JPH0318955B2 - - Google Patents

Info

Publication number
JPH0318955B2
JPH0318955B2 JP14572081A JP14572081A JPH0318955B2 JP H0318955 B2 JPH0318955 B2 JP H0318955B2 JP 14572081 A JP14572081 A JP 14572081A JP 14572081 A JP14572081 A JP 14572081A JP H0318955 B2 JPH0318955 B2 JP H0318955B2
Authority
JP
Japan
Prior art keywords
digestion tank
liquid
digestion
digester
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
JP14572081A
Other languages
Japanese (ja)
Other versions
JPS5845796A (en
Inventor
Kaoru Chigusa
Yutaka Takemoto
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 KANKYO EISEI KENKYUSHO KK
Original Assignee
NISHIHARA KANKYO EISEI KENKYUSHO KK
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 KANKYO EISEI KENKYUSHO KK filed Critical NISHIHARA KANKYO EISEI KENKYUSHO KK
Priority to JP56145720A priority Critical patent/JPS5845796A/en
Publication of JPS5845796A publication Critical patent/JPS5845796A/en
Publication of JPH0318955B2 publication Critical patent/JPH0318955B2/ja
Granted legal-status Critical Current

Links

Classifications

    • Y02W10/12

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

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。高
膿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、撹拌によつ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つて所
定の処理が行われる。この消化汚泥と脱離液との
分離は、従来の方法では静置による沈降分離作用
によつているため、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
て槽の有効容積を縮少する等の別の欠点を生じ
る。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for anaerobically digesting highly concentrated organic wastewater such as human waste. In the anaerobic digestion method applied to highly purulent organic wastewater, the substrate is brought into contact with anaerobic bacteria by heating and stirring, which promotes the decomposition of the substrate and the production of metabolic products such as methane gas. A predetermined treatment is performed by separating the sludge containing a large amount of anaerobic bacteria from the desorbed liquid. In conventional methods, this separation of the digested sludge and the desorbed liquid is based on the sedimentation separation effect caused by standing still, and the separation effect is often not sufficient even after a long residence time, and the separated liquid and the desorbed liquid The disadvantage is 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 will increase and gas generation will be suppressed, and solids such as sand mixed in the liquid to be treated will settle and cause This results in other disadvantages such as reducing the effective volume of the device.

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。
This invention does not have the above-mentioned drawbacks, and
The purpose 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.

つぎにこの発明方法の工程の一例を図面にした
がつて説明する。第1図において、し尿のような
高濃度有機性廃水は、まず消化槽1内に導入さ
れ、嫌気性条件のもとで消化処理されることによ
つてメタン発酵を行う。そして消化液は、限外濾
過装置2に送られて圧力差により濾過される。瀘
液は脱離液として後続の2次処理工程に送られ、
濃縮液の一部は消化槽1に返送され、残部は余剰
汚泥として排出される。なお濃縮液は全量消化槽
1に返送し、消化槽1より直接余剰汚泥を排出し
てもよい。
Next, an example of the steps of the method of this invention will be explained with reference to the drawings. In FIG. 1, highly concentrated organic wastewater such as human waste is first introduced into a digestion tank 1, and is digested under anaerobic conditions to undergo methane fermentation. The digestive fluid is then sent to the ultrafiltration device 2 and filtered by the pressure difference. The filtrate is sent to the subsequent secondary treatment process as a desorbed liquid.
A part of the concentrated liquid is returned to the digestion tank 1, and the remainder is discharged as surplus sludge. Incidentally, the entire concentrated liquid may be returned to the digestion tank 1, and the excess sludge may be directly discharged from the digestion tank 1.

ここで、重量なことは、本発明の一層具体的な
構成にある。すなわち、本発明では限外濾過装置
2は、消化槽1に一体的に設けるか、消化槽1内
に直接に収容させる。この構成により、消化槽1
内のメタン発酵によるガス圧や、消化槽混合液の
水位圧が濾過圧の一部として利用することがで
き、効率的かつ経済的に運転が可能となる。
Here, the weight lies in the more specific configuration of the present invention. That is, in the present invention, the ultrafiltration device 2 is provided integrally with the digestion tank 1 or is housed directly within the digestion tank 1. With this configuration, the digestion tank 1
The gas pressure from methane fermentation in the digester and the water level pressure of the mixed liquid in the digester can be used as part of the filtration pressure, allowing efficient and economical operation.

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、およびよく撹拌す
ることが重要である。この発明によれば、消化槽
1内で生じた消化液は、限外濾過装置2の作用で
脱離液を除去することによつて濃縮させるので、
消化槽1内での処理能力を高く維持できるほか、
限外濾過装置2を消化槽1に一体的に設けるか、
消化槽1内に収納させて構成するので、限外濾過
装置2の気密性を容易に保つことができ、濃縮液
と空気と接触することがないので、メタン発酵菌
の活性を損なうことがない。
In order to efficiently carry out methane fermentation in the digestion tank 1, the concentration of microorganisms in the tank must be maintained at a high level.
It is important to ensure anaerobic conditions and good agitation. According to this invention, the digestive juice produced in the digestion tank 1 is concentrated by removing the desorbed liquid by the action of the ultrafiltration device 2.
In addition to maintaining high processing capacity in the digestion tank 1,
Either the ultrafiltration device 2 is provided integrally with the digestion tank 1, or
Since it is configured to be housed in the digestion tank 1, the airtightness of the ultrafiltration device 2 can be easily maintained, and since the concentrated liquid does not come into contact with air, the activity of the methane fermentation bacteria is not impaired. .

