JPS61111200A - Methane fermentation tank - Google Patents
Methane fermentation tankInfo
- Publication number
- JPS61111200A JPS61111200A JP59233659A JP23365984A JPS61111200A JP S61111200 A JPS61111200 A JP S61111200A JP 59233659 A JP59233659 A JP 59233659A JP 23365984 A JP23365984 A JP 23365984A JP S61111200 A JPS61111200 A JP S61111200A
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- liquid
- treated
- tank
- tank body
- 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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Landscapes
- Treatment Of Sludge (AREA)
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は高ＢＯＤ値の排水や二次処理施設からの汚泥等
を処理するために用いられるメタン発酵槽に関するもの
である。DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a methane fermentation tank used for treating wastewater with a high BOD value, sludge from secondary treatment facilities, and the like.
従来例を第４図に示す。図において（１）は槽体であり
、底部には注入口（２）が連絡し上部には排出口（３）
が連絡する。そして該槽体（１）の内部において上部に
は集ガス器（４）が設置される。 ・上記構成におい
て、被処理液（５）は注入口（２）を介して槽体（１）
底部から供給され、スラッジ（５）Ａを沈降分離し上澄
液（５）Ｂは排出口（３）から溢出する。この間主とし
てスラッジ層（５）Ａ内でメタンガスが発生し、該メタ
ンガスは上行して集ガス器（４）で採集せられ外へ取出
される。A conventional example is shown in FIG. In the figure, (1) is the tank body, with an inlet (2) connected to the bottom and an outlet (3) connected to the top.
will contact you. A gas collector (4) is installed in the upper part of the tank body (1). - In the above configuration, the liquid to be treated (5) is supplied to the tank body (1) through the inlet (2).
It is supplied from the bottom, the sludge (5)A is sedimented and separated, and the supernatant (5)B overflows from the outlet (3). During this time, methane gas is mainly generated within the sludge layer (5) A, and the methane gas ascends and is collected by the gas collector (4) and taken out.
上記従来技術においては主としてスラッジ（５）Ａ層か
ら発生するメタンガスは上行する時に被処理液（５）を
騒乱することになるから、被処理液（５）のスラッジ（
５）Ａの分離に支障をきたし、スラッジ（５）Ａが上澄
液（５１Ｂ Ｋ同伴されて排出口（３）から溢出するお
それがありた。In the above conventional technology, the methane gas mainly generated from layer A of the sludge (5) disturbs the liquid to be treated (5) when it ascends, so the sludge (
5) There was a risk that the separation of A would be hindered, and the sludge (5) A would be accompanied by the supernatant liquid (51BK) and overflow from the discharge port (3).
本発明は上記従来の問題点を解決するための手段として
、槽体（１）と、槽体（１）下部に連絡する注入口（２
）と、槽体（１）上部に連絡する排出口（３）と、槽内
（１）に設置される傾斜板（７ＪＡ、（７）Ｂとからな
るメタン発酵槽を提供するものである。The present invention provides a tank body (1) and an inlet (2
), a discharge port (3) communicating with the upper part of the tank body (1), and an inclined plate (7JA, (7)B) installed in the tank (1).
上記構成にもとづく本発明の作用は下記の通シである。 The operation of the present invention based on the above configuration is as follows.
注入口から被処理液を槽体下部に注入する。該被処理液
は槽内において上行しつ＼含有するスラッジを沈降し、
上澄液は排出口から槽外に排出される。この際被処理液
中に含ま糺るＢＯＤ成分は嫌気性生物学的分解によって
メタンガスにまで分解され、かくして発生したメタンガ
スは被処理液内を上行して外出する。該メタンガスは主
として高ＢＯＤ値のスラッジ層から発生し被処理液内を
上行する際に被処理液を騒乱する。該被処理液はこのよ
うにメタンガスによって騒乱されるが傾斜板の間を通シ
抜ける時に整流される。更に傾斜板に微生物膜が形成さ
れてこの個所でも被処理物にｔ 含まれ
るＢＯＤ成分の嫌気性生物学的分解が起る。Inject the liquid to be treated into the lower part of the tank body from the injection port. The liquid to be treated ascends in the tank, and the sludge it contains settles out.
