JPH0225675B2 - - Google Patents

Info

Publication number
JPH0225675B2
JPH0225675B2 JP60034146A JP3414685A JPH0225675B2 JP H0225675 B2 JPH0225675 B2 JP H0225675B2 JP 60034146 A JP60034146 A JP 60034146A JP 3414685 A JP3414685 A JP 3414685A JP H0225675 B2 JPH0225675 B2 JP H0225675B2
Authority
JP
Japan
Prior art keywords
pipe
fluidized bed
air lift
treatment
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.)
Expired - Lifetime
Application number
JP60034146A
Other languages
Japanese (ja)
Other versions
JPS61192390A (en
Inventor
Hideki Iwabe
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kubota Corp
Original Assignee
Kubota Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kubota Corp filed Critical Kubota Corp
Priority to JP60034146A priority Critical patent/JPS61192390A/en
Publication of JPS61192390A publication Critical patent/JPS61192390A/en
Publication of JPH0225675B2 publication Critical patent/JPH0225675B2/ja
Granted 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)

Description

【発明の詳細な説明】 「産業上の利用分野」 本発明は、担体粒子の自動洗浄機構を備えた半
流動層式廃水処理装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION "Field of Industrial Application" The present invention relates to a semi-fluidized bed wastewater treatment apparatus equipped with an automatic cleaning mechanism for carrier particles.

「従来の技術」 廃水の微生物による処理において、下部が流動
化され上部が静止している微粒状の担体粒子の層
を形成した半流動層式廃水処理装置を使用するこ
とは知られている。この半流動層による処理は、
流動層部と固定層部とを併せもつことにより、流
動層部での完全混合による高速処理と固定層部で
の密な微生物層による仕上げ処理との双方の長所
が得られ、槽単位容積当りの微生物濃度を高める
ことができ、高速処理とともに処理槽の小型化が
可能となる、という利点がある。
``Prior Art'' In the microbial treatment of wastewater, it is known to use a semi-fluidized bed wastewater treatment device in which a bed of fine carrier particles is formed, the lower part of which is fluidized and the upper part is stationary. This semi-fluid bed treatment is
By having both a fluidized bed section and a fixed bed section, it is possible to obtain the advantages of both high-speed processing due to complete mixing in the fluidized bed section and finishing processing due to a dense microbial layer in the fixed bed section, and it is possible to achieve a This method has the advantage of increasing the concentration of microorganisms, enabling high-speed processing, and miniaturization of the processing tank.

しかし、この半流動層式の処理においては、処
理が進むにつれて廃水中の浮遊物質或は担体粒子
から剥離した微生物フロツクなどにより固定層部
が閉塞され、廃水処理を一時中断し、しばしば洗
浄処理をしなければならないという難点がある。
However, in this semi-fluidized bed type treatment, as the treatment progresses, the fixed bed becomes clogged by suspended solids in the wastewater or microbial flocs detached from carrier particles, causing the wastewater treatment to be temporarily interrupted and cleaning treatment often to be performed. The problem is that it has to be done.

このような難点を解決するため、固定層部を拘
束する多孔板を上下に移動自在に設け、固定層部
が閉塞されるようになると多孔板を上昇させて固
定層部の流動化を図り、閉塞の原因をなしている
浮遊物質や微生物フロツクなどを多孔板の目を通
して排出させるようにするという提案がなされた
(特開昭55−106594号公報、特公昭59−32197号公
報等参照)。しかし、その方法においても、多孔
板を上昇して固定層部を流動化するクリーニング
サイクル時には廃水処理を中断して洗浄しなけれ
ばならず、依然として従来の難点を解決するとい
うことには至つていない。
In order to solve this problem, we installed a perforated plate that restrains the fixed layer section so that it can move up and down, and when the fixed layer section becomes blocked, the perforated plate is raised to fluidize the fixed layer section. A proposal has been made to discharge suspended solids, microbial flocs, etc. that cause blockages through the holes of the perforated plate (see Japanese Patent Laid-Open Nos. 55-106594, 1982-32197, etc.). However, even with this method, during the cleaning cycle in which the perforated plate is raised to fluidize the fixed bed, wastewater treatment must be interrupted for cleaning, and it still does not solve the problems of the conventional method. do not have.

