can be easily performed, and it is possible to easily prevent the outflow of the processing solution. When the microorganism-adhering carrier used here is heavier than the specific gravity of the treated water, screen clogging can be greatly reduced. Furthermore, it is advantageous that the bottom communicating with the bioreactor is such that the microbial adhesion carrier can automatically settle and move in the direction of the bioreactor.
[0014]
The treatment liquid containing the activated sludge and the like that has passed through the carrier separation device is sent to the sedimentation tank 5 to separate the activated sludge and the like, and the supernatant is discharged as a treated water 11 to a river or the like. A part of the precipitated activated sludge is sent as a return sludge 8 to the biological reaction tank, mixed with the influent water 7 and used for a biological reaction, and the remaining activated sludge is treated as surplus sludge.
The microorganism-adhering carrier used in the present invention is not particularly limited, and may be a polymer hydrous gel. However, from the viewpoint of the mechanical strength of the microorganism-adhering carrier, the density is adjusted with an inorganic filler such as calcium carbonate. It is preferable to use a carrier made of a polyolefin foam such as polypropylene and polyethylene and having a density adjusted to about 0.95 to 1.10 g / cm 3 . If the density is 1.0 g / cm 3 or less, it should not settle in water, but after a while after being stirred in water, it settles unexpectedly. This is considered to be because the density exceeds 1.0 g / cm 3 as a result of water absorption of the filler or adhesion of microorganisms. The shape of the carrier is not particularly limited, such as a cylindrical body, cylindrical body, spherical body, cube, or indefinite shape. The smaller the carrier size, the larger the surface area, but it is limited because it is greatly affected by the flow rate of the treated water. However, if possible, a cylindrical body having an outer diameter of 5 to 30 mmφ, a thickness of 0.5 to 5 mm, and a length of about 0.8 to 1.2 times the outer diameter is preferable.
[0015]
Since such a carrier has a rough surface due to the filler and foaming material, it is suitable for the adhesion of microorganisms, and since it is cylindrical, the microorganisms adhering to the inside adhere to the carrier in a stable state unless the carrier is destroyed. It is effective for microbial treatment in the treatment section.
Even if the amount of the microorganism-adhering carrier in the biological reaction tank is varied over a wide range, the effect can be exerted. The larger the effect, the more effective, but usually 15 to 20% by volume of the treatment volume of the biological reaction tank is energy efficiency in stirring. From the viewpoint of the above, it is preferable.
Moreover, the ratio of surplus sludge and return sludge should just be operated in the same manner as in the general case, and it can be operated at about 50%.
[0016]
The biological reaction tank 1 using the microorganism adhesion carrier shows a strong dependence on the dissolved oxygen concentration in the treatment using the microorganism adhesion carrier, and the biological reaction rate is almost proportional to the concentration. In general, when a biological reaction is carried out at a high dissolved oxygen concentration, the settleability of the activated sludge contained in the treated water is improved. However, it is preferable to operate at a dissolved oxygen concentration of at least about 3 mg / liter, although not limited thereto.
[0017]
【The invention's effect】
In the treatment method using activated sludge of wastewater, it is attempted to improve the treatment speed by using a microorganism-adhering carrier. However, as the treatment speed improves, oxygen or oxygen can be used as a method for supplying oxygen corresponding to the oxygen consumption rate. The use of oxygen-enriched air is conceivable. In this case, a screen has been installed in each treatment tank so far to prevent the microorganism-adhering carrier from flowing out, but there is no appropriate means for preventing clogging of the screen.
In the present invention, by changing the installation location of the carrier separation device including the screen provided inside the biological reaction tank to the outside of the reaction tank, the carrier separation device is likely to cause clogging due to microbial adhesion carrier, activated sludge, SS, etc. The screen of this product can be cleaned, maintained, and inspected extremely easily, so even if a microbial adhesion carrier is used together to improve the processing capacity, it is possible to prevent a decrease in operational efficiency due to troubles caused by clogging of the screen. It was.
As a result, this bioreactor has a high oxygen supply rate and a high bioreaction rate, which can prevent clogging of the screen without opening the bioreaction tank. Even if it is deposited, it can be removed easily without opening the sealed biological reaction tank. For this reason, not only long-term continuous operation became possible, but also an extremely advantageous wastewater treatment method could be developed, such as the activated sludge produced as a by-product having a high density and easy separation.
[Brief description of the drawings]
FIG. 1 is a conceptual diagram of an example of a bioreactor combined with a microorganism-adhering carrier of the present invention.
FIG. 2 is a conceptual diagram of a conventional bioreactor device combined with a microorganism adhesion carrier.
[Explanation of symbols]
1 Biological reaction tank 2 Stirrer 4 Screen 5 Sedimentation tank 6 Sludge scraping machine 7 Waste water (inflow water)
8 Return sludge 9 Oxygen (oxygen-enriched air)
10 Exhaust gas 11 Treated water (discharged water)
12 Surplus sludge

Claims (2)

微生物付着担体を流動させながら密閉した生物反応槽で水処理を行う装置において、前記生物反応槽の外部に、底部において連通した状態で大気開放の状態のスクリーンを内蔵した担体分離装置を設けることを特徴とする担体併用生物反応槽の構造。In an apparatus for performing water treatment in a closed biological reaction tank while flowing a microorganism-adhering carrier, a carrier separation device having a screen open to the atmosphere in a state of being communicated at the bottom outside the biological reaction tank is provided. The structure of the bioreactor combined with the characteristic carrier. 密閉した生物反応槽が、酸素または酸素富化空気を用いる曝気槽である請求項1記載の担体併用生物反応槽の構造。The structure of the biological reaction tank with a carrier according to claim 1, wherein the sealed biological reaction tank is an aeration tank using oxygen or oxygen-enriched air.
JP12799497A 1997-04-30 1997-04-30 Structure of bioreactor with carrier Expired - Fee Related JP3668358B2 (en)

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Application Number Priority Date Filing Date Title
JP12799497A JP3668358B2 (en) 1997-04-30 1997-04-30 Structure of bioreactor with carrier

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JP3668358B2 true JP3668358B2 (en) 2005-07-06

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Publication number Priority date Publication date Assignee Title
JP4796852B2 (en) * 2006-01-25 2011-10-19 前澤化成工業株式会社 Wastewater treatment equipment
JP5666187B2 (en) * 2010-07-29 2015-02-12 佐竹化学機械工業株式会社 Waste water treatment apparatus and waste water treatment method
JP2022549249A (en) * 2019-11-21 2022-11-24 オルガノ株式会社 Biological treatment device, carrier capture device for biological treatment device, water treatment method, and modification method for biological treatment device

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