The supernatant liquid is discharged to the outside of the tank from the discharge port. At this time, the BOD component contained in the liquid to be treated is decomposed into methane gas by anaerobic biological decomposition, and the methane gas thus generated travels up the liquid to be treated and exits. The methane gas is mainly generated from the sludge layer with a high BOD value and disturbs the liquid to be treated as it moves upward within the liquid to be treated. The liquid to be treated is thus disturbed by the methane gas, but is rectified when passing between the inclined plates. Furthermore, a microbial film is formed on the inclined plate, and anaerobic biological decomposition of the BOD component contained in the material to be treated occurs at this location as well.
しだがって本発明においては発生するメタンガスによっ
て騒乱された被処理液が傾斜板によって整流されるから
、スラッジの分離効率が大きくな〕上澄液へのスラッジ
の同伴が防止されるし、傾斜板に微生物膜が形成される
から、これが固定相となって被処理物に含まれるＢＯＤ
成分が更に分解され、ＢＯＤ成分の除去率も向上する。Therefore, in the present invention, since the liquid to be treated that is disturbed by the generated methane gas is rectified by the inclined plate, the sludge separation efficiency is increased, the entrainment of sludge into the supernatant liquid is prevented, and the inclined plate Since a microbial film is formed on the plate, this becomes a stationary phase and absorbs BOD contained in the processed material.
The components are further decomposed and the removal rate of BOD components is also improved.
第１図には本発明の第１実施例が示される。 FIG. 1 shows a first embodiment of the invention.
図において、（１）は槽体であシ底部には注入口（２）
が連絡し上部には排出口（３）が連絡し上端には排ガス
ｏ（６）が連絡する。槽体（１）の内部においては被処
理液（５）のスラッジ層（５）Ａ域の上部に上澄液層（
５）Ｂ域にまたがって傾斜板（７）Ａが設置され、更に
該傾斜板（７）Ａの横から上方にガス分離板（４）が差
出され、また排出口（３）付近（被処理液（５）の水面
付近）には傾斜板（７）Ｂが設置される。更に排出口（
３）から注入口（２）に還流径路（８）が連絡する。In the figure, (1) is the tank body, and there is an inlet (2) at the bottom.
The upper end is connected to the exhaust port (3), and the upper end is connected to the exhaust gas o (6). Inside the tank body (1), a supernatant liquid layer (
5) An inclined plate (7)A is installed across area B, and a gas separation plate (4) is extended upward from the side of the inclined plate (7)A. An inclined plate (7)B is installed near the water surface of the liquid (5). Furthermore, the outlet (
A reflux path (8) communicates from 3) to the inlet (2).
上記構成において、被処理液（５）は注入口（２）から
槽体（１）底部に供給され、槽体（１）内を上行して排
出口（３）から溢出する。この間被処理液（５）に含ま
れるＢＯＤ成分は嫌気性生物学的分解され発生するメタ
ンガスはガス分離板（４）にガイドされて矢印イ方向に
被処理液（５）内を上行して排ガス口（６）から排出さ
れる。また被処理液（５）はメタンガスの上行の際に騒
乱されるが傾斜板（力Ａによって整流されてスラッジを
効率よく分離し、更に傾斜板（７）Ｂによっても整流さ
れて同伴するスラッジがあればこれを効率よく分離する
。傾斜板（７）Ｂによる被処理液の整流はメタンガスの
影響からガス分離板（４）によって殆んど遮断されてい
るから略完全に行われる。In the above configuration, the liquid to be treated (5) is supplied to the bottom of the tank body (1) from the inlet (2), moves up inside the tank body (1), and overflows from the discharge port (3). During this time, the BOD component contained in the liquid to be treated (5) is decomposed anaerobically and the generated methane gas is guided by the gas separation plate (4) and ascends in the liquid to be treated (5) in the direction of arrow A, and is discharged as exhaust gas. It is discharged from the mouth (6). In addition, the liquid to be treated (5) is disturbed when the methane gas ascends, but it is rectified by the inclined plate (force A) to efficiently separate the sludge, and further rectified by the inclined plate (7) B to remove the accompanying sludge. If any, the liquid to be treated is efficiently separated.The rectification of the liquid to be treated by the inclined plate (7)B is almost completely effected because it is almost completely blocked by the gas separation plate (4) due to the influence of methane gas.