「本考案が解決しようとする問題点」 前述した廃水の半流動層による処理における大
きな問題点は、処理槽内の流動層部や固定層部に
目詰まりが生じることなく廃水の連続処理が能率
よく行えるようにすることにある。本発明はかか
る問題点を解決するためになされたもので、廃水
の処理中において、固定層部の担体粒子を遂次洗
浄して返送する機構を処理槽中に設けることによ
り、固定層部の目詰りを防ぎつつ廃水の連続処理
を可能とし、廃水の微生物学的処理を能率的に行
えるようにするとともに、操作や保守が容易な半
流動層式廃水処理装置を提供しようとするもので
ある。
``Problems to be solved by the present invention'' The major problem with the semi-fluidized bed treatment of wastewater mentioned above is that continuous treatment of wastewater is efficient without clogging the fluidized bed or fixed bed in the treatment tank. The goal is to be able to perform well. The present invention has been made to solve this problem, and by providing a mechanism in the treatment tank to sequentially wash and return the carrier particles in the fixed bed during wastewater treatment, the fixed bed can be washed and returned. The objective is to provide a semi-fluidized bed wastewater treatment device that enables continuous treatment of wastewater while preventing clogging, enables efficient microbiological treatment of wastewater, and is easy to operate and maintain. .

「問題点を解決するための手段」 流動層部とその上部に固定層部を形成してなる
半流動層式処理層の中心部に、気体の送入される
エアリフト管を立設し、該エアリフト管の下端開
口に、上端が固定層部内に開口した担体粒子導入
管を連通させるとともに、前記エアリフト管の上
端には、これより流出する担体を流動層部に返送
するとともに、流出する洗浄汚水を槽外へ排出す
る手段を設けたことを特徴とするものである。
``Means for solving the problem'' An air lift pipe through which gas is introduced is installed upright in the center of a semi-fluidized bed treatment bed consisting of a fluidized bed section and a fixed bed section above the fluidized bed section. A carrier particle introduction pipe whose upper end opens into the fixed bed section is connected to the lower end opening of the air lift pipe, and the carrier particles flowing out from the pipe are returned to the fluidized bed section, and the washed wastewater flowing out is connected to the upper end of the air lift pipe. This is characterized by providing a means for discharging the water out of the tank.

「実施例」 以下、本発明装置の実施例について図面を参照
して説明する。
"Embodiments" Hereinafter, embodiments of the apparatus of the present invention will be described with reference to the drawings.

図において1は上下方向に長く形成した処理槽
で、その下部には槽底2と所要の間隔を存して多
孔分散板3が設けられており、それらの間には原
水供給管4が接続されている。また、処理槽1の
中心部には、上下端が多光分散板3と天板5との
間にそれぞれ所要の間隔をおいて開口したエアリ
フト管6が立設されており、エアリフト管6の下
端部には送気管7が突入している。この送気管に
は天板5を通して処理槽の上端部内に連通した排
ガス管8がブロワー9を介して接続されている。
そして、処理槽1の上部にはエアリフト管6の上
部を囲んで分離筒10が設けられており、その外
側には、槽1外に設けた排水溜12に至る排水管
13を接続した排水越流室11が設けられてい
る。
In the figure, 1 is a treatment tank formed long in the vertical direction, and a porous distribution plate 3 is provided at the bottom of the tank at a required distance from the tank bottom 2, and a raw water supply pipe 4 is connected between them. has been done. Further, in the center of the processing tank 1, an air lift tube 6 is installed upright, and the upper and lower ends are opened between the multi-optical dispersion plate 3 and the top plate 5 with a required interval between them. An air pipe 7 protrudes into the lower end. An exhaust gas pipe 8 communicating with the upper end of the processing tank through the top plate 5 is connected to this air supply pipe via a blower 9.
A separation tube 10 is provided in the upper part of the treatment tank 1 to surround the upper part of the air lift pipe 6, and on the outside of the separation tube 10, a drainage pipe 13 leading to a drainage sump 12 provided outside the tank 1 is connected. A flow chamber 11 is provided.

