JPS59230694A - Fluidized aeration tank using particulate medium - Google Patents
Fluidized aeration tank using particulate mediumInfo
- Publication number
- JPS59230694A JPS59230694A JP58105002A JP10500283A JPS59230694A JP S59230694 A JPS59230694 A JP S59230694A JP 58105002 A JP58105002 A JP 58105002A JP 10500283 A JP10500283 A JP 10500283A JP S59230694 A JPS59230694 A JP S59230694A
- Authority
- JP
- Japan
- Prior art keywords
- aeration tank
- medium
- air
- fluidized
- air lift
- 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
Links
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
- Biological Treatment Of Waste Water (AREA)
Abstract
Description
【発明の詳細な説明】
本発明は粒状媒体を使用した流動曝気槽に関するもので
ある。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a fluidized aeration tank using granular media.
有機性廃水の生物処理法として高BOD負荷、汚泥の生
成量が少ないなどの利点を有する生物膜処理法が見直さ
れ、各種の装置が即発されている。As a biological treatment method for organic wastewater, the biofilm treatment method, which has advantages such as a high BOD load and a small amount of sludge produced, is being reconsidered, and various devices are being put into production.
生物膜処理法には、従来より流動床媒体法と固定床媒体
法とがある。Conventional biofilm treatment methods include fluidized bed media methods and fixed bed media methods.
流動床媒体法は曝気槽中に媒体を投入し、曝気によって
流動循環させ、媒体に生物膜を形成させ、この微生物に
よって廃水中の有機成分を除去する方法である。The fluidized bed media method is a method in which a medium is placed in an aeration tank and circulated in a fluidized manner by aeration to form a biofilm on the medium, and the organic components in the wastewater are removed by this microorganism.
また、固定床媒体法は、媒体を曝気槽内に固定充填して
生物膜を形成させ、微生物によって廃水を処理する方法
である。Furthermore, the fixed bed media method is a method in which a medium is fixedly packed into an aeration tank to form a biofilm, and wastewater is treated with microorganisms.
本発明は前者である流動床媒体法に適用される流動曝気
槽に関するもので、流動媒体として砂などのような粒状
物を利用し、槽内にできるだ番ノ多くの微生物を保持し
た媒体が円滑に旋回・流動できるように構成した粒状媒
体を使用した流動曝気槽を提供することを目的としてい
る。The present invention relates to a fluidized aeration tank applied to the former fluidized bed media method, in which a granular material such as sand is used as the fluidized medium, and a medium holding as many microorganisms as possible is produced in the tank. The object of the present invention is to provide a fluidized aeration tank using a granular medium configured to smoothly swirl and flow.
以下、図面に示す実施例に暴いて本発明の詳細な説明す
る。Hereinafter, the present invention will be explained in detail with reference to embodiments shown in the drawings.
図は本発明の一実施例を説明するもので、本発明の流動
曝気槽は円筒部1の下端部に絞られたコてン部2と、上
端に上に向って断面積を拡大した固液分離部3を有し、
コーン部2の下端は閉塞されており、このコーン部2の
底面から配管4を介して原水が槽内に供給される。The figure explains one embodiment of the present invention, and the fluidized aeration tank of the present invention has a coin part 2 constricted at the lower end of a cylindrical part 1, and a solid part 2 whose cross-sectional area is enlarged upwards at the upper end. It has a liquid separation part 3,
The lower end of the cone portion 2 is closed, and raw water is supplied into the tank from the bottom surface of the cone portion 2 via a pipe 4.
コーン部2の内周面のほぼ中央部から底部に向かってコ
ーン部2よりもさらに絞られた形状の仕切板5が設けら
れており、コーン部2の底面と仕切板5の下端との間に
は、わずかな隙間としてのスリット6が形成されている
。A partition plate 5 is provided which is narrower in shape than the cone part 2 from approximately the center of the inner circumferential surface of the cone part 2 toward the bottom thereof, and is provided between the bottom of the cone part 2 and the lower end of the partition plate 5. A slit 6 is formed as a slight gap.
