JPH0673676B2 - Method and apparatus for biological treatment of organic wastewater - Google Patents
Method and apparatus for biological treatment of organic wastewaterInfo
- Publication number
- JPH0673676B2 JPH0673676B2 JP4590790A JP4590790A JPH0673676B2 JP H0673676 B2 JPH0673676 B2 JP H0673676B2 JP 4590790 A JP4590790 A JP 4590790A JP 4590790 A JP4590790 A JP 4590790A JP H0673676 B2 JPH0673676 B2 JP H0673676B2
- Authority
- JP
- Japan
- Prior art keywords
- air
- overlayer
- tank
- cleaning
- raw water
- 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 - Fee Related
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Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Biological Treatment Of Waste Water (AREA)
Description
【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、下水,各種有機性産業廃水,し尿,浄化槽汚
泥などの各種有機性汚水を生物学的に処理する方法およ
び装置に関するものである。TECHNICAL FIELD The present invention relates to a method and apparatus for biologically treating various organic wastewater such as sewage, various organic industrial wastewaters, human waste, septic tank sludge and the like. .
〔従来の技術〕 従来、有機性汚水を生物学的に処理するための最も代表
的な手段は、活性汚泥処理である。[Prior Art] Conventionally, the most typical means for biologically treating organic wastewater is activated sludge treatment.
活性汚泥処理のための装置は、曝気槽と沈殿池を主体と
して成っており、適用範囲が広いという大きな長所があ
るために、現在最も多く使用されている。An apparatus for treating activated sludge mainly consists of an aeration tank and a sedimentation basin, and is widely used at present because of its great advantage that it has a wide range of application.
しかしながら、適用範囲が広いという長所がある活性汚
泥処理装置にも、次のような短所がある。However, the activated sludge treatment device, which has the advantage of having a wide application range, has the following disadvantages.
曝気槽と沈殿池が必要なので、設置面積が大きくな
り、建設費も高い。Since it requires an aeration tank and sedimentation tank, the installation area is large and construction costs are high.
沈殿池からのSSのキャリオーバーが避けられない。SS carryover from the settling basin is inevitable.
処理水質の良否が、活性汚泥の沈降性に支配される。The quality of treated water is governed by the settling property of activated sludge.
SSを高度に除去した処理水を得るには、砂過などの
過工程を付加しなければならない。このため、ますま
す設置面積と建設費の増加を招く。To obtain treated water from which SS is highly removed, an over-process such as sand filtration must be added. For this reason, the installation area and the construction cost are further increased.
などの問題点があった。There were problems such as.
本発明は、これら従来の活性汚泥処理での諸欠点を排除
しようとするもので、槽の水面部を利用して、生物学的
処理と高度のSS除去が可能な過による固液分離をも可
能にした有機性汚水の生物処理方法およびその装置を提
供することを目的とするものである。The present invention is intended to eliminate these various drawbacks in the conventional activated sludge treatment, and by utilizing the water surface of the tank, the biological treatment and solid-liquid separation due to excess SS removal are also possible. An object of the present invention is to provide a biological treatment method for organic sewage and an apparatus for the same.
本発明は、下部に原水流入部を持つ槽内を垂直隔壁によ
って複数に区画し、各区画に浮上材による過層を浸
漬保持させ、各区画の過層の上部にそれぞれ処理水流
出部と洗浄排水流出部を設け、これらの各区画の過層
の下部から各過層の材を空気洗浄するための空気
を、所定時間間隔で各区画に対して順々水平移動させて
供給して各過層を空気洗浄し、他の過層部分では原
水の浄化を行い、空気洗浄除去されたSSを原水の上向流
によって過層上部から洗浄排水として取り出すように
したものであり、また、前記槽内の各区画の下方部を連
通した沈殿部としたことで、生物学的処理と過による
固液分離を単一装置内で効果的に行い、従来、別に設置
されていた沈殿池を不要とし、また微生物の沈降性状に
支配されずに常に清澄な処理水を得ることができるもの
である。The present invention divides the inside of the tank having the raw water inflow section into a plurality of sections by vertical partition walls, so that each section is immersed and retained by the levitation material, and the treated water outflow section and the cleaning section are respectively provided above the overlayer of each section. A drainage / outflow section is provided, and air for cleaning the air of each overlayer is air-moved from the lower part of the overlayer of each of these sections by moving horizontally to each section at a predetermined time interval and is supplied to each section. The layer is air-washed, the raw water is purified in other overlayers, and the SS that has been air-washed and removed is taken out as wash drainage from the upper part of the overlayer by upward flow of the raw water. By making the lower part of each compartment inside to communicate with each other, biological treatment and solid-liquid separation by filtration can be effectively performed in a single device, eliminating the need for a separate settling tank that was conventionally installed. To obtain clear treated water without being influenced by the sedimentation properties of microorganisms. It is those that can be.
