JPH1128490A - Fluidized bed type sewage treatment device - Google Patents

Fluidized bed type sewage treatment device

Info

Publication number
JPH1128490A
JPH1128490A JP9186826A JP18682697A JPH1128490A JP H1128490 A JPH1128490 A JP H1128490A JP 9186826 A JP9186826 A JP 9186826A JP 18682697 A JP18682697 A JP 18682697A JP H1128490 A JPH1128490 A JP H1128490A
Authority
JP
Japan
Prior art keywords
carrier
tank
treated water
aeration tank
separation tank
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
JP9186826A
Other languages
Japanese (ja)
Inventor
Masato Fujino
正人 藤野
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.)
JFE Engineering Corp
Original Assignee
NKK Corp
Nippon Kokan Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by NKK Corp, Nippon Kokan Ltd filed Critical NKK Corp
Priority to JP9186826A priority Critical patent/JPH1128490A/en
Publication of JPH1128490A publication Critical patent/JPH1128490A/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

  • Biological Treatment Of Waste Water (AREA)

Abstract

PROBLEM TO BE SOLVED: To easily execute the sepn. of microorganism adhesion carriers and to facilitate maintenance and control by providing the device with a means for withdrawing the microorganism adhesion carriers in the treated water gathered in the bottom of a carrier sepn. tank and returning the carriers to an aeration tank by the vortex generated by a means of admitting the treated water to the carrier sepn. tank and forming the vortex. SOLUTION: The sewage introduced into the aeration tank 1 is decomposed by microorganisms and purified within the tank where the microorganism adhesion carriers flow by blowing air therein from an air diffuser 2. The treated water flows together with the microorganism adhesion carriers and the suspended sewage through an inflow channel 11 into the carrier sepn. tank 10. At this time, the inflow rate and flow velocity of the treated water are adequately set by the control of a valve 12 and the vortex is formed in the carrier sepn. tank 10 by this inflow, by which the microorganism adhesion carriers are gathered to the center of the vortex and are stagnated at the bottom. The floating up microorganism adhesion carriers are gathered together with the floating materials by a trap and are dropped downward of a water collecting tray 14 where the carriers settle and accumulate at the bottom. The accumulated microorganism adhesion carriers 40 and solid contents are withdrawn and are returned from a carrier return pipe 19 to the upstream side of the aeration tank 1.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、槽内に微生物を付
着させた粒子(以下、微生物付着担体と言う)を流動さ
せながら、汚水を好気的に処理する流動床式汚水処理装
置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a fluidized bed type sewage treatment apparatus for aerobically treating sewage while fluidizing particles (hereinafter referred to as microorganism-adhered carriers) having microorganisms attached thereto in a tank.

【0002】[0002]

【従来の技術】槽内に微生物付着担体を存在させ、空気
を吹き込んで、この微生物付着担体を流動させながら汚
水と接触させることにより、汚水中の有機物質を生物学
的に分解処理する流動床式汚水処理装置は、微生物を付
着させる担体粒子の表面積が非常に大きく、従って、槽
内に多量の微生物を保持することができるので、コンパ
クトな装置であると共に、高負荷操業が可能であること
など、多くの利点を有し、注目されている装置である。
2. Description of the Related Art A fluidized bed for biologically decomposing organic substances in sewage by bringing microbial-adhered carriers into a tank, blowing air into the tank, and bringing the microorganism-adhered carriers into contact with sewage while flowing. The sewage treatment system has a very large surface area of the carrier particles to which the microorganisms are attached, and therefore can hold a large amount of microorganisms in the tank. Therefore, the device is compact and capable of high-load operation. It is a device that has many advantages such as, for example, attention.

【0003】図5は従来の流動床式汚水処理装置の一例
を示す断面図である。この装置においては、曝気槽1の
底部に散気器2が設けられており、槽内の汚水中に空気
が吹き込まれるようになっている。40は汚水中を流動
している微生物付着担体を示す。そして、処理水の出口
には、微生物付着担体40の流出を阻止するためのスク
リーン30が設けられている。
FIG. 5 is a sectional view showing an example of a conventional fluidized bed type sewage treatment apparatus. In this device, an air diffuser 2 is provided at the bottom of an aeration tank 1 so that air is blown into sewage in the tank. Reference numeral 40 denotes a microorganism-adhering carrier flowing in sewage. At the outlet of the treated water, a screen 30 for preventing the microorganism-adhering carrier 40 from flowing out is provided.