また、固液分離部3の内部には曝気槽円筒部1と同等の
径を有する仕切円筒8を設け、その下縁と固液分離部3
の内周面との間は廃水が自由に流通ずるような間隔が設
(プられている。Further, inside the solid-liquid separation section 3, a partition cylinder 8 having the same diameter as the aeration tank cylinder section 1 is provided, and its lower edge and the solid-liquid separation section 3
A gap is provided between the inner peripheral surface of the pipe and the inner circumferential surface of the pipe to allow waste water to flow freely.
一方、曝気槽円筒部1の軸線上にはエアリフト管9が配
置されている。エアリフト管9は、その下端が前記仕切
板5の下縁より上方へ最適な間隔になる如く配置され、
かつ、エアリフト管9の下方部の外周面には下方に向か
って開いた仕切板10が設けられている。この場合、仕
切板10の下縁は相対する仕切板5の内周面に接するこ
となく、媒体が自由に通過できる間隔7が設けられてい
る。 ニアリフ1〜管9の軸線上にはエア供給管11が
挿入されており、その下端は多孔により開口されており
、エアリフト管9の下端部より若干 ゛上方に位置
している。On the other hand, an air lift pipe 9 is arranged on the axis of the cylindrical part 1 of the aeration tank. The air lift pipe 9 is arranged such that its lower end is at an optimal distance above the lower edge of the partition plate 5,
Further, a partition plate 10 that opens downward is provided on the outer peripheral surface of the lower part of the air lift pipe 9. In this case, the lower edge of the partition plate 10 does not come into contact with the inner peripheral surface of the opposing partition plate 5, and a gap 7 is provided through which the medium can freely pass. An air supply pipe 11 is inserted on the axis of the near lift pipe 1 to the pipe 9, the lower end of which is opened with a porous hole, and is located slightly above the lower end of the air lift pipe 9.
図中に、破線12で示すものは循環水用配管で、その一
端吸込側は前記固液分離部3の水面に浅(複数箇所に挿
入され、また、下端吐出側はコーン部2の底面近傍の複
数個所において、コーン部2に対して接線方向となるよ
うに開口している。In the figure, what is indicated by a broken line 12 is a pipe for circulating water, one end of which is inserted into the water surface of the solid-liquid separator 3 shallowly (inserted in multiple locations), and its lower end discharge side is near the bottom surface of the cone part 2. The openings are tangential to the cone portion 2 at a plurality of locations.
13は処理水を循環させるだめのポンプである。13 is a pump for circulating treated water.
ところで、曝気山内には所定量の砂などの粒状物が流動
媒体として投入されている。By the way, a predetermined amount of granular material such as sand is put into the aeration pile as a fluidizing medium.
次に、以上のように構成された本実施例の動作について
説明する。Next, the operation of this embodiment configured as above will be explained.
まづ、固液分離部3の上縁まで水を満たし、つぎに、エ
ア供給管11の下端からは常時所定量の空気が供給され
、その気泡はエアリフト管9内を上昇して排出され、曝
気槽内に旋回流を起させる。First, the solid-liquid separation section 3 is filled with water up to the upper edge, and then a predetermined amount of air is constantly supplied from the lower end of the air supply pipe 11, and the air bubbles rise inside the air lift pipe 9 and are discharged. Create a swirling flow in the aeration tank.
一方、配管12を介して固液分離部3の水面からコーン
部2の底面の接線方向に向かって、ポンプ13の作動に
より処理水を循環させる。この循環水によってコーン部
2に沈澱した砂などの粒状物はゆっくりと槽の中心部へ
回転移動されるとともに、スリット6を通って上昇する
循環水とともにエアリフト管9内に導かれる。On the other hand, the pump 13 is operated to circulate the treated water from the water surface of the solid-liquid separation section 3 to the tangential direction of the bottom surface of the cone section 2 via the pipe 12. Particulate matter such as sand deposited in the cone portion 2 is slowly rotated and moved to the center of the tank by this circulating water, and is guided into the air lift pipe 9 together with the circulating water rising through the slit 6.