処理槽1上部の槽壁と排水越流室11との間に
は槽1内に収容された担体粒子14の流動を規制
する抑え板15が設けられ、これには担体粒子1
4より小径とした多数の孔15a,15aが設け
られており、その上部には処理槽1の外側に設け
られた処理水溜16に至る処理水流出管17が接
続されている。
A restraining plate 15 is provided between the tank wall at the top of the treatment tank 1 and the wastewater overflow chamber 11 to regulate the flow of the carrier particles 14 housed in the tank 1.
A large number of holes 15a, 15a having a diameter smaller than 4 are provided, and a treated water outflow pipe 17 leading to a treated water reservoir 16 provided outside the treatment tank 1 is connected to the upper part of the holes 15a, 15a.

また、エアリフト管6の外側には、上端を抑え
板15の下方位置に開口18aさせるとともに、
下端がエアリフト管6の下端より下方に位置して
底板により閉じられた担体粒子導入管18が設け
られ、その下端はエアリフト管6の下端と連通さ
れている。そして、分離筒10の下端には、担体
粒子14の返送管19が導入管18の外側を囲ん
で下方に延び、下端を処理槽1の下部に開口して
設けられ、エアリフト管6より流出した担体粒子
14がこの返送管19内を流下して処理槽1の下
部へ返送されるようになつている。
Further, on the outside of the air lift pipe 6, an opening 18a is formed at the upper end at a position below the holding plate 15, and
A carrier particle introduction tube 18 whose lower end is located below the lower end of the air lift tube 6 and is closed by a bottom plate is provided, and its lower end is communicated with the lower end of the air lift tube 6. A return pipe 19 for the carrier particles 14 is provided at the lower end of the separation cylinder 10 so as to surround the outside of the introduction pipe 18 and extend downward, with its lower end opening at the bottom of the processing tank 1. The carrier particles 14 flow down within this return pipe 19 and are returned to the lower part of the processing tank 1.

なお、図中20は処理水の一部をポンプ21に
より処理槽底部に供給するために設けられた循環
管路である。
Note that 20 in the figure is a circulation pipe provided for supplying a portion of the treated water to the bottom of the treatment tank by a pump 21.

「作用」 前記構成の処理装置において、処理槽1内へは
担体粒子14が、従来の半流動処理槽におけると
同様に収容される。この場合、担体粒子は比重差
が若干ある2種類のものを使用するのがよい。原
水供給管4より流入した原水は、多孔分散板3よ
り槽の下部全域分散され、担体粒子間を上昇して
抑え板15の孔15aより流出される。その際、
原水の流れによつて担体粒子14は流動化し、担
体粒子14のうち軽いものは上昇して抑え板15
により流動化が抑制され、したがつて、抑え板1
5の下側には固定層部aが形成され、その固定層
部aの下側には多光分散板3までの間の流動層部
bが形成されることになり、原水はそれらの各層
部a,bを通る間に微生物による処理をうけ、そ
の処理水は抑え板15の孔15aを通つて上昇
し、処理水流出管17より処理水溜16を通つて
槽外に排出22されることになる。
"Operation" In the processing apparatus configured as described above, carrier particles 14 are accommodated in the processing tank 1 in the same manner as in a conventional semi-fluid processing tank. In this case, it is preferable to use two types of carrier particles with a slight difference in specific gravity. The raw water flowing in from the raw water supply pipe 4 is dispersed throughout the lower part of the tank by the porous dispersion plate 3, rises between the carrier particles, and flows out from the holes 15a of the restraining plate 15. that time,
The carrier particles 14 are fluidized by the flow of raw water, and lighter ones of the carrier particles 14 rise and reach the holding plate 15.
Fluidization is suppressed by the pressure plate 1.
A fixed layer part a is formed below the fixed layer part a, and a fluidized bed part b between the fixed layer part a and the polyoptic dispersion plate 3 is formed below the fixed layer part a, and the raw water flows through each layer. While passing through parts a and b, the treated water is treated by microorganisms, rises through the hole 15a of the holding plate 15, and is discharged 22 from the treated water outflow pipe 17 through the treated water reservoir 16 to the outside of the tank. become.

