JPS6323999Y2 - - Google Patents

Info

Publication number
JPS6323999Y2
JPS6323999Y2 JP1982174477U JP17447782U JPS6323999Y2 JP S6323999 Y2 JPS6323999 Y2 JP S6323999Y2 JP 1982174477 U JP1982174477 U JP 1982174477U JP 17447782 U JP17447782 U JP 17447782U JP S6323999 Y2 JPS6323999 Y2 JP S6323999Y2
Authority
JP
Japan
Prior art keywords
medium
layer
treatment
upper liquid
aeration
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
Application number
JP1982174477U
Other languages
Japanese (ja)
Other versions
JPS5979290U (en
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 filed Critical
Priority to JP1982174477U priority Critical patent/JPS5979290U/en
Publication of JPS5979290U publication Critical patent/JPS5979290U/en
Application granted granted Critical
Publication of JPS6323999Y2 publication Critical patent/JPS6323999Y2/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

  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Biological Treatment Of Waste Water (AREA)

Description

【考案の詳細な説明】 この考案は生物膜を付着した媒体を循環、洗浄
することによつてBOD負荷を増大でき、槽容積、
敷地面積の縮少を可能とし、しかも目詰り、逆洗
装置を不要とした維持管理の容易な汚水処理装置
に関する。
[Detailed description of the invention] This invention can increase the BOD load by circulating and cleaning the medium with biofilm attached, and the tank volume and
The present invention relates to a sewage treatment system that enables a reduction in site area and is easy to maintain and manage without clogging or backwashing equipment.

現在、最も普及している汚水処理装置として標
準活性汚泥法があるが、この処理法ではBOD容
積負荷が精々0.3〜0.8Kg/m3日にすぎず、効果的
な処理を行なうためには槽容積、敷地面積等が大
きくなるという欠点があつた。また浮遊法では固
液分離の点で解決困難な問題があり、さらには生
物膜法では媒体間の目詰りや特別の逆洗装置を必
要とするという欠点があつた。
Currently, the standard activated sludge method is the most popular sewage treatment equipment, but this treatment method has a BOD volumetric load of only 0.3 to 0.8 Kg/m for 3 days, and requires a tank for effective treatment. The disadvantage was that the volume and site area were larger. Furthermore, the floating method has problems that are difficult to solve in terms of solid-liquid separation, and the biofilm method has the drawbacks of clogging between media and the need for special backwashing equipment.

この考案は上記欠点を解決し、生物膜の付着し
た媒体を循環、洗浄することにより、BOD負荷
を飛躍的に増大し槽容積、敷地面積を縮少でき、
またバルキング等の心配がなく発生汚泥量も少な
く、さらには媒体間の目詰りを防止し、逆洗装置
も不要であつて、しかも維持管理が容易で対象汚
水の処理可能濃度範囲も著しく広い汚水処理装置
を提供することを目的とする。
This idea solves the above drawbacks, and by circulating and cleaning the medium with biofilm attached, it is possible to dramatically increase the BOD load and reduce the tank volume and site area.
In addition, there is no need to worry about bulking, the amount of sludge generated is small, and it also prevents clogging between media, does not require a backwashing device, is easy to maintain, and has an extremely wide range of sludge concentrations that can be treated. The purpose is to provide processing equipment.

以下、この考案の一実施例について図面を参照
して説明する。
An embodiment of this invention will be described below with reference to the drawings.

この考案の第1の実施例は第1図に示すように
ばつ気処理部1と、このばつ気処理部1で処理さ
れた処理液をさらに沈殿処理する沈殿処理部2と
を有する。
As shown in FIG. 1, the first embodiment of this invention has an aeration processing section 1 and a precipitation processing section 2 for further precipitating the processing liquid treated in the aeration processing section 1.