下水などの有機性汚物である原水は、槽内下方部の原水
流入部から槽内に流入し、沈降性の良いSSが沈降分離さ
れる。この沈降性の良いSSが分離,除去された原水は、
上向流で上方部の各区画内に浸漬保持されている浮上
材による過層を流過するが、その間に沈降分離されな
かった微細SSが過除去されると同時に、各過層を形
成する材表面には好気性あるいは嫌気性の生物膜が発
達しているので、原水中の溶解性BODが除去され、過
層を好気性状態に維持することによって、原水中のNH4
‐Nも硝化される。Raw water, which is organic waste such as sewage, flows into the tank from the raw water inflow section at the lower part of the tank, and SS with good sedimentation is separated by sedimentation. The raw water from which this good SS has been separated and removed is
It flows through the overlayer of the levitation material that is dipped and held in each of the upper compartments by upward flow, but at the same time, the fine SS that has not been settled and separated is excessively removed and at the same time forms each overlayer. Since an aerobic or anaerobic biofilm is developed on the surface of the material, soluble BOD in the raw water is removed, and by keeping the upper layer aerobic, NH 4 in the raw water is
-N is also nitrified.
また、槽内上方部をエアレーションなどによって好気性
状態に維持するようにすれば、浮遊性の活性汚泥の存在
によって、溶解性BODの一部が除去される。If the upper part of the tank is kept aerobic by aeration or the like, a part of the soluble BOD is removed due to the presence of the floating activated sludge.
なお、槽内の各区画の下方部を連通した沈殿部とした時
は、原水中のSSの沈降分離が促進される。In addition, when the lower part of each section in the tank is set as a communicating settling section, the settling separation of SS in the raw water is promoted.
このようにして、原水中のSSの沈降及び過による除去
や、有機物やNH4‐Nなどの生物学的除去が行われて清
澄となった処理水は、各区画の上部から泉のように湧出
し、各処理水流出部を経て処理水流出管から系外に流出
してゆく。In this way, the treated water that has been clarified by the removal of SS in the raw water by sedimentation and excess as well as the biological removal of organic matter and NH 4 -N becomes like a spring from the top of each section. It flows out and flows out of the system through the treated water outlet pipe through each treated water outlet.
さて、このような処理を続けるにつれて、過層におけ
るSS捕捉量の増加,生物膜の増殖に起因して過抵抗が
増加し、所定の過抵抗(通常1000〜1400mmH2O程度が
選ばれる)に達した時点で、過層の洗浄を行う。Now, as such treatment is continued, the amount of SS trapped in the overlayer increases, the overresistance increases due to the growth of the biofilm, and the predetermined overresistance (usually about 1000 to 1400 mmH 2 O is selected). Once reached, the overlayer is washed.
即ち、空気洗浄装置を、各区画の材層下部をゆっくり
と水平方向に移動させながら、多量の空気を噴出させ、
過層の下部から多量の空気を送り込む。この操作によ
って、その区画の浮上材による過層内が激しく撹乱
され、捕捉されていたSSが洗い出される。このような、
空気洗浄操作時には原水の槽内への流入を停止する必要
はなく、洗浄区画で洗出された多量のSSを含む洗浄排水
が上部の処理水流出部を経て洗浄排水流通管から系外に
流出する。この時、空気洗浄以外の他の区画において
は、処理が継続され、清澄な処理水が流出している。そ
して1つの区画の過層の空気洗浄が終了すると、空気
洗浄装置は隣りの区画に水平移動し、その区画の過層
を空気洗浄する。That is, while the air cleaning device slowly moves the lower part of the material layer in each section in the horizontal direction, a large amount of air is ejected,
A large amount of air is sent in from the bottom of the overlayer. This operation violently disturbs the inside of the superlayer due to the floating material in that section, and the trapped SS is washed out. like this,
It is not necessary to stop the inflow of raw water into the tank during the air cleaning operation, and the cleaning wastewater containing a large amount of SS that has been washed out in the cleaning section flows out of the system from the cleaning wastewater distribution pipe through the treated water outflow section at the top. To do. At this time, in the sections other than the air cleaning, the treatment is continued and clear treated water is flowing out. Then, when the air cleaning of the overlayer of one section is completed, the air cleaning device horizontally moves to the adjacent section, and air-cleans the overlayer of the section.
