JPS5845797A - Anaerobic digestion of highly-concentrated organic waste water - Google Patents

Anaerobic digestion of highly-concentrated organic waste water

Info

Publication number
JPS5845797A
JPS5845797A JP56145721A JP14572181A JPS5845797A JP S5845797 A JPS5845797 A JP S5845797A JP 56145721 A JP56145721 A JP 56145721A JP 14572181 A JP14572181 A JP 14572181A JP S5845797 A JPS5845797 A JP S5845797A
Authority
JP
Japan
Prior art keywords
digesting
digestion
highly
waste water
vessel
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.)
Granted
Application number
JP56145721A
Other languages
Japanese (ja)
Other versions
JPH0318956B2 (en
Inventor
Kaoru Chigusa
千種 薫
Yutaka Takemoto
竹本 裕
Shigeru Inami
茂 稲見
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.)
Nishihara Environment Co Ltd
Original Assignee
Nishihara Environmental Sanitation Research 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 Nishihara Environmental Sanitation Research Corp filed Critical Nishihara Environmental Sanitation Research Corp
Priority to JP56145721A priority Critical patent/JPS5845797A/en
Publication of JPS5845797A publication Critical patent/JPS5845797A/en
Publication of JPH0318956B2 publication Critical patent/JPH0318956B2/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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Abstract

PURPOSE:To enhance the efficiency of anaerobic digesting reaction, by anaerobically digesting highly-concentrated organic waste water in a first digesting vessel, concentrating digestive fluid from the first digesting vessel with a centrifugal concentrator, and returning the concentrated liquid to the first digesting vessel. CONSTITUTION:Highly-concentrated organic waste water (a) such as night soil is anaerobically digested in a first digesting vessel 1, the resulting digestive fluid is concentrated by a centrifugal concentrator 2 without being brought into contact with oxygen in air, and at least a part of the concentrated liquid is returned to the first digesting vessel 1 while the remainder is discharged as excess sludge (e). As a result, a condition in each vessel comes to the optimum for digestion, so that the efficiency of digestion is remarkably improved. Consequently, the method can be applied for difficulty decomposable stroma-contg. waste water or highly-loaded operation, and the reduction of the total volume can make the size of installation small.

Description

【発明の詳細な説明】 この発明は、し尿のような高濃度有機性廃水を嫌気性消
化処理する方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for anaerobically digesting highly concentrated organic wastewater such as human waste.

高濃度有機性廃水に対して適用される嫌気性消化法では
、加温、攪拌によって基質と嫌気性細菌とを接触させ、
基質の分解とメタンガス等の代謝生産物の生成を促す作
用と、嫌気性細菌を多量に含有する汚泥と脱離液とを分
離す゛る作用と:によって処理が行われる。この方法C
=もとづく一部の処理プロセスを第1図に示す。原水は
、まず第1消化槽1で嫌気性消化処理を受けたのち、第
2消化槽すに送られ、消化汚泥と脱離液との分離が行わ
れる。そして脱離液は次段の処理工程に送られ、消化汚
泥の一部は第1消化槽1に返送される。この消化汚泥と
脱離液との分−は、従来の方法では静置4=よる沈降分
離作用によっているため、その分離効果は、長い滞留時
間をかけても充分でない場合が多く、脱離液とともに多
量の固形物が流出するという欠点がある。とくに被処理
液中の基質が難分解性で嫌気性細菌の増殖速度が遅くな
る場合には、細菌の脱離液への流出は消化処理の過負荷
状態を招き、消化効率の低下の原因となる。また細菌の
流出を防止するために沈降分離時間をいたずらに長くす
ると、スカム発生頻度を高めてガス発生を抑制したり、
被処理液中に混入している砂などの固形物が沈積して櫂
の有効容積を縮小する等の別の欠点が生じる。
In the anaerobic digestion method applied to highly concentrated organic wastewater, the substrate and anaerobic bacteria are brought into contact with each other by heating and stirring.
Treatment is carried out by: promoting the decomposition of substrates and the production of metabolic products such as methane gas, and separating the sludge containing a large amount of anaerobic bacteria from the desorbed liquid. This method C
A part of the underlying processing process is shown in FIG. The raw water is first subjected to anaerobic digestion treatment in the first digestion tank 1, and then sent to the second digestion tank, where the digested sludge and the desorbed liquid are separated. The desorbed liquid is then sent to the next treatment step, and a portion of the digested sludge is returned to the first digestion tank 1. In the conventional method, the separation between the digested sludge and the desorbed liquid is achieved by the sedimentation separation effect caused by standing still, so the separation effect is often not sufficient even after a long residence time, and the desorbed liquid There is also a drawback that a large amount of solid matter flows out. In particular, if the substrate in the liquid to be treated is difficult to decompose and the growth rate of anaerobic bacteria is slowed down, the flow of bacteria into the desorption liquid may lead to overload of the digestion process and cause a decrease in digestion efficiency. Become. Furthermore, if the sedimentation separation time is unnecessarily prolonged in order to prevent the outflow of bacteria, the frequency of scum generation may be increased and gas generation may be suppressed.
Other drawbacks arise, such as the accumulation of solids such as sand mixed in the liquid to be treated, reducing the effective volume of the paddle.