【0004】なお、流動床式汚水処理装置においては、
微生物付着担体を流動させるエネルギーを節減するため
に、微生物を付着させる粒子の材料はできるだけ比重の
小さい物質の中から選定され、例えば、プラスチックや
活性炭などで、比重が水の比重より若干大きい程度のも
のが使用される。また、その粒子は数mm程度の大きさ
のものである。
[0004] In a fluidized bed type sewage treatment apparatus,
In order to save energy for flowing the microorganism-adhering carrier, the material of the particles to which the microorganisms are attached is selected from substances having a specific gravity as small as possible.For example, in plastics or activated carbon, the specific gravity is slightly larger than the specific gravity of water. Things are used. The particles have a size of about several mm.

【0005】上記装置により汚水を処理する場合、曝気
槽1へ汚水を流入させ、散気器2から空気を吹き込んで
微生物付着担体40を流動させながら汚水を浄化処理す
る。浄化された処理水は浮遊していた汚泥と共にスクリ
ーン30を通過して排出し、汚泥を分離除去するための
沈澱池へ送られる。微生物付着担体40は流出を阻止さ
れて槽内に残留し、再び流動しながら槽内を循環して汚
水を浄化処理する働きをする。
When sewage is treated by the above-described apparatus, sewage is introduced into the aeration tank 1, and air is blown from the aerator 2 to purify the sewage while flowing the microorganism-attached carrier 40. The purified treated water is discharged together with the suspended sludge through the screen 30 and sent to a sedimentation basin for separating and removing the sludge. The microorganism-adhering carrier 40 is prevented from flowing out, remains in the tank, and circulates in the tank while flowing again to purify sewage.

【0006】[0006]

【発明が解決しようとする課題】前述のように、微生物
付着担体は小さな粒子であり、従って、微生物付着担体
を分離するスクリーンの目の幅は非常に狭く、その上、
汚水中には様々な固形物が含まれている。このため、上
記従来の装置においては、スクリーンが目詰まりし、操
業に支障をきたすと言う問題が発生する。
As described above, the microorganism-attached carriers are small particles, and therefore, the screen width for separating the microorganism-attached carriers is very narrow.
Sewage contains various solids. For this reason, in the above-mentioned conventional apparatus, there is a problem that the screen is clogged and the operation is hindered.

【0007】スクリーンに固形物が詰まり始まると、目
詰まりした固形物に微生物膜が生成し、その上に他の固
形物が付着し易くなる。そして、目詰まりの度合いは次
第に激しくなる。スクリーンが目詰まりすると、その通
水面積が減少して曝気槽の水位が上昇し、所定の処理能
力を維持することができなくなるので、しばしば、スク
リーンの清掃を実施しなければならない。この際、清掃
を要するスクリーンの箇所が水中にあるので、その作業
には多くの労力を要する。また、スクリーンを目詰まり
させたものに毛髪などの繊維状のものがあった場合、繊
維状のものはスクリーンに絡みついているので、その除
去は容易ではない。特に、大規模の汚水処理装置におい
ては、スクリーンも大きく、また、その設置数も多いの
で、スクリーンの清掃作業には更に多大の労力を要す
る。
[0007] When the solids start to clog the screen, a microbial membrane is formed on the clogged solids, and other solids tend to adhere thereon. Then, the degree of clogging becomes increasingly severe. When the screen is clogged, the water passing area decreases, the water level in the aeration tank rises, and it becomes impossible to maintain a predetermined processing capacity. Therefore, the screen must often be cleaned. At this time, since the portion of the screen that needs to be cleaned is underwater, the work requires a lot of labor. Also, if the screen is clogged, there is a fibrous material such as hair, and the fibrous material is not easily removed because it is entangled with the screen. In particular, in a large-scale sewage treatment apparatus, since the screen is large and the number of the screens is large, the cleaning work of the screen requires much more labor.