過層を形成する材としては、発泡スチロール,ポリ
ウレタンフォーム,ポリプロピレンなど、比重1.0未満
の浮上材を使用すれば、上方部における過層の保持
が容易であり、しかも空気洗浄時に気泡等による撹乱作
用が良好で、効果的な洗浄が行われ、前記過層の一部
を洗浄しながら、空気洗浄以外の他の部分では原水の浄
化処理が行える連続処理が可能である。If a floating material with a specific gravity of less than 1.0 is used as the material for forming the overlayer, such as styrofoam, polyurethane foam, polypropylene, etc., it is easy to hold the overlayer in the upper part, and there is a disturbing effect due to air bubbles during air cleaning. Good and effective cleaning is performed, and continuous processing is possible in which, while cleaning a part of the overlayer, a purification process of raw water is performed in a part other than air cleaning.
なお、各区画からの洗浄排水は、原水と一緒に、又は別
個に槽内に流過させ、洗浄排水中のSSを沈降分離するこ
とによって処分する。この際、洗浄排水中に高分子凝集
剤などを添加すれば、洗浄排水中のSSを急速に沈降分離
することができる。従って、浮上材による過層の洗
浄に、清澄な処理水を使用する必要がなく、処理水の生
産効率が高まる。In addition, the wastewater from each section is discharged together with the raw water or separately into the tank, and the SS in the wastewater is separated by sedimentation. At this time, if a polymer flocculant or the like is added to the cleaning wastewater, SS in the cleaning wastewater can be rapidly settled and separated. Therefore, it is not necessary to use clear treated water for cleaning the overlayer by the floating material, and the production efficiency of the treated water is increased.
なお、各区画の下部に各区画に空気を供給する散気装置
を固定配備することが好ましく、過層で好気性生物膜
処理を行う場合には、これらの散気装置から空気を供給
しておくが、過層で嫌気性生物膜処理を行う場合に
は、散気装置からの空気の供給を停止するだけで対応す
ることができる。In addition, it is preferable to fixedly deploy an air diffuser for supplying air to each compartment at the bottom of each compartment, and when performing aerobic biofilm treatment in an overstory, supply air from these air diffusers. However, when the anaerobic biofilm treatment is performed in the upper layer, it can be dealt with only by stopping the supply of air from the air diffuser.
このようにして、下水などの有機性汚水は、単一槽にお
いて、 という一連の除去メカニズムによって、高度に浄化され
る。In this way, organic sewage such as sewage, in a single tank, It is highly purified by a series of removal mechanisms called.
本発明の一実施例を図面に基づいて説明すれば、槽1内
上方部は、垂直隔壁2によって複数に区画されており、
各区画内には、スポンジ、軽量骨材,パーライト,プラ
スチック粒子,木材チップ,ガラスマイクロバルーンな
どの比重が1.0未満で水に浮く粒状材を充填した過
層3が設けられ、その上部をネットなどの通水性の支持
部材4で抑えて過層3は水中に浸漬保持されており、
各区画内上部にはそれぞれ処理水が越流する処理水流出
部5が設けられ、弁61を介して処理水流出管6に連なっ
ている。An embodiment of the present invention will be described with reference to the drawings. The upper part of the tank 1 is divided into a plurality of vertical partition walls 2.
Within each compartment, there is an overlayer 3 filled with sponge, lightweight aggregate, perlite, plastic particles, wood chips, glass microballoons, etc., which has a specific gravity of less than 1.0 and floats in water. Is suppressed by the water-permeable support member 4 and the overlayer 3 is immersed and held in water,
Each treated water to each compartment top is treated water outlet 5 for overflow provided are continuous to the treated water outlet pipe 6 via a valve 61.