この原水処理により、原水中の汚濁物や生長し
た生物膜或は脱落した生物膜は、次第に固定層部
aに堆積して担体粒子14間に目詰りが生じてく
ることとなることは、従来処理槽におけると同様
であるが、この処理中において、送気管を介して
エアリフト管6に気体を注入する。実施例図のよ
うに、処理槽1を天板5で密閉した嫌気性処理を
行う方法のものにおいては、生物学的処理により
発生した消化ガス(メタン醗酵ガス)の一部をブ
ロワー9により還流してエアリフト管6へ注入す
るようにするが、好気性処理を行う場合は外気を
注入する。
Conventionally, it has been known that by this raw water treatment, pollutants in the raw water and biofilms that have grown or fallen off will gradually accumulate on the fixed layer part a, causing clogging between the carrier particles 14. As in the processing tank, during this processing, gas is injected into the air lift pipe 6 via the air supply pipe. As shown in the example diagram, in the method of performing anaerobic treatment in which the treatment tank 1 is sealed with a top plate 5, a part of the digestion gas (methane fermentation gas) generated by the biological treatment is refluxed by the blower 9. However, when performing aerobic treatment, outside air is injected into the air lift pipe 6.

エアリフト管6への気体の注入により、エアリ
フト作用が生じ、上端開口18aより入つた固定
層部aの担体粒子14と汚水等は、エアリフト管
6の下端に導入されて同管内を上昇し、担体粒子
14は洗浄作用を受けてそれに付着している汚濁
物や生物膜フロツク等は分離されてエアリフト管
6の上端より流出されることになる。ここで、比
重の重い担体粒子は沈降して行き、返送管18を
通つてその下端から槽下部の流動層部bに戻され
ることになる。また、汚水や汚濁物等は排水越流
室11よりオーバーフローして排水管15より排
水溜12を通つて排出23されることになる。
By injecting gas into the air lift tube 6, an air lift effect occurs, and the carrier particles 14 and sewage etc. in the fixed layer part a that entered from the upper end opening 18a are introduced into the lower end of the air lift tube 6 and rise inside the tube, and the carrier particles 14 and sewage etc. The particles 14 are subjected to a cleaning action, and the pollutants, biofilm flocs, etc. adhering to them are separated and flowed out from the upper end of the air lift tube 6. Here, the carrier particles having a heavy specific gravity settle and are returned to the fluidized bed part b at the bottom of the tank from the lower end of the return pipe 18. In addition, sewage, pollutants, etc. overflow from the drainage overflow chamber 11 and are discharged 23 through the drainage pipe 15 and the drainage sump 12.

このようにして、固定層部a及び流動層部bに
ある担体粒子や汚濁物等は、原水の処理中におい
て、エアリフト管6を上昇する際の洗浄作用で洗
浄、分離され、洗浄された担体粒子は再び槽の下
部に返却され、汚濁物等は槽外に排出除去される
ことになり、原廃水の生物学的処理と固定槽部
a、流動層部bの担体粒子の洗浄と汚濁物等の除
去とが同時に行われるのである。
In this way, carrier particles, pollutants, etc. in the fixed bed section a and the fluidized bed section b are washed and separated by the washing action when ascending through the air lift tube 6 during raw water treatment, and the washed carrier particles The particles are returned to the bottom of the tank, and the pollutants are removed from the tank by biological treatment of the raw wastewater, cleaning of carrier particles in the fixed tank section a and fluidized bed section b, and pollutants. etc. are removed at the same time.