【0008】本発明は、微生物付着担体の分離が容易に
行われ、維持管理が容易な流動床式汚水処理装置を提供
することを目的とする。
[0008] An object of the present invention is to provide a fluidized bed type sewage treatment apparatus in which a microorganism-adhered carrier can be easily separated and maintenance is easy.

【0009】[0009]

【課題を解決するための手段】上記の目的を達成するた
めに、第一の発明に係る装置は、散気器を備えた曝気槽
と、円筒部の下にすり鉢状の円錐部が延設された形状を
なし、曝気槽から流入された処理水中の微生物付着担体
を分離するための担体分離槽と、この担体分離槽の円筒
部に接線方向に向かって取り付けられ、曝気槽から流入
される処理水を担体分離槽へ流入させて担体分離槽内に
渦流を形成させる手段と、この渦流を形成させる手段に
よって発生させた渦流により担体分離槽の底部に集めら
れた処理水中の微生物付着担体を抜き出して曝気槽へ返
送する手段とを具備している。
In order to achieve the above object, an apparatus according to a first aspect of the present invention comprises an aeration tank provided with a diffuser and a mortar-shaped conical portion extending below a cylindrical portion. A carrier separation tank for separating the microorganism-adhered carrier in the treated water flowing from the aeration tank, and a tangential direction attached to the cylindrical portion of the carrier separation tank, which flows in from the aeration tank. A means for causing the treated water to flow into the carrier separation tank to form a vortex in the carrier separation tank, and a vortex generated by the means for forming the vortex to remove the microorganism-adhered carrier in the treated water collected at the bottom of the carrier separation tank. Means for extracting and returning it to the aeration tank.

【0010】第二の発明に係る装置は、第一の発明にお
いて、担体分離槽と曝気槽が連通して設置されており、
担体分離槽の処理水排出管が曝気槽の操業時の水位より
低いレベルに設けられて、曝気槽と担体分離槽の間に水
位差ができるように構成され、この水位差によって曝気
槽の処理水が担体分離槽へ流入するように構成されてい
る。
[0010] In the apparatus according to the second invention, in the first invention, the carrier separation tank and the aeration tank are installed in communication with each other.
The treated water discharge pipe of the carrier separation tank is provided at a level lower than the water level at the time of operation of the aeration tank, so that a water level difference is formed between the aeration tank and the carrier separation tank. The water is configured to flow into the carrier separation tank.

【0011】第三の発明に係る装置は、第二の発明にお
いて、担体分離槽が曝気槽の下流側端部に接続されてい
る。
According to a third aspect of the present invention, in the second aspect, the carrier separation tank is connected to a downstream end of the aeration tank.

【0012】第四の発明に係る装置は、第二の発明にお
いて、担体分離槽が曝気槽内に設置されている。
According to a fourth aspect of the present invention, in the second aspect, the carrier separation tank is provided in the aeration tank.

【0013】上記各発明においては、担体分離槽を設
け、この槽内に渦流を形成させて、その渦流の中心に固
形分を集める方式によって微生物付着担体を分離するの
で、その分離が無理なく、容易に行われる。この際、曝
気槽から排出する処理水中には微生物付着担体の他に汚
泥が含まれており、これらの固形分が一緒に担体分離槽
へ導入されるが、微生物付着担体と汚泥は分離され、微
生物付着担体だけが抜き出される。すなわち、微生物付
着担体は沈降して担体分離槽の底部に集められるが、汚
泥は比重が極めて水に近い値を有し、沈降速度が非常に
遅いものであるので、沈降せず、処理水と共に排出す
る。
In each of the above inventions, a carrier separation tank is provided, a vortex is formed in the tank, and the microorganism-adhered carrier is separated by a method of collecting solids at the center of the vortex. Easy to do. At this time, the treated water discharged from the aeration tank contains sludge in addition to the microorganism-attached carrier, and these solids are introduced together into the carrier separation tank, but the microorganism-attached carrier and the sludge are separated, Only the microorganism-adhered carrier is withdrawn. In other words, the microorganism-adhered carrier settles and is collected at the bottom of the carrier separation tank. Discharge.