上記ばつ気処理部1は下部ホツパー状の処理槽
3と、この処理槽3内に充填され、後述する散気
装置5によるばつ気では流動しない砂、アンスラ
サイト、ガラス球等の好ましくはほぼ球状の媒体
4と、この媒体4層の中間部に配設された散気装
置5と、処理槽3底部から媒体4層上部まで伸び
駆動部6の作動により媒体4層底部近傍の媒体4
を引抜き、媒体4層上部の上液部8へ循環するス
クリユーコンベア(媒体循環装置)7とを有し、
このスクリユーコンベア7は微生物生物膜が付着
した媒体4を再生循環させる作用を成す。上液部
8は、媒体4層上方に形成され、媒体4から剥離
した生物膜と、処理すべき汚水aとを散気装置5
によりばつ気浮遊させる機能を果たす。
The aeration treatment section 1 includes a lower hopper-shaped treatment tank 3, and the treatment tank 3 is filled with sand, anthracite, glass spheres, etc., which are preferably approximately spherical and do not flow with aeration by an aeration device 5, which will be described later. The medium 4, the air diffuser 5 disposed in the middle of the four layers of the medium, and the medium 4 near the bottom of the fourth layer by the operation of the drive unit 6 extending from the bottom of the processing tank 3 to the top of the fourth layer of the medium.
It has a screw conveyor (medium circulation device) 7 that pulls out and circulates it to the upper liquid part 8 above the four layers of media,
This screw conveyor 7 functions to regenerate and circulate the medium 4 to which the microbial biofilm is attached. The upper liquid part 8 is formed above the four layers of the medium, and the biofilm peeled off from the medium 4 and the wastewater a to be treated are transferred to the aeration device 5.
It functions to make air float.

以上の構成によれば、処理すべき汚水aは処理
槽3下部より媒体4層に流入し、媒体4に付着し
た微生物によつてBODSS等が除去されながら矢
印イに示すように上昇し、その後、上液部8で媒
体4から剥離した微生物と一緒に滞留し、散気装
置5から供給される空気により活性汚泥処理を受
ける。そしてこの活性汚泥混合液は処理槽3上部
より流出し、沈殿処理部2の沈殿槽2aへ供給さ
れ、十分な固液分離後、上澄液は処理水として放
流され、他方沈殿汚泥は余剰汚泥として系外へ除
去される。
According to the above configuration, the wastewater a to be treated flows from the lower part of the treatment tank 3 into the medium 4 layer, and rises as shown by arrow A while BODSS etc. are removed by the microorganisms attached to the medium 4, and then The microorganisms separated from the medium 4 remain in the upper liquid section 8, and are subjected to activated sludge treatment by air supplied from the aeration device 5. This activated sludge mixture flows out from the upper part of the treatment tank 3 and is supplied to the settling tank 2a of the settling section 2. After sufficient solid-liquid separation, the supernatant liquid is discharged as treated water, while the settled sludge is treated as surplus sludge. removed from the system as

このようにこの考案では汚水処理を小さな球状
媒体に付着した微生物膜により行うために、その
比表面積は従来の固定床に比べ大幅に増加するの
で、容積当りの負荷を飛躍的に増大(BOD負荷
3〜10Kg/m3日)でき、それに伴い槽容積、敷地
面積も著しく縮少できる。しかも生物膜法である
のでバルキングの心配がなく、発生汚泥量も少な
く負荷変動に強い等の長所がある。さらに媒体4
は好ましくは球状のものを使用するために、媒体
4間の接触面積が最小でその表面に微生物が有効
に付着でき、しかも媒体4間の空隙は均等になる
ので、液体や気体の移動を均一に保持でき、特に
散気装置5からの空気は媒体4間を上昇し、媒体
4に付着した微生物に酸素を均一に供給すると同
時に肥大化した生物膜の剥離をも促す。特にこの
考案では、散気装置5によるばつ気では流動しな
い媒体4層中に散気装置5を配置したので、散気
装置5から供給された空気は、媒体4間の間隙を
ぬつて上昇する。このため、空気が細分化され、
上昇速度が遅くなり、さらに媒体4に付着した生
物膜に直接接触するので、酸素供給の効率が非常
に優れている。また散気装置5により、媒体4層
中に空気が供給されるので、媒体4に付着した生
物膜の肥大化による目詰りが防止できる。
In this way, in this design, sewage treatment is performed using a microbial membrane attached to a small spherical medium, and its specific surface area is greatly increased compared to conventional fixed beds, resulting in a dramatic increase in the load per volume (BOD load). 3 to 10Kg/m 3 days), and the tank volume and site area can be significantly reduced accordingly. In addition, since it is a biofilm method, there is no need to worry about bulking, and there are advantages such as the amount of sludge generated is small and it is resistant to load fluctuations. Further medium 4
It is preferable to use a spherical one, so that the contact area between the media 4 is minimal and microorganisms can effectively adhere to the surface, and the gaps between the media 4 are even, so the movement of liquid and gas is uniform. In particular, the air from the air diffuser 5 rises between the media 4, uniformly supplies oxygen to the microorganisms attached to the media 4, and at the same time promotes the exfoliation of enlarged biofilms. In particular, in this invention, the air diffuser 5 is placed in four layers of media that do not flow due to the air diffused by the air diffuser 5, so the air supplied from the air diffuser 5 rises through the gap between the media 4. . For this reason, the air is fragmented,
Since the rate of rise is slow and the biofilm attached to the medium 4 is directly contacted, the efficiency of oxygen supply is very high. Furthermore, since the air diffuser 5 supplies air into the four layers of the medium, clogging due to enlargement of the biofilm attached to the medium 4 can be prevented.