前記槽1内の各区画の下方部は連通した沈殿部7として
あり、この沈殿部7内に、下水などの有機性汚水を導く
原水流入管8が開口されているが、この沈殿部7は必ず
しも設ける必要はない。9は槽内底部の適宜箇所に形成
された沈殿汚泥の濃縮部であって、排泥管10が連結され
ている。The lower part of each compartment in the tank 1 is a communicating sedimentation part 7, and a raw water inflow pipe 8 for introducing organic wastewater such as sewage is opened in the sedimentation part 7. It does not necessarily have to be provided. Reference numeral 9 denotes a concentrated portion of the settled sludge formed at an appropriate position on the bottom of the tank, and a sludge pipe 10 is connected to the concentrated portion.
さらに、槽1の水面上にはレール11が設けられ、その上
に曝気ブロワー12と駆動機13を搭載した台車14が走行可
能に乗っており、曝気ブロワー12の吐出部には空気配管
15が連結され、この空気配管15は垂直隔壁2の下まで伸
び、その先端には散気管からなる空気洗浄装置16が連結
され、この空気洗浄装置16は台車14の走行と共に水平方
向に移動するようになっている。Further, a rail 11 is provided on the water surface of the tank 1, and a trolley 14 having an aeration blower 12 and a drive unit 13 is movably mounted on the rail 11, and an air pipe is provided at a discharge portion of the aeration blower 12.
The air pipes 15 are connected to each other, the air pipes 15 extend below the vertical partition wall 2, and an air cleaning device 16 composed of an air diffusing pipe is connected to the tip of the air pipes 15. The air cleaning device 16 moves horizontally as the carriage 14 travels. It is like this.
また、垂直隔壁2で区画された各区画上部に備えられた
前記処理水流出部5には弁171を介して洗浄排水流出管1
7が連なっていて、前記処理水流出管6の弁61との切替
操作で処理水並びに洗浄排水の系外取り出しができるよ
うにしてある。即ち、浮上材による過層3が支持部
材4によって浮上を阻止された状態になっているので、
過層洗浄時に原水を上向流で流しながら、過層洗浄
時に原水を上向流で流しながら、弁61を閉じ、弁171を
開け、洗浄用空気を空気洗浄装置16から多量に吐出させ
ると、槽内で激しい気液混相流が発生し、材が流動化
する。その結果、それまで過層3内に捕捉されていた
SSと、増殖微生物によるSSが剥離され、SSを多量に含ん
だ洗浄水が洗浄排水流出管17から系外に流出してゆく。
このような操作を所要時間(通常1〜1.5hr)続ける
と、洗浄排水流出管17のSS濃度が所定値まで減少するの
で、この時点で空気洗浄用空気の供給を停止し、弁171
を閉じ、前記処理水流出管6の弁61を開けると、通常処
理状態に戻り、清澄処理水が流出する。The cleaning waste water outlet pipe through a valve 17 1 in the treated water outflow part 5 provided in each compartment upper partitioned by vertical partition walls 2 1
7 is not continuous, it is to allow the outside of the system is taken out of the treated water and detergent drain with switching operation of the valve 6 1 of the treated water outlet pipe 6. That is, since the overlayer 3 of the levitation material is in a state in which the levitation is blocked by the support member 4,
While flowing the raw water during the over-layer washed with upflow, while flowing the raw water during the over-layer washed with upflow, closing valve 61, opening the valve 17 1, large amounts discharging cleaning air from the air cleaning apparatus 16 Then, a violent gas-liquid mixed phase flow is generated in the tank, and the material is fluidized. As a result, it was trapped in the upper layer 3 until then.
The SS and the SS caused by the proliferating microorganisms are separated, and the wash water containing a large amount of SS flows out of the system through the wash drainage outflow pipe 17.
If such an operation is continued for a required time (usually 1 to 1.5 hours), the SS concentration of the cleaning drainage outflow pipe 17 decreases to a predetermined value, so at this point, the supply of the air for cleaning air is stopped and the valve 17 1
The closed and opened valve 6 1 of the treated water outlet pipe 6, returns to the normal processing state, clear treated water flows out.
なお、図示例のように、槽内にブロワー18に連なり、各
区画の過層3に空気を供給するための散気板19または
散気管を配設して、過層3で好気性生物膜処理を行う
場合に空気供給し、過層3で嫌気性生物膜処理を行う
場合には空気の供給を停止して用いる。In addition, like the illustrated example, a diffusing plate 19 or a diffusing pipe, which is connected to the blower 18 in the tank and is used to supply air to the overlayer 3 of each compartment, is provided, and the aerobic biofilm is formed in the overlayer 3. When the treatment is performed, air is supplied, and when the anaerobic biofilm treatment is performed in the overlayer 3, the air supply is stopped.