【0014】担体分離槽においては、曝気槽との間に水
位差があるので、処理水は、動力を用いることなく、渦
流を形成させることができる流入速度で導入される。
Since there is a water level difference between the carrier separation tank and the aeration tank, the treated water is introduced at an inflow velocity capable of forming a vortex without using power.

【0015】[0015]

【発明の実施の形態】図1は本発明の流動床式汚水処理
装置に係る実施の形態の一例を示す平面図であり、図2
はその概略の断面を示す図である。図1および図2にお
いて、1は曝気槽、2は散気器、40は微生物付着担体
である。この装置においては、曝気槽1の下流側に、処
理水中の微生物付着担体を分離するための担体分離槽1
0が連設されている。
FIG. 1 is a plan view showing an example of an embodiment of a fluidized-bed sewage treatment apparatus of the present invention, and FIG.
FIG. 2 is a diagram showing a schematic cross section thereof. 1 and 2, 1 is an aeration tank, 2 is an aerator, and 40 is a microorganism-adhering carrier. In this apparatus, a carrier separation tank 1 for separating microorganism-attached carriers in treated water is provided downstream of the aeration tank 1.
0 is continuously provided.

【0016】担体分離槽10は図4に示す構造のもので
あって、円筒部の下にすり鉢状の円錐部が延設された形
状に形成されている。図4において、11は担体分離槽
内に曝気槽の処理水を導入して渦流を形成させる手段で
ある流入渠であって、担体分離槽の円筒部に接線方向に
向けて取り付けられている。13は上部が水面上に位置
するように取り付けられた潜り堰、14は排出させる処
理水を集める集水盆、15は集水盆14の上部に形成さ
れた越流堰、16は処理水排出管、17は浮上物を集め
て集水盆14の下方へ落とすためのトラップ、18は微
生物付着担体の抜き出し口である。
The carrier separation tank 10 has the structure shown in FIG. 4, and is formed in a shape in which a mortar-shaped conical part is extended below a cylindrical part. In FIG. 4, reference numeral 11 denotes an inflow culvert, which is a means for introducing treated water from an aeration tank into a carrier separation tank to form a vortex, and is attached to a cylindrical portion of the carrier separation tank in a tangential direction. 13 is a submerged weir mounted so that the upper part is located on the water surface, 14 is a catchment basin for collecting treated water to be discharged, 15 is an overflow weir formed on the upper part of the catchment basin 14, and 16 is treated water discharge. A pipe 17 is a trap for collecting the floating matter and dropping it below the catchment basin 14, and 18 is an outlet for extracting a microorganism-adhering carrier.

【0017】上記構造の担体分離槽10が設置された図
1および図2の装置において、流入渠11が曝気槽1の
側壁を貫通して接続されており、担体分離槽10と曝気
槽1は連通している。また、担体分離槽10の処理水排
出管16は曝気槽1の操業時の水位より低いレベルに設
けられている。このため、曝気槽1の処理水が水位差に
よって担体分離槽10へ流入するようになっている。ま
た、流入渠11が担体分離槽10の接線方向に接続され
ているので、担体分離槽10内に渦流が形成され、この
渦流によって微生物付着担体が中心に集められ、底部に
溜まるようになっている。図中、12は処理水の流入量
を調節するための弁である。
In the apparatus shown in FIGS. 1 and 2 in which the carrier separation tank 10 having the above structure is installed, the inflow culvert 11 is connected through the side wall of the aeration tank 1, and the carrier separation tank 10 and the aeration tank 1 are connected to each other. Communicating. Further, the treated water discharge pipe 16 of the carrier separation tank 10 is provided at a level lower than the water level during the operation of the aeration tank 1. For this reason, the treated water in the aeration tank 1 flows into the carrier separation tank 10 due to a difference in water level. Further, since the inflow culvert 11 is connected in a tangential direction of the carrier separation tank 10, a vortex is formed in the carrier separation tank 10, and the microorganism-adhered carrier is collected at the center by the vortex, and accumulates at the bottom. I have. In the figure, reference numeral 12 denotes a valve for adjusting the flow rate of the treated water.