この発明は、上記のような欠点を伴なわずに、嫌気性消
化反応の効率を高め、後続の処理の負荷を低減させるこ
とができる嫌気性消化方法を提供することを目的として
いる。
An object of the present invention is to provide an anaerobic digestion method that can increase the efficiency of the anaerobic digestion reaction and reduce the burden of subsequent processing without the above-mentioned drawbacks.

つぎにこの発明方法の工程の一例を図面にしたがって説
明する。第2図において、符号1は第1消化槽、2は遠
心P:A1m縮機、3は第2消化槽をそれぞれ示し、遠
心−通論縮機2の気密なハウジングの内部は、連通管4
を介して第1消化槽1の上部に連通している。
Next, an example of the steps of the method of this invention will be explained with reference to the drawings. In FIG. 2, reference numeral 1 indicates the first digester, 2 indicates the centrifugal P:A1m compressor, and 3 indicates the second digester.
It communicates with the upper part of the first digestion tank 1 via.

し尿のような高濃度有機性廃水は、まず第1消化槽1内
に導入され、嫌気性条件のもとで消化も理されることに
よってメタン発酵を行う、そして消化液は、遠心濾過濃
縮82に送られ、−細波の一部は第1消化槽1に返送さ
れ、残部ば余剰汚泥として排出される。またr液は第2
消化檜3償;送られ、さらに消化処理されるとともに消
化汚泥の沈殿分離が行われる。ここで生じた脱離液は後
続の処理工程に送られ、消化汚泥は遠心濾過濃縮機2か
らの濃縮液とともに余剰汚泥として排出される。但し、
第2消化槽6は、設けない場合もある。
Highly concentrated organic wastewater such as human waste is first introduced into the first digestion tank 1 and digested under anaerobic conditions to perform methane fermentation, and the digested liquid is centrifugally filtered and concentrated 82. A part of the sludge is returned to the first digestion tank 1, and the remainder is discharged as surplus sludge. Also, the r liquid is the second
Digested sludge is sent to the cypress, where it is further digested and the digested sludge is separated by precipitation. The desorbed liquid generated here is sent to the subsequent treatment process, and the digested sludge is discharged as surplus sludge together with the concentrated liquid from the centrifugal filtration thickener 2. however,
The second digestion tank 6 may not be provided.