そして、エアリフト管9内を上昇する気泡によって生じ
る上昇流に乗ってエアリフト管9の上端部から、仕切内
WJ8の内部へ排出され、やがて重力により沈降しはじ
め、仕切板10と仕切板5との間の隙間を通ってコーン
部2の底部に達し、前述した回転移動と上昇運動を(り
返す。The air bubbles are then discharged from the upper end of the air lift pipe 9 into the partition WJ 8 on the upward flow generated by the bubbles rising inside the air lift pipe 9, and eventually begin to settle due to gravity, causing the separation between the partition plate 10 and the partition plate 5. It reaches the bottom of the cone part 2 through the gap between them, and repeats the rotational movement and upward movement described above.
このように所定時間循環、n留が行なわれている間に媒
体である砂などの粒状物の表面に生物膜が形成され、こ
の微生物によって原水中の有機成分が除去される。During this circulation and distillation for a predetermined period of time, a biofilm is formed on the surface of the granular medium such as sand, and the organic components in the raw water are removed by the microorganisms.
原水送入管4から曝気槽へ送入され所定時間滞留した原
水は、やがて固液分離部3の上端からオーバーフローし
、処理水配管13によって図示していない沈殿槽側へと
導かれ、汚泥を分離して処理水となる。The raw water that is sent from the raw water feed pipe 4 to the aeration tank and stagnated for a predetermined time eventually overflows from the upper end of the solid-liquid separation section 3 and is led to the settling tank (not shown) by the treated water pipe 13, where the sludge is removed. It is separated and becomes treated water.
以上の説明から明らかなように本発明によれば、処理水
を槽の底部に接線状に循環させ、媒体をゆっくり槽底の
中心部へ回転移動させつつ、エアリフトされ易い状態に
することができる。その場合、仕切板10および5の設
置によって沈積した媒体は、間隙7を通って徐々に下方
へ移動するので、前記循環水の作用を効果的にすること
ができる。As is clear from the above description, according to the present invention, the treated water can be circulated tangentially to the bottom of the tank, and the medium can be slowly rotated to the center of the tank bottom, making it easy to air lift. . In that case, the medium deposited by the installation of the partition plates 10 and 5 gradually moves downward through the gap 7, so that the effect of the circulating water can be made effective.
すなわち、仕切板10および5の設置、ならびに循4環
水の送入がない場合は、媒体投入量が増加するとコーン
部2に沈積したままの状態となり、空気mを増加させて
もニアリフ1−されなくなる。しかし、本実施例によれ
ば、コーン部2に沈積した媒体は円滑に移動して順調に
エアリフトされるため、媒体投入量を増加することがで
きる。In other words, if the partition plates 10 and 5 are not installed and the circulating water is not supplied, if the amount of medium input increases, it will remain deposited in the cone part 2, and even if the air m is increased, the near rift 1- It will no longer be done. However, according to this embodiment, the medium deposited in the cone portion 2 moves smoothly and is smoothly airlifted, so that the amount of medium input can be increased.
、 本実施例は以上のように構成されているので、槽
内に多くの微生物を保持することでき、かつ微生物に効
率よく酸素を供給することもでき、微生物による有機物
の生物酸化を効率よく行ない、良好な処理水を得ること
ができる。Since this embodiment is configured as described above, it is possible to hold many microorganisms in the tank, and also to efficiently supply oxygen to the microorganisms, so that the microorganisms can efficiently perform biological oxidation of organic matter. , good quality treated water can be obtained.
図は本発明の一実施例を説明する概略椛成図である。
第1図は全体構造の縦断面図、第2図は第1図をA−A
方向よりみた図である。
1は曝気槽円筒部、2はコーン部、3は固液分離部、4
は原水送入管、5,10は仕切板、6はスリット、7は
間隙、8は仕切円筒、9はエアリフト管、11はエア供
給管、12は循環水配管、13は処理水配管である。
特許出願人 宇部興産株式会社The figure is a schematic diagram illustrating an embodiment of the present invention. Figure 1 is a vertical cross-sectional view of the overall structure, Figure 2 is a cross-sectional view of Figure 1.