【0018】また、19は担体分離槽10の底部と曝気
槽1を接続させた担体返送管、20は担体返送管19中
へ処理水を噴射するための処理水ポンプ、21は処理水
抜き出し管、22は処理水噴射管であり、この担体返送
管19、処理水ポンプ20、処理水抜き出し管21、お
よび処理水噴射管22によって、担体分離槽10の底部
に集められた微生物付着担体を抜き出して曝気槽へ返送
する手段が構成されている。なお、処理水噴射管22は
その先端部が担体返送管19中へ挿入されており、その
挿入部がエダクターと同様の作用をする構造になってい
る。
Reference numeral 19 denotes a carrier return pipe connecting the bottom of the carrier separation tank 10 and the aeration tank 1, 20 denotes a treated water pump for injecting treated water into the carrier return pipe 19, and 21 denotes a treated water discharge pipe. , 22 are treated water injection pipes, and the microorganism return carriers collected at the bottom of the carrier separation tank 10 are extracted by the carrier return pipe 19, the treated water pump 20, the treated water extraction pipe 21, and the treated water injection pipe 22. Means for returning to the aeration tank. The treated water injection pipe 22 has a distal end inserted into the carrier return pipe 19, and the inserted portion has a structure that performs the same operation as the eductor.

【0019】このような構成による装置による汚水処理
は、次のように行われる。曝気槽1へ導入された汚水
は、散気器2から空気が吹き込まれ微生物付着担体が流
動している槽内で微生物によって分解され、浄化され
る。処理水は微生物付着担体および浮遊している汚泥と
共に、流入渠11を経由し担体分離槽10内へ流入す
る。この際、必要に応じて、弁12の調節が行われ、処
理水の流入量とその流速が適度に設定される。この処理
水の流入によって、担体分離槽10内に渦流が形成さ
れ、微生物付着担体40が渦流の中心に集められて底部
に溜まる。また、浮上していた微生物付着担体があった
場合、この微生物付着担体は浮上物と共にトラップ17
によって集められて、集水盆14の下方へ落とされ、沈
降して底部に溜まる。底部に溜まった微生物付着担体4
0と固形分は抜き出され、担体返送管19を経て曝気槽
1の上流側へ戻される。
The sewage treatment by the apparatus having such a configuration is performed as follows. The sewage introduced into the aeration tank 1 is decomposed and purified by microorganisms in a tank in which air is blown from the diffuser 2 and the microorganism-adhering carrier is flowing. The treated water flows into the carrier separation tank 10 via the inflow culvert 11 together with the microorganism-adhering carrier and the suspended sludge. At this time, if necessary, the valve 12 is adjusted, and the inflow amount of the treated water and the flow speed thereof are appropriately set. Due to the inflow of the treated water, a vortex is formed in the carrier separation tank 10, and the microorganism-adhered carriers 40 are collected at the center of the vortex and accumulated at the bottom. If there is a microorganism-adhering carrier that has floated, the microorganism-adhering carrier is trapped together with the floating material in a trap 17.
And fall below the catchment basin 14 and settle and collect at the bottom. Microorganism-adhering carrier 4 accumulated at the bottom
Zero and solids are extracted and returned to the upstream side of the aeration tank 1 through the carrier return pipe 19.

【0020】微生物付着担体40の返送に際しては、処
理水ポンプ20によって担体返送管19内へ処理水が噴
射される。そして、エダクターと同様の作用によって、
担体分離槽10底部の微生物付着担体40が抜き出さ
れ、輸送される。このような方法で微生物付着担体を輸
送すれば、微生物付着担体に付着した生物膜が剥がれた
り、担体自体が破壊されたりする問題の発生が最小限に
とどめられる。
At the time of returning the microorganism-adhered carrier 40, the treated water is injected into the carrier return pipe 19 by the treated water pump 20. And by the same action as the eductor,
The microorganism-adhered carrier 40 at the bottom of the carrier separation tank 10 is extracted and transported. When the microorganism-adhered carrier is transported by such a method, the occurrence of problems such as peeling of the biofilm adhered to the microorganism-adhered carrier and destruction of the carrier itself is minimized.