遠心濾過濃縮82の具体的な構造の一例を第2図に示す
。第2図において気密構造のハウジング11内には回転
軸12に支持されたバスケット13が収容され、このバ
スケット13の内面に沿ってP布14が配置されている
。回転軸12とハウジング11との間にはメカニカルシ
ール15が設けられ、ハウジング11内の気密性が保持
されている。そして処理すべき消化液は、供給パイプ1
6を経てP布14の中心部に供給される。回転バスケッ
ト13およびP布14は上下を逆にした円錐台形をなし
、そして高速回転しているので、消化液中の液分はr布
14およびバスケット13の小孔を遠心力の作用で通過
してP液室17内に放射方向に放出され、固形分はP布
14上を回転中心から離れる方向C第3図の上方)に遠
心力の作用で移動したのち、r液室17から隔壁18で
分離された濃縮液室19内に放出される。これによって
消化液の固液分離が効率よく行われ、消化汚泥を多量に
含む濃縮液はパイプ20を経て取出され、P液はパイプ
21を経て第2消化槽3に送られる。
An example of a specific structure of the centrifugal filtration concentration 82 is shown in FIG. In FIG. 2, a basket 13 supported by a rotating shaft 12 is accommodated in a housing 11 having an airtight structure, and a P cloth 14 is arranged along the inner surface of the basket 13. A mechanical seal 15 is provided between the rotating shaft 12 and the housing 11 to maintain airtightness within the housing 11. The digestive fluid to be treated is supplied to the supply pipe 1.
6 and is supplied to the center of the P cloth 14. Since the rotating basket 13 and the P cloth 14 have an upside-down truncated conical shape and are rotating at high speed, the liquid in the digestive juices passes through the small holes of the R cloth 14 and the basket 13 due to the action of centrifugal force. The solid content is released into the P liquid chamber 17 in the radial direction, and the solid content moves on the P cloth 14 in the direction away from the center of rotation C (upward in FIG. 3) due to the action of centrifugal force. The concentrate is discharged into the separated concentrate chamber 19. As a result, solid-liquid separation of the digestive fluid is efficiently performed, the concentrated liquid containing a large amount of digested sludge is taken out via the pipe 20, and the P liquid is sent to the second digestion tank 3 via the pipe 21.

さらにハウジング11の内部は、連通管4v介して第1
消化槽1の上部と連通しているため、第1消化槽で発生
したメタンガスを主体とするガスで充満される。このた
め遠心濾過濃縮1124’通過する液体が空気中の酸素
と接触することはない。
Furthermore, the inside of the housing 11 is connected to the first
Since it communicates with the upper part of the digestion tank 1, it is filled with gas mainly composed of methane gas generated in the first digestion tank. Therefore, the liquid passing through the centrifugal filtration concentration 1124' does not come into contact with oxygen in the air.

なお符号22は、多数のノズル23を設けた洗浄パイプ
を示し、P布14等が目詰りしたときに、作業を中断し
て洗浄を行う際に使用あれる。
The reference numeral 22 indicates a cleaning pipe provided with a large number of nozzles 23, which is used to interrupt the work and perform cleaning when the P cloth 14 or the like becomes clogged.