It is a diagram seen from the direction. 1 is the aeration tank cylindrical part, 2 is the cone part, 3 is the solid-liquid separation part, 4
is a raw water supply pipe, 5 and 10 are partition plates, 6 is a slit, 7 is a gap, 8 is a partition cylinder, 9 is an air lift pipe, 11 is an air supply pipe, 12 is a circulating water pipe, and 13 is a treated water pipe. . Patent applicant: Ube Industries, Ltd.
Claims (1)
ン部を有し、上端部に上方へ向かって開いた固液分離部
を有する曝気槽ど、その曝気槽の中央部に同心円状に配
置されたエアリフト管と、このエアリフト管内に同心円
状に配置されたエア供給管と、前記コーン部の内側に配
置され、その下縁部をコーン部の底面の近傍にまで臨ま
せた漏斗状の仕切板と、前記ニアリフ1〜管の下方部に
設けられ、その下端を前記仕切板の近傍に臨ませた末広
がりの仕切板とを設け、原水はコーン部の底面から供給
するとともに上記固液分離部の水面から配管を介して処
理水をコーン部の下部の周囲の複数箇所から接線状に供
給して循環させるようにしたことを特徴とする粒状媒体
を使用した流動曝気槽。An aeration tank that is formed in a cylindrical shape, has a cone portion constricted downward at the lower end, and a solid-liquid separation section that opens upward at the upper end, has a concentric shape in the center of the aeration tank. an air lift pipe arranged in the air lift pipe, an air supply pipe arranged concentrically within the air lift pipe, and a funnel-shaped air supply pipe arranged inside the cone part with its lower edge facing close to the bottom surface of the cone part. A partition plate is provided at the lower part of the near rift 1 to the pipe, and a partition plate that widens toward the end with its lower end facing the vicinity of the partition plate is provided, raw water is supplied from the bottom of the cone part, and the solid-liquid A fluidized aeration tank using a granular medium, characterized in that treated water is supplied from the water surface of the separation section via piping tangentially from multiple locations around the lower part of the cone section and circulated.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP58105002A JPS59230694A (en) | 1983-06-14 | 1983-06-14 | Fluidized aeration tank using particulate medium |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP58105002A JPS59230694A (en) | 1983-06-14 | 1983-06-14 | Fluidized aeration tank using particulate medium |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS59230694A true JPS59230694A (en) | 1984-12-25 |
Family
ID=14395872
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP58105002A Pending JPS59230694A (en) | 1983-06-14 | 1983-06-14 | Fluidized aeration tank using particulate medium |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS59230694A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0728122A4 (en) * | 1993-11-10 | 1998-07-29 | Ocean Arks Int Inc | System and method for treatment of polluted water |
JP2008259966A (en) * | 2007-04-12 | 2008-10-30 | Ihi Corp | High pressure fluidized bed type aerobic waste water treatment equipment |
JP2008264710A (en) * | 2007-04-23 | 2008-11-06 | Ihi Corp | High-pressure fluidized bed aerobic wastewater treatment equipment |
CN110255732A (en) * | 2019-06-17 | 2019-09-20 | 南京理工大学 | A kind of energy-efficient separation of solid and liquid purification device |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS53140457U (en) * | 1977-04-13 | 1978-11-07 | ||
JPS56137074U (en) * | 1980-03-17 | 1981-10-17 |
-
1983
- 1983-06-14 JP JP58105002A patent/JPS59230694A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS53140457U (en) * | 1977-04-13 | 1978-11-07 | ||
JPS56137074U (en) * | 1980-03-17 | 1981-10-17 |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0728122A4 (en) * | 1993-11-10 | 1998-07-29 | Ocean Arks Int Inc | System and method for treatment of polluted water |
JP2008259966A (en) * | 2007-04-12 | 2008-10-30 | Ihi Corp | High pressure fluidized bed type aerobic waste water treatment equipment |
JP2008264710A (en) * | 2007-04-23 | 2008-11-06 | Ihi Corp | High-pressure fluidized bed aerobic wastewater treatment equipment |
CN110255732A (en) * | 2019-06-17 | 2019-09-20 | 南京理工大学 | A kind of energy-efficient separation of solid and liquid purification device |
CN110255732B (en) * | 2019-06-17 | 2021-09-17 | 南京理工大学 | Energy-saving solid-liquid separation and purification device |
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