「発明の効果」 以上説明したように、本発明の処理装置は、流
動層部とその上部に固定層部を形成してなる半流
動層式処理槽の中心部に、気体の送入されるエア
リフト管を立設し、該エアリフト管の下端開口
に、上端が固定層部内に開口した担体粒子導入管
を連通させるとともに、前記エアリフト管の上端
には、これより流出する担体を流動層部に返送す
るとともに、流出する洗浄汚水を槽外へ排出する
手段を設けたので、廃水の処理を行うと同時に、
特に目詰りを発生し易い固定層部の洗浄と汚濁物
等の分離、排出を行うことができ、常に目詰りの
生じないようにして連続した廃水処理が可能とな
り、廃水の微生物学的処理の能率を著しく向上さ
せることができる。
"Effects of the Invention" As explained above, in the processing apparatus of the present invention, gas is introduced into the center of the semi-fluidized bed processing tank, which has a fluidized bed section and a fixed bed section formed above the fluidized bed section. An air lift tube is installed upright, and a carrier particle introduction tube whose upper end opens into the fixed bed section is communicated with the lower end opening of the air lift tube, and at the same time, the carrier particles flowing out from the air lift tube are connected to the fluidized bed section at the upper end of the air lift tube. In addition to returning the washed wastewater, we also installed a means to discharge the washing wastewater out of the tank, so that the wastewater can be treated at the same time.
It is possible to wash the fixed bed part, which is particularly prone to clogging, and to separate and discharge pollutants, etc., making it possible to continuously treat wastewater without clogging, and to improve the microbiological treatment of wastewater. Efficiency can be significantly improved.

しかも、固定層部の洗浄はエアリフト管に気体
を注入するだけの手段で自動的に行われ、構造が
簡単で操作や保守も容易である等、優れた半流動
層式廃水処理装置を提供し得るものである。
In addition, the fixed bed section is automatically cleaned by simply injecting gas into the airlift pipe, and the structure is simple and easy to operate and maintain, providing an excellent semi-fluidized bed wastewater treatment system. It's something you get.

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

第1図は本発明装置の一実施例を示す側断面
図、第2図は第1図A−A部分の切断平面図であ
る。 1……処理槽、4……原水供給管、6……エア
リフト管、7……送気管、10……分離筒、11
……排水越流室、13……排水管、14……担体
粒子、15……抑え板、17……処理水流出管、
18……導入管、19……返送管。
FIG. 1 is a side sectional view showing an embodiment of the apparatus of the present invention, and FIG. 2 is a cutaway plan view taken along the line A--A in FIG. 1... Treatment tank, 4... Raw water supply pipe, 6... Air lift pipe, 7... Air supply pipe, 10... Separation tube, 11
...Drainage overflow chamber, 13...Drain pipe, 14...Carrier particles, 15...Suppressing plate, 17...Treatment water outflow pipe,
18...Introduction pipe, 19...Return pipe.

Claims (1)

【特許請求の範囲】[Claims] 1 流動層部とその上部に固定層部を形成してな
る半流動層式処理層の中心部に、気体の送入され
るエアリフト管を立設し、該エアリフト管の下端
開口に、上端が固定層部内に開口した担体粒子導
入管を連通させるとともに、前記エアリフト管の
上端には、これより流出する担体を流動層部に返
送するとともに、流出する洗浄汚水を槽外へ排出
する手段を設けたことを特徴とする、半流動層式
水処理装置。
1. An air lift pipe through which gas is introduced is installed upright in the center of a semi-fluidized bed processing bed consisting of a fluidized bed part and a fixed bed part formed above the fluidized bed part, and the upper end is connected to the lower end opening of the air lift pipe. A carrier particle introduction pipe opened into the fixed bed section is communicated with the air lift pipe, and a means is provided at the upper end of the air lift pipe to return the carrier flowing out from the pipe to the fluidized bed section, and to discharge washing wastewater flowing out to the outside of the tank. A semi-fluidized bed water treatment equipment.
JP60034146A 1985-02-22 1985-02-22 Semi-fluidized bed type water treatment apparatus Granted JPS61192390A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60034146A JPS61192390A (en) 1985-02-22 1985-02-22 Semi-fluidized bed type water treatment apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60034146A JPS61192390A (en) 1985-02-22 1985-02-22 Semi-fluidized bed type water treatment apparatus

Publications (2)

Publication Number Publication Date
JPS61192390A JPS61192390A (en) 1986-08-26
JPH0225675B2 true JPH0225675B2 (en) 1990-06-05

Family

ID=12406060

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60034146A Granted JPS61192390A (en) 1985-02-22 1985-02-22 Semi-fluidized bed type water treatment apparatus

Country Status (1)

Country Link
JP (1) JPS61192390A (en)

Also Published As

Publication number Publication date
JPS61192390A (en) 1986-08-26

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