更に傾斜板（力Ａ、（７１Ｂに微生物膜が形成されるか
らこの個所でも被処理液（５）に含まれるＢＯＤ成分の
嫌気性生物学的分解が行われる。かくして被処理液（５
）はＢＯＤ成分およびスラッジを効率よく除去された後
排出口（３）から溢出するがその一部は還流径路（８）
から注入口（２）側に還流される。Furthermore, since a microbial film is formed on the inclined plate (force A, (71B), anaerobic biological decomposition of the BOD component contained in the liquid to be treated (5) is also performed at this point.In this way, the liquid to be treated (5)
) overflows from the discharge port (3) after the BOD components and sludge are efficiently removed, but some of it flows through the reflux path (8).
The water is then refluxed to the injection port (2).
第２図には本発明の第２実施例が示される０本実施例に
おいては傾斜板（ハ）Ａの上方にガス分離板■Ｃが被着
され、該ガス分離板（ロ）Ｃの上方両側にガス分離板ｆ
４１）Ａ、（６）Ｂが配置されており、メタンガスは矢
印口方向にガイドされて傾斜板（ハ）Ｂへの影響を遮断
されている。FIG. 2 shows a second embodiment of the present invention. In this embodiment, a gas separation plate (C) is attached above the inclined plate (C) A, and above the gas separation plate (B) C. Gas separation plate f on both sides
41)A and (6)B are arranged, and methane gas is guided in the direction of the arrow and its influence on the inclined plate (c)B is blocked.
第３図には本発明の第、３実施例が示される。FIG. 3 shows a third embodiment of the present invention.
本実施例においては槽体（１）Ａと槽体（１）Ｂと２５
（結合されてお択槽体（１）Ａには傾斜板（２）ＡＪｉ
内設され槽体（１） Ｂ Ｋは傾斜板（２）Ｂが内設さ
れている。そして槽体（１）人の底部には注入口（２）
Ａが連絡し、上部には浴出口（３）Ａが設けられ、槽体
（１）Ｂの下部には槽体（１）Ａの浴出口（３１Ａに連
絡する注入口（２） Ｂ ＡＥ設けられ上部には排出０
（３）Ｂが連絡する。更に槽体（１）Ａと槽体（１）Ｂ
の上端には夫々排ガス口（６）Ａ。In this example, tank body (1) A, tank body (1) B and 25
(The selected tank body (1) A has a slanted plate (2) AJi.
An inclined plate (2) B is installed inside the tank body (1) BK. And the tank body (1) and the injection port (2) at the bottom of the body.
The bath outlet (3) A is connected to the upper part, and the bath outlet (3) A is installed in the lower part of the tank body (1) B. There is no discharge at the top.
(3) B contacts. Furthermore, tank body (1) A and tank body (1) B
There is an exhaust gas port (6) A at the upper end of each.
（６）Ｂが連絡し槽体（１）Ｂの底部には汚泥返送径路
（９）が連絡し該汚泥返送径路（９）にはポンプ（９）
Ａ −Ａ（介在する。(6) B is connected to the tank body (1). A sludge return path (9) is connected to the bottom of B, and a pump (9) is connected to the sludge return path (9).
A-A (intervening)
上記構成においては被処理液（５）はまず槽体（１）Ａ
内で粗大スラッジＨＡを沈降分離し、浴出口（３１Ａ。In the above configuration, the liquid to be treated (5) is first transferred to the tank body (1)A.
The coarse sludge HA is sedimented and separated in the bath outlet (31A).
注入口（２）Ｂを介して槽体（１）Ｂ内へ流入し槽体（
１）Ｂ内で微小スラッジＧＤＢを沈降分離する。そして
槽体（１） Ａ 、 （１） Ｂで包有するＢＯＤ成分
を嫌気性生物学的分解され、発生するメタンガスは夫々
排ガス口（６） Ａ 、 （６） Ｂから排出される。It flows into the tank body (1) B through the injection port (2) B, and the tank body (
1) Sedimentation and separation of minute sludge GDB in B. The BOD components contained in the tank bodies (1) A and (1) B are then anaerobically and biologically decomposed, and the generated methane gas is discharged from the exhaust gas ports (6) A and (6) B, respectively.