【0021】一方、処理水は浮遊している汚泥と一緒に
潜り堰13を潜って集水盆14内へ流れ込み、処理水排
出管16から沈澱池(図示せず)へ送られる。
On the other hand, the treated water flows into the catchment basin 14 through the dive weir 13 together with the suspended sludge, and is sent from the treated water discharge pipe 16 to a sedimentation basin (not shown).

【0022】図3は本発明の流動床式汚水処理装置に係
る他の実施の形態の断面を示す図である。図3におい
て、図1、図2、および図4で説明した部分について
は、同一の符号を付し説明を省略する。この実施の形態
においては、担体分離槽10が曝気槽内に設置されてい
る。このため、設置面積を狭めることができると言う効
果がもたらされる。
FIG. 3 is a sectional view showing another embodiment of the fluidized bed sewage treatment apparatus of the present invention. 3, the same reference numerals are given to the portions described in FIGS. 1, 2, and 4, and the description is omitted. In this embodiment, a carrier separation tank 10 is provided in an aeration tank. For this reason, there is an effect that the installation area can be reduced.

【0023】[0023]

【発明の効果】本発明においては、槽内に渦流を発生さ
せる担体分離槽を設け、固形分をその渦流の中心に集め
て底部に溜める方式によって微生物付着担体を分離する
ので、その分離が無理なく、容易に行われる。このた
め、清掃などの作業を行う必要がなく、装置の維持管理
が極めて容易である。
According to the present invention, a carrier separation tank for generating a vortex is provided in the tank, and the microorganism-adhered carrier is separated by a method of collecting solids at the center of the vortex and collecting the solids at the bottom. Not easily done. Therefore, there is no need to perform operations such as cleaning, and maintenance and management of the apparatus is extremely easy.

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

【図1】本発明の流動床式汚水処理装置に係る実施の形
態の一例を示す平面図である。
FIG. 1 is a plan view showing an example of an embodiment according to a fluidized-bed sewage treatment apparatus of the present invention.

【図2】図1の装置の概略の断面図である。FIG. 2 is a schematic sectional view of the apparatus of FIG. 1;

【図3】本発明の流動床式汚水処理装置に係る他の実施
の形態を示す概略の断面図である。
FIG. 3 is a schematic cross-sectional view showing another embodiment of the fluidized bed sewage treatment apparatus of the present invention.

【図4】図1、図2、および図3における担体分離槽の
構造を示す図である。
FIG. 4 is a view showing a structure of a carrier separation tank in FIGS. 1, 2 and 3;

【図5】従来の流動床式汚水処理装置の一例を示す断面
図である。
FIG. 5 is a cross-sectional view showing an example of a conventional fluidized bed sewage treatment apparatus.

【符号の説明】[Explanation of symbols]

1 曝気槽 2 散気器 10 担体分離槽 11 流入渠 12 弁 16 処理水排出管 19 担体返送管 20 処理水ポンプ 21 処理水抜き出し管 22 処理水噴射管 40 微生物付着担体 REFERENCE SIGNS LIST 1 aeration tank 2 diffuser 10 carrier separation tank 11 inflow culvert 12 valve 16 treated water discharge pipe 19 carrier return pipe 20 treated water pump 21 treated water drain pipe 22 treated water injection pipe 40 microorganism adhered carrier