本発明によれば、従来技術の欠点を解決し、次のような
顕著な効果を奏するものである。According to the present invention, the drawbacks of the prior art are solved and the following remarkable effects are achieved.
従来の活性汚泥処理プロセスの嫌気槽に相当する槽の
みで、完全な浄化処理が可能であり、活性汚泥処理法に
おいて不可欠な沈殿池が不要になり、著しい省スペース
効果を維持できる。Complete purification can be performed only with a tank that corresponds to the anaerobic tank of the conventional activated sludge treatment process, the sedimentation tank that is indispensable in the activated sludge treatment method is not required, and a significant space saving effect can be maintained.
従来の活性汚泥処理法において、高度なSS除去が必要
なケースで不可欠であった、沈殿池のあとの砂過槽も
不要になり、しかも、常にSS10mg/l以下の清澄処理水が
得られる。In the conventional activated sludge treatment method, the sand filtration tank after the sedimentation basin, which was indispensable in the case where advanced SS removal is required, is no longer necessary, and the clarified water with SS 10 mg / l or less can always be obtained.
活性汚泥の沈降性に左右されずに、安定した高度なSS
除去が達成される。従って、維持管理も非常に容易にな
る。Stable advanced SS without being affected by sedimentation of activated sludge
Removal is achieved. Therefore, maintenance is also very easy.
過層の洗浄時に、原水の流入を停止する必要がな
く、その洗浄用水に処理水を消費する必要がなく、処理
水の生産効率が高い。It is not necessary to stop the inflow of raw water at the time of cleaning the overlayer, and it is not necessary to consume the treated water for the cleaning water, resulting in high production efficiency of the treated water.
連続過が可能であるので、回分過に比較して運転
操作が容易である。回分過法では、過層洗浄時に原
水供給を止め、処理水で洗浄し、洗浄排水を排出し、再
び原水の供給を行うという一連のシーケンス操作が不可
欠であるが、本発明ではこのような煩雑な操作が不要で
ある。Since continuous passing is possible, driving operation is easier than batch operation. In the batch filtration method, a series of sequence operations in which the raw water supply is stopped at the time of overlayer cleaning, the treated water is washed, the cleaning waste water is discharged, and the raw water is supplied again is essential, but in the present invention, such a complicated operation is required. Operation is unnecessary.
過層の洗浄排水の処分に別個の沈殿槽を必要としな
い。No separate settling tank is required to dispose of the wash effluent in the overlayer.
原水のSSが沈降されたのち、過層で処理が行われる
ので、過層の目詰まり進行が遅い。After the SS of the raw water is settled, the treatment is performed in the upper layer, so the clogging of the upper layer is slow.
過層の下部で、浮遊微生物による溶解性BOD除去を
行うことが出来るので、浮上材による過層へのBOD
負荷を小さく抑えることができる。この結果、過層に
おいて高度なBOD除去と効率的なNH4‐Nの硝化を達成す
ることができる。Soluble BOD can be removed by suspended microorganisms at the bottom of the overlayer, so the BOD to the overlayer by the floating material
The load can be kept small. As a result, a high degree of BOD removal and efficient NH 4 -N nitrification can be achieved in the overlayer.
図面は本発明の一実施例を示し、第1図は縦断側面図、
第2図は平面図、第3図は一部の拡大縦断面図である。 1……槽、2……垂直隔壁、3……過層、4……支持
部材、5……処理水流出部、6……処理水流出管、7…
…沈殿部、9……原水流入管、10……排泥管、11……レ
ール、12……曝気ブロワー、14……台車、15……空気配
管、16……空気洗浄装置、17……洗浄排水流出管、18…
…ブロワー、19……散気板。The drawings show an embodiment of the present invention, and FIG. 1 is a vertical sectional side view,
FIG. 2 is a plan view and FIG. 3 is a partially enlarged vertical sectional view. 1 ... Tank, 2 ... Vertical partition wall, 3 ... Overlayer, 4 ... Support member, 5 ... Treated water outlet, 6 ... Treated water outlet pipe, 7 ...