他方、処理槽3底部の媒体4は、中央に配置さ
れているスクリユーコンベア7によつて引抜かれ
媒体4層上部の上液部8に揚上移動され、この時
に媒体4表面に付着した生物膜が剥離除去され、
自重によつて循環される。従つて、この工程で媒
体4の洗浄、循環が行なわれるので、嫌気化や目
詰りを防止でき、しかも特別な逆洗設備が不要と
なり、高度な維持管理技術を全く必要としないば
かりでなく、装置のコンパクト化が図れる。さら
に処理槽3の上液部8では剥離微生物および散気
空気により効果的な活性汚泥処理が行なわれ、し
かも、これに伴つてその後段階処理である沈殿槽
2aで処理される汚泥は濃縮分離性が著しく良好
で、汚泥処理が極めて容易となる。
On the other hand, the medium 4 at the bottom of the treatment tank 3 is pulled out by the screw conveyor 7 located in the center and lifted to the upper liquid part 8 above the medium 4 layer, and at this time, the organisms attached to the surface of the medium 4 are removed. The film is peeled off and removed.
Circulated by its own weight. Therefore, since the medium 4 is cleaned and circulated in this process, anaerobic formation and clogging can be prevented, and special backwashing equipment is not required, and advanced maintenance technology is not required at all. The device can be made more compact. Furthermore, in the upper liquid part 8 of the treatment tank 3, effective activated sludge treatment is carried out by the detached microorganisms and diffused air. is extremely good, making sludge treatment extremely easy.

尚、この実施例の処理すべき汚水は下水2次処
理、3次処理、上水処理、産業癈水処理等極めて
広い汚水濃度範囲に於て適用できる。
The wastewater to be treated in this embodiment can be applied to a very wide range of wastewater concentration, such as secondary sewage treatment, tertiary treatment, clean water treatment, and industrial waste water treatment.

以上のようにこの考案によれば、BOD負荷を
飛躍的に増大でき敷地面積も著しく縮少可能とな
り、またバルキング等の心配がなく発生汚泥量も
少なく、さらには媒体の目詰りを防止し逆洗装置
も不要であり、維持管理が容易でかつ汚水の処理
範囲も著しく広い等の極めて優れた実用的効果が
ある。
As described above, according to this invention, the BOD load can be dramatically increased, the site area can be significantly reduced, there is no need to worry about bulking, the amount of sludge generated is small, and the clogging of the media can be prevented and reversed. It has excellent practical effects such as no washing equipment is required, easy maintenance and management, and an extremely wide range of wastewater treatment.

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

第1図はこの考案の一実施例の概略的構成図示
す。 3……処理槽、4……媒体、5……散気装置、
7……媒体循環装置。
FIG. 1 shows a schematic configuration diagram of an embodiment of this invention. 3... treatment tank, 4... medium, 5... aeration device,
7...Medium circulation device.