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 曝気槽内に微生物付着担体を存在させ、
空気を吹き込んで汚水中の有機物質を生物学的に分解処
理する流動床式汚水処理装置であって、散気器を備えた
曝気槽と、円筒部の下にすり鉢状の円錐部が延設された
形状をなし、曝気槽から流入された処理水中の微生物付
着担体を分離するための担体分離槽と、この担体分離槽
の円筒部に接線方向に向かって取り付けられ、曝気槽か
ら流入される処理水を担体分離槽へ流入させて担体分離
槽内に渦流を形成させる手段と、この渦流を形成させる
手段によって発生させた渦流により担体分離槽の底部に
集められた処理水中の微生物付着担体を抜き出して曝気
槽へ返送する手段とを具備したことを特徴とする流動床
式汚水処理装置。
1. A microorganism-attached carrier is present in an aeration tank,
A fluidized-bed type sewage treatment system that blows air to biologically decompose organic substances in sewage, with an aeration tank equipped with an aerator and a mortar-shaped conical section below the cylindrical section. A carrier separation tank for separating the microorganism-adhered carrier in the treated water flowing from the aeration tank, and a tangential direction attached to the cylindrical portion of the carrier separation tank, which flows in from the aeration tank. A means for causing the treated water to flow into the carrier separation tank to form a vortex in the carrier separation tank, and a vortex generated by the means for forming the vortex to remove the microorganism-adhered carrier in the treated water collected at the bottom of the carrier separation tank. A fluidized bed sewage treatment apparatus, comprising: means for extracting and returning to an aeration tank.
【請求項2】 担体分離槽と曝気槽が連通して設置され
ており、担体分離槽の処理水排出管が曝気槽の操業時の
水位より低いレベルに設けられて、曝気槽と担体分離槽
の間に水位差ができるように構成され、この水位差によ
って曝気槽の処理水が担体分離槽へ流入するように構成
されたことを特徴とする請求項1に記載の流動床式汚水
処理装置。
2. A carrier separation tank and an aeration tank are provided in communication with each other, and a treated water discharge pipe of the carrier separation tank is provided at a level lower than a water level during operation of the aeration tank. The fluidized bed type sewage treatment apparatus according to claim 1, wherein a water level difference is formed between the fluidized bed and the water level difference, whereby the treated water in the aeration tank flows into the carrier separation tank. .
【請求項3】 担体分離槽が曝気槽の下流側端部に接続
されていることを特徴とする請求項2に記載の流動床式
汚水処理装置。
3. The fluidized bed sewage treatment apparatus according to claim 2, wherein the carrier separation tank is connected to a downstream end of the aeration tank.
【請求項4】 担体分離槽が曝気槽内に設置されている
ことを特徴とする請求項2に記載の流動床式汚水処理装
置。
4. The fluidized bed sewage treatment apparatus according to claim 2, wherein the carrier separation tank is provided in the aeration tank.
JP9186826A 1997-07-11 1997-07-11 Fluidized bed type sewage treatment device Pending JPH1128490A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9186826A JPH1128490A (en) 1997-07-11 1997-07-11 Fluidized bed type sewage treatment device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9186826A JPH1128490A (en) 1997-07-11 1997-07-11 Fluidized bed type sewage treatment device

Publications (1)

Publication Number Publication Date
JPH1128490A true JPH1128490A (en) 1999-02-02

Family

ID=16195297

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9186826A Pending JPH1128490A (en) 1997-07-11 1997-07-11 Fluidized bed type sewage treatment device

Country Status (1)

Country Link
JP (1) JPH1128490A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000296396A (en) * 1999-04-14 2000-10-24 Kobe Steel Ltd Biological water treating apparatus and biological water treatment
JP2003080284A (en) * 2001-09-14 2003-03-18 Sumitomo Heavy Ind Ltd Wastewater treatment equipment
JP2011507682A (en) * 2007-12-19 2011-03-10 サウジ アラビアン オイル カンパニー Suspended solvent granular activated carbon membrane bioreactor system and process
US7946392B2 (en) 2005-01-11 2011-05-24 Inventio Ag Drive for an elevator door with a displacement curve adapted to the air flows in the shaft
CN110240291A (en) * 2019-07-18 2019-09-17 郝津晶 A kind of super Inka aeration microbial biochemical bed and sewage disposal system

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000296396A (en) * 1999-04-14 2000-10-24 Kobe Steel Ltd Biological water treating apparatus and biological water treatment
JP2003080284A (en) * 2001-09-14 2003-03-18 Sumitomo Heavy Ind Ltd Wastewater treatment equipment
US7946392B2 (en) 2005-01-11 2011-05-24 Inventio Ag Drive for an elevator door with a displacement curve adapted to the air flows in the shaft
JP2011507682A (en) * 2007-12-19 2011-03-10 サウジ アラビアン オイル カンパニー Suspended solvent granular activated carbon membrane bioreactor system and process
CN110240291A (en) * 2019-07-18 2019-09-17 郝津晶 A kind of super Inka aeration microbial biochemical bed and sewage disposal system

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