以上のように、この発明によれば、消化槽内に
おける嫌気性消化処理によつて生じた消化液は、
限外濾過装置によつて消化槽のガス圧および/ま
たは消化槽混合液の水位圧を利用して効率的かつ
経済的に濃縮され、瀘液だけが脱離液として2次
処理工程に送られる。したがつて、嫌気性消化処
理の処理能力を高め、2次処理工程の負荷の軽減
を達成できる。さらに消化槽内における沈降分離
機能を軽減し、もしくは不要とすることができる
ので、消化槽総容積を小さくできる。しかも限外
濾過の濃縮液は大気と接触することなく循環され
るので、メタン菌の活性を損なうことがない。
As described above, according to the present invention, the digestive fluid produced by the anaerobic digestion treatment in the digestion tank is
The ultrafiltration device utilizes the gas pressure of the digester tank and/or the water level pressure of the digester mixed liquid to efficiently and economically concentrate, and only the filtrate is sent to the secondary treatment process as the desorbed liquid. . Therefore, the throughput of anaerobic digestion treatment can be increased, and the load on the secondary treatment process can be reduced. Furthermore, since the sedimentation separation function within the digestion tank can be reduced or eliminated, the total volume of the digestion tank can be reduced. Moreover, since the ultrafiltrated concentrate is circulated without coming into contact with the atmosphere, the activity of the methane bacteria is not impaired.

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

図はこの発明方法の工程の一例を示すフローシ
ートである。 1……消化槽、2……限外濾過装置。
The figure is a flow sheet showing an example of the steps of the method of this invention. 1... Digestion tank, 2... Ultrafiltration device.

Claims (1)

【特許請求の範囲】[Claims] 1 高濃度有機性廃水を消化槽内で嫌気性消化さ
せ、この消化液を前記消化槽に一体的に設ける
か、もしくは消化槽内に収納した限外濾過装置に
よつて前記消化槽のガス圧および/または消化槽
混合液の水位圧を濾過圧として用いて限外濾過
し、濃縮液の少なくとも一部は上記消化槽に返送
し、瀘液は脱離液として外部に取出すことを特徴
とする高濃度有機性廃水の嫌気性消化方法。
1 Highly concentrated organic wastewater is anaerobically digested in a digestion tank, and this digestive fluid is either provided integrally in the digestion tank, or the gas pressure in the digestion tank is reduced by using an ultrafiltration device housed in the digestion tank. and/or ultrafiltration is performed using the water level pressure of the digester mixed liquid as filtration pressure, at least a part of the concentrated liquid is returned to the digester, and the filtrate is taken out as a separated liquid. Anaerobic digestion method for highly concentrated organic wastewater.
JP56145720A 1981-09-16 1981-09-16 Anaerobic digestion of highly-concentrated organic waste water Granted JPS5845796A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP56145720A JPS5845796A (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
JP56145720A JPS5845796A (en) 1981-09-16 1981-09-16 Anaerobic digestion of highly-concentrated organic waste water

Publications (2)

Publication Number Publication Date
JPS5845796A JPS5845796A (en) 1983-03-17
JPH0318955B2 true JPH0318955B2 (en) 1991-03-13

Family

ID=15391564

Family Applications (1)

Application Number Title Priority Date Filing Date
JP56145720A Granted JPS5845796A (en) 1981-09-16 1981-09-16 Anaerobic digestion of highly-concentrated organic waste water

Country Status (1)

Country Link
JP (1) JPS5845796A (en)

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62273100A (en) * 1986-05-22 1987-11-27 Kubota Ltd Treatment of sewage
JPS63305997A (en) * 1987-06-05 1988-12-13 Ebara Infilco Co Ltd Process for treating sewage and wastes
JPH03199A (en) * 1989-05-25 1991-01-07 Ebara Infilco Co Ltd Methane fermentation treatment
JP2010017614A (en) * 2008-07-08 2010-01-28 Kurita Water Ind Ltd Method and apparatus for treating organic wastewater
JP5801769B2 (en) * 2012-06-28 2015-10-28 水ing株式会社 Method and apparatus for anaerobic digestion treatment of organic wastewater
EP2958663B1 (en) 2013-02-22 2020-04-08 BL Technologies, Inc. Open tank reactor with membrane assembly for supporting a biofilm
JP5860989B2 (en) * 2015-06-10 2016-02-16 株式会社神鋼環境ソリューション Water treatment method and water treatment apparatus

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4840971A (en) * 1971-10-01 1973-06-15
JPS54102056A (en) * 1978-01-27 1979-08-11 Ebara Infilco Co Ltd Process for high-speed treatment of waste water
JPS55149681A (en) * 1979-05-10 1980-11-21 Kuraray Co Ltd Disposal method for waste water disposed with activated sludge

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4840971A (en) * 1971-10-01 1973-06-15
JPS54102056A (en) * 1978-01-27 1979-08-11 Ebara Infilco Co Ltd Process for high-speed treatment of waste water
JPS55149681A (en) * 1979-05-10 1980-11-21 Kuraray Co Ltd Disposal method for waste water disposed with activated sludge

Also Published As

Publication number Publication date
JPS5845796A (en) 1983-03-17

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