第1消化槽1内でメタン発酵を効率よく行わせるために
は、槽内の微生物濃度を高水準に保つこと、嫌気性条件
を確実に保つこと、およびよく攪拌することが重要であ
る。この発明によれば、第1消化槽1から取出された消
化液が遠心−通論縮機2で濃縮されたのち返送されるの
で、第1消化槽1内の固形物濃度を高水準(たとえばM
L88が4慢以上)に保つことができ、充分な攪拌な行
うこともできる。また遠心濾過濃縮機2の内部は気密に
保たれているので、空気が混入することはなく、メタン
生成菌の活動は阻害されない、さらに第2消化槽を設け
る場合(二は遠心濾過濃縮J12で生じたP液は第2消
化槽6内で消化および沈殿処理を受けるので、r液にあ
る程度の固形物が混入してい工も支障はない。したがっ
てP布14として幾分目の粗いものを使用することがで
き、目詰りの機会が減少して安定した連続運転を2行う
ことが可能である。また運転中にパイプ22に洗浄水を
供給して洗浄を行っても、洗浄排水は濃縮液中ζ=は混
入せず、P液とともに排出されるので、・返送濃縮液)
の影響はない。
In order to carry out methane fermentation efficiently in the first digestion tank 1, it is important to maintain the microbial concentration in the tank at a high level, to reliably maintain anaerobic conditions, and to stir well. According to this invention, the digestive fluid taken out from the first digestion tank 1 is concentrated in the centrifugal compressor 2 and then returned, so that the solids concentration in the first digestion tank 1 is maintained at a high level (for example, M
L88 can be maintained at 4 degrees or higher, and sufficient stirring can be performed. In addition, since the inside of the centrifugal filtration concentrator 2 is kept airtight, air will not get mixed in and the activity of methane-producing bacteria will not be inhibited. Since the generated P liquid undergoes digestion and precipitation treatment in the second digestion tank 6, there is no problem in processing the R liquid even if some solid matter is mixed in.Therefore, a somewhat coarse mesh material is used as the P cloth 14. This reduces the chance of clogging and allows for stable continuous operation.Furthermore, even if cleaning water is supplied to the pipe 22 during operation, the cleaning waste water will be a concentrated liquid. The medium ζ= is not mixed in and is discharged together with the P solution, so ・return concentrated liquid)
There is no effect.

以上のようにこの発明によれば、第1消化槽からの消化
液を遠心r過濃縮機で濃縮し、その濃縮液は第1消化槽
に返送するように、したので、各消化槽における条件が
消化処理に最適なものとなり、消化効率が格段に向上す
る。このため難分解性基“質を含む廃水や高負荷運転に
も対応で゛き、また総容量の縮小による装置の小形化も
可能である。さらに脱離液の88 、BOD等が低濃度
になるので、2次処理系の負荷が軽減されるという効果
も得ら、・熟る。
As described above, according to the present invention, the digestive juice from the first digestion tank is concentrated using a centrifugal superconcentrator, and the concentrated liquid is returned to the first digestion tank, so that the conditions in each digestion tank are becomes optimal for digestion, and digestion efficiency is greatly improved. Therefore, it can handle wastewater containing difficult-to-decompose substances and high-load operation, and it is also possible to downsize the equipment by reducing the total capacity.Furthermore, the desorbed liquid, such as 88 and BOD, can be reduced in concentration. As a result, the load on the secondary processing system is reduced.

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

第1図は従来の嫌気性消化方法の工程を示すフローシー
ト、第2図はこの発明方法の工程の一例を示すフローシ
ート、第3図はこの発明で使用された遠心濾過濃縮機の
概略的縦断面図である。 1・・・第1消化槽、2・・・遠心濾過濃縮装置、6・
・・第2消化槽、4・・・連通管、11・・・ハウジン
グ、12・・・回転軸、16・j・バスケット、14・
・・P布、15・・・メカニカルシール、16・・・供
給パイプ、17・・・r液室、18・・・隔壁、19・
・・濃縮液室、26・・・ノズル。 特許出願人    株式会社 西原環境衛生研究所余中
1沃0厄
Fig. 1 is a flow sheet showing the steps of a conventional anaerobic digestion method, Fig. 2 is a flow sheet showing an example of the steps of this invention method, and Fig. 3 is a schematic diagram of the centrifugal filtration concentrator used in this invention. FIG. 1... First digestion tank, 2... Centrifugal filtration and concentration device, 6.
...Second digestion tank, 4.Communication pipe, 11.Housing, 12.Rotating shaft, 16.j.basket, 14.
... P cloth, 15... Mechanical seal, 16... Supply pipe, 17... r liquid chamber, 18... Partition wall, 19...
...Concentrate chamber, 26...nozzle. Patent applicant Nishihara Environmental Health Research Institute Co., Ltd.