… Sedimentation part, 9 …… Raw water inflow pipe, 10 …… Mud pipe, 11 …… Rail, 12 …… Aeration blower, 14 …… Bogie, 15 …… Air piping, 16 …… Air cleaning device, 17 …… Wash drainage pipe, 18…
… Blower, 19… Air diffuser.
Claims (3)
槽内上方部が複数に垂直隔壁で区画され、各区画に浮上
材が保持されている各過層に流過させて、槽内上部
の処理水流出部から流出させて生物処理する方法におい
て、各区画の過層の下部から各過層の材を空気洗
浄する空気洗浄装置を水平移動させて空気を所定時間間
隔で各区画に対して順次供給して各過層を空気洗浄
し、他の過層部分では原水の浄化を行い、空気洗浄除
去されたSSを原水の上向流によって過層上部から洗浄
排水として槽内上部の洗浄排水流出部から取り出すよう
にしたことを特徴とする有機性汚水の生物処理方法。1. Raw water flows in from the lower part of the tank to flow upward,
In the method of biological treatment by allowing the upper part of the tank to be partitioned into a plurality of vertical partition walls, allowing the floating material to pass through each partition to pass through each overlayer, and flowing out from the treated water outflow part of the upper part of the tank, From the lower part of the overlayer of each section, horizontally move the air cleaning device that air-cleans the material of each overlayer, and sequentially supply air to each section at predetermined time intervals to wash each overlayer with air. Organic water is characterized by purifying raw water in the upper layer and removing SS that has been air-cleaned and removed from the upper portion of the upper layer as cleaning drain by upward flow of raw water from the outlet of the cleaning drain in the upper part of the tank. Biological treatment method for sewage.
直隔壁によって複数に区画し、各区画内に浮上材によ
る過層を浸漬保持すると共に各区画内の過層の上部
にそれぞれ処理水流出部と、洗浄排水流出部とを設け、
これらの各区画の過層の下部に各過層の材を空気
洗浄するための空気を各区画に対して順々供給する空気
洗浄装置を水平移動可能に配備し、前記材から空気洗
浄除去されたSSを材層上部から洗浄排水流出部で排出
する構成としたことを特徴とする有機性汚水の生物処理
装置。2. An upper part of a tank having a raw water inflow part at a lower part is divided into a plurality of parts by vertical partition walls, and an upper layer of a levitation material is dipped and held in each part and each upper part of the upper part in each part. A treated water outflow section and a cleaning drainage outflow section are provided,
An air cleaning device that supplies air for cleaning the air of each overlayer to each of the sections is installed horizontally below the overlayer of each of these sections so that the air is removed from the material by air cleaning. The biological treatment device for organic sewage is characterized in that SS is discharged from the upper part of the material layer at the washing drainage outflow part.
部とした請求項2記載の有機性汚水の生物処理装置。3. The biological treatment apparatus for organic sewage according to claim 2, wherein a lower part of each compartment in the tank is a communicating part which is a communicating part.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4590790A JPH0673676B2 (en) | 1990-01-24 | 1990-02-28 | Method and apparatus for biological treatment of organic wastewater |
Applications Claiming Priority (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2-12501 | 1990-01-24 | ||
| JP1250190 | 1990-01-24 | ||
| JP4590790A JPH0673676B2 (en) | 1990-01-24 | 1990-02-28 | Method and apparatus for biological treatment of organic wastewater |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH03249993A JPH03249993A (en) | 1991-11-07 |
| JPH0673676B2 true JPH0673676B2 (en) | 1994-09-21 |
Family
ID=26348133
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP4590790A Expired - Fee Related JPH0673676B2 (en) | 1990-01-24 | 1990-02-28 | Method and apparatus for biological treatment of organic wastewater |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0673676B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102225822B (en) * | 2011-04-13 | 2012-07-25 | 哈尔滨工业大学 | Artificial reinforced ecological filter bed, and method for treating polluted river water through the artificial reinforced ecological filter bed |
| WO2017212591A1 (en) * | 2016-06-08 | 2017-12-14 | 株式会社アイエンス | Wastewater purifying system |
-
1990
- 1990-02-28 JP JP4590790A patent/JPH0673676B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH03249993A (en) | 1991-11-07 |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| LAPS | Cancellation because of no payment of annual fees |