Claims (1)

【実用新案登録請求の範囲】[Scope of utility model registration request] 下部ホツパー状の処理層と、この処理層内に充
填され、後述する散気装置によるばつ気では流動
しない媒体と、この媒体層の中間部に配設された
散気装置と、上記媒体層底部近傍に位置する上記
媒体を後述する上液部へ揚上循環させるスクリユ
ーコンベアと、上記処理層内の上記媒体層上方に
形成され、該媒体から剥離した生物膜を上記散気
装置によりばつ気させると共に浮遊させる上液部
と、上記媒体層の下部に導入され、該媒体層を上
向流で流通し、上記上液部に滞留する汚水と、上
記上液部の液の一部を沈殿処理した後、処理水と
して放流する沈殿処理部とを備えた汚水処理装
置。
A lower hopper-shaped treatment layer, a medium filled in this treatment layer that does not flow due to aeration by an aeration device described below, an aeration device disposed in the middle of this media layer, and a bottom portion of the media layer. A screw conveyor that lifts and circulates the medium located nearby to an upper liquid section, which will be described later, and a biological film formed above the medium layer in the treatment layer and separated from the medium are aerated by the aeration device. The upper liquid part is introduced into the lower part of the medium layer and flows upward through the medium layer, and the sewage that stays in the upper liquid part and a part of the liquid in the upper liquid part are precipitated. A sewage treatment device comprising a sedimentation treatment section that discharges treated water as treated water.
JP1982174477U 1982-11-17 1982-11-17 Sewage treatment equipment Granted JPS5979290U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1982174477U JPS5979290U (en) 1982-11-17 1982-11-17 Sewage treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1982174477U JPS5979290U (en) 1982-11-17 1982-11-17 Sewage treatment equipment

Publications (2)

Publication Number Publication Date
JPS5979290U JPS5979290U (en) 1984-05-29
JPS6323999Y2 true JPS6323999Y2 (en) 1988-07-01

Family

ID=30379832

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1982174477U Granted JPS5979290U (en) 1982-11-17 1982-11-17 Sewage treatment equipment

Country Status (1)

Country Link
JP (1) JPS5979290U (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2019078003A1 (en) * 2017-10-19 2019-04-25 パナソニックIpマネジメント株式会社 Microbial fuel cell, liquid processing system, and liquid processing structure

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4573991B2 (en) * 2000-11-06 2010-11-04 フジクリーン工業株式会社 Sewage treatment apparatus and treatment method
JP4573997B2 (en) * 2000-11-14 2010-11-04 フジクリーン工業株式会社 Sewage treatment apparatus and treatment method

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5310393A (en) * 1976-07-16 1978-01-30 Otoji Ishizaka Hydrogen generating method by water decomposition
JPS54112559A (en) * 1978-02-21 1979-09-03 Hitachi Chem Co Ltd Apparatus for clarifying filthy water
JPS56100690A (en) * 1980-01-11 1981-08-12 Ebara Infilco Co Ltd Treatment of waste water
JPS57130590A (en) * 1981-02-04 1982-08-13 Ebara Infilco Co Ltd Biological treatment of org. waste water

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5310393A (en) * 1976-07-16 1978-01-30 Otoji Ishizaka Hydrogen generating method by water decomposition
JPS54112559A (en) * 1978-02-21 1979-09-03 Hitachi Chem Co Ltd Apparatus for clarifying filthy water
JPS56100690A (en) * 1980-01-11 1981-08-12 Ebara Infilco Co Ltd Treatment of waste water
JPS57130590A (en) * 1981-02-04 1982-08-13 Ebara Infilco Co Ltd Biological treatment of org. waste water

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2019078003A1 (en) * 2017-10-19 2019-04-25 パナソニックIpマネジメント株式会社 Microbial fuel cell, liquid processing system, and liquid processing structure

Also Published As

Publication number Publication date
JPS5979290U (en) 1984-05-29

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