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
Links
- 230000029087 digestion Effects 0.000 claims description 28
- 239000007788 liquid Substances 0.000 claims description 18
- 238000000034 method Methods 0.000 claims description 10
- 238000000108 ultra-filtration Methods 0.000 claims description 9
- 239000002351 wastewater Substances 0.000 claims description 5
- 230000001079 digestive effect Effects 0.000 claims description 4
- 239000000706 filtrate Substances 0.000 claims description 3
- 239000012530 fluid Substances 0.000 claims description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 3
- 238000001914 filtration Methods 0.000 claims description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 12
- 238000000926 separation method Methods 0.000 description 5
- 241000894006 Bacteria Species 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 238000000855 fermentation Methods 0.000 description 4
- 230000004151 fermentation Effects 0.000 description 4
- 239000010802 sludge Substances 0.000 description 4
- 238000004062 sedimentation Methods 0.000 description 3
- 239000000758 substrate Substances 0.000 description 3
- 241001148471 unidentified anaerobic bacterium Species 0.000 description 3
- 239000012141 concentrate Substances 0.000 description 2
- 239000010800 human waste Substances 0.000 description 2
- 230000001771 impaired effect Effects 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 238000013019 agitation Methods 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 238000003795 desorption Methods 0.000 description 1
- 235000011389 fruit/vegetable juice Nutrition 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000002503 metabolic effect Effects 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 230000002035 prolonged effect Effects 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
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)
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.
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)
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)
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 |
-
1981
- 1981-09-16 JP JP56145720A patent/JPS5845796A/en active Granted
Patent Citations (3)
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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