第」図は本発明の第ユ実施例にか＼る模式図、第２図は
第２実施例にか＼る模式図、第３図は第３実施例にか＼
る模式図、第４図は従来例の模式図である。Figure 2 is a schematic diagram of the second embodiment of the present invention, Figure 2 is a schematic diagram of the second embodiment, and Figure 3 is a schematic diagram of the third embodiment.
FIG. 4 is a schematic diagram of a conventional example.
Claims (2)
に連絡する排出口と、槽内に設置される傾斜板とからな
るメタン発酵槽(1) A methane fermentation tank consisting of a tank body, an inlet communicating with the lower part of the tank body, an outlet communicating with the upper part of the tank body, and an inclined plate installed in the tank
に連絡する排出口と、槽内に設置される傾斜板と、槽内
において傾斜板の上部に設置されるガス分離板とからな
るメタン発酵槽(2) A tank body, an inlet connected to the bottom of the tank, an outlet connected to the top of the tank, an inclined plate installed in the tank, and a gas separation installed above the inclined plate in the tank. Methane fermentation tank consisting of a plate
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP59233659A JPS61111200A (en) | 1984-11-06 | 1984-11-06 | Methane fermentation tank |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP59233659A JPS61111200A (en) | 1984-11-06 | 1984-11-06 | Methane fermentation tank |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPS61111200A true JPS61111200A (en) | 1986-05-29 |
Family
ID=16958511
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP59233659A Pending JPS61111200A (en) | 1984-11-06 | 1984-11-06 | Methane fermentation tank |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS61111200A (en) |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2006051490A (en) * | 2004-01-15 | 2006-02-23 | Sumitomo Heavy Ind Ltd | Anaerobic treatment apparatus and method |
| JP2009522096A (en) * | 2006-01-05 | 2009-06-11 | バイオタン システムズ インターナショナル ビー．ブイ． | Method and reactor for anaerobic wastewater purification |
| JP2009522095A (en) * | 2006-01-05 | 2009-06-11 | バイオタン システムズ インターナショナル ビー．ブイ． | Method and reactor for anaerobic wastewater purification |
| JP2012050910A (en) * | 2010-08-31 | 2012-03-15 | Kobelco Eco-Solutions Co Ltd | Upflow type reaction tank, water treatment method using the reaction tank, and water treatment apparatus equipped with the reaction tank |
| JP2012125716A (en) * | 2010-12-16 | 2012-07-05 | Japan Organo Co Ltd | Flocculation sedimentation apparatus |
-
1984
- 1984-11-06 JP JP59233659A patent/JPS61111200A/en active Pending
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2006051490A (en) * | 2004-01-15 | 2006-02-23 | Sumitomo Heavy Ind Ltd | Anaerobic treatment apparatus and method |
| JP2009522096A (en) * | 2006-01-05 | 2009-06-11 | バイオタン システムズ インターナショナル ビー．ブイ． | Method and reactor for anaerobic wastewater purification |
| JP2009522095A (en) * | 2006-01-05 | 2009-06-11 | バイオタン システムズ インターナショナル ビー．ブイ． | Method and reactor for anaerobic wastewater purification |
| US8021552B2 (en) | 2006-01-05 | 2011-09-20 | Veolia Water Solutions & Technologies Support | Process and reactor for anaerobic waste water purification |
| US8043506B2 (en) | 2006-01-05 | 2011-10-25 | Biothane Systems International B.V. | Process and reactor for anaerobic waste water purification |
| JP2012050910A (en) * | 2010-08-31 | 2012-03-15 | Kobelco Eco-Solutions Co Ltd | Upflow type reaction tank, water treatment method using the reaction tank, and water treatment apparatus equipped with the reaction tank |
| JP2012125716A (en) * | 2010-12-16 | 2012-07-05 | Japan Organo Co Ltd | Flocculation sedimentation apparatus |
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