Claims (1)

【特許請求の範囲】[Claims] (1)高濃度有機性廃水を第1消化槽内で嫌気性消化さ
せ、この消化液を空気中の酸素に接触させ−ることなく
遠心r過淡縮−で―縮し、濃縮液の少なくとも一部を上
記第1消化槽に返送することを特徴とする高濃度有機性
廃水の嫌気性消化方法。 伐)上記遠心濾過濃縮機からのP液を第2消化槽に供給
して嫌気性消化させ、消化汚泥を沈殿分離することを特
徴とする特許請求の範囲第1項記職の高濃度有機性廃水
の嫌気性消化方法。
(1) High-concentration organic wastewater is anaerobically digested in the first digestion tank, and the digested liquid is reduced by centrifugation and over-water reduction without contacting with oxygen in the air. A method for anaerobic digestion of highly concentrated organic wastewater, characterized in that a portion of the wastewater is returned to the first digestion tank. 1) The high-concentration organic compound as described in Claim 1, characterized in that the P solution from the centrifugal filtration and concentration machine is supplied to a second digestion tank for anaerobic digestion, and the digested sludge is separated by sedimentation. Methods of anaerobic digestion of wastewater.
JP56145721A 1981-09-16 1981-09-16 Anaerobic digestion of highly-concentrated organic waste water Granted JPS5845797A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP56145721A JPS5845797A (en) 1981-09-16 1981-09-16 Anaerobic digestion of highly-concentrated organic waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP56145721A JPS5845797A (en) 1981-09-16 1981-09-16 Anaerobic digestion of highly-concentrated organic waste water

Publications (2)

Publication Number Publication Date
JPS5845797A true JPS5845797A (en) 1983-03-17
JPH0318956B2 JPH0318956B2 (en) 1991-03-13

Family

ID=15391589

Family Applications (1)

Application Number Title Priority Date Filing Date
JP56145721A Granted JPS5845797A (en) 1981-09-16 1981-09-16 Anaerobic digestion of highly-concentrated organic waste water

Country Status (1)

Country Link
JP (1) JPS5845797A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6224595A (en) * 1985-07-25 1987-02-02 松下電工株式会社 Discharge lamp lighting apparatus
JPS62100997A (en) * 1985-10-25 1987-05-11 松下電工株式会社 Discharge lamp burner
JP2008136984A (en) * 2006-12-05 2008-06-19 Fuji Electric Holdings Co Ltd Methane fermentation treatment apparatus

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS528660A (en) * 1975-07-09 1977-01-22 Hitachi Ltd Anaerobic digestion of organic waste fluid
JPS5541160A (en) * 1978-09-13 1980-03-22 Meidensha Electric Mfg Co Ltd Dc feeding system for electric railway
JPS5613092A (en) * 1979-07-14 1981-02-07 Shin Meiwa Ind Co Ltd Method and apparatus for treating of organic solid

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS528660A (en) * 1975-07-09 1977-01-22 Hitachi Ltd Anaerobic digestion of organic waste fluid
JPS5541160A (en) * 1978-09-13 1980-03-22 Meidensha Electric Mfg Co Ltd Dc feeding system for electric railway
JPS5613092A (en) * 1979-07-14 1981-02-07 Shin Meiwa Ind Co Ltd Method and apparatus for treating of organic solid

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6224595A (en) * 1985-07-25 1987-02-02 松下電工株式会社 Discharge lamp lighting apparatus
JPS62100997A (en) * 1985-10-25 1987-05-11 松下電工株式会社 Discharge lamp burner
JPH0744077B2 (en) * 1985-10-25 1995-05-15 松下電工株式会社 Discharge lamp lighting device
JP2008136984A (en) * 2006-12-05 2008-06-19 Fuji Electric Holdings Co Ltd Methane fermentation treatment apparatus

Also Published As

Publication number Publication date
JPH0318956B2 (en) 1991-03-13

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