JPS61242696A - Method for fermenting methane - Google Patents
Method for fermenting methaneInfo
- Publication number
- JPS61242696A JPS61242696A JP60085250A JP8525085A JPS61242696A JP S61242696 A JPS61242696 A JP S61242696A JP 60085250 A JP60085250 A JP 60085250A JP 8525085 A JP8525085 A JP 8525085A JP S61242696 A JPS61242696 A JP S61242696A
- Authority
- JP
- Japan
- Prior art keywords
- carrier
- methane fermentation
- reaction tank
- raw water
- methane
- 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
-
- 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)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- 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、有機物を含んだ廃水などの原水に微生物を作
用させてメタン発酵を行なう方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention relates to a method for performing methane fermentation by allowing microorganisms to act on raw water such as wastewater containing organic matter.
[従来の技術]
メタン発酵とは、有機物に各種の嫌気性微生物を作用さ
せて有機物を分解し、メタンと二酸化炭素を生成する発
酵である。このメタン発酵は、下水処理場などで大量に
生成される活性汚泥を消化分解して汚泥投棄量の減少を
図るために1またはし尿処理あるいは有機物を含む各種
産業廃水の生化学的酸素要求月(BOD)を減少させる
ために利用されている。[Prior Art] Methane fermentation is a fermentation in which various anaerobic microorganisms act on organic matter to decompose it and produce methane and carbon dioxide. This methane fermentation is used to reduce the amount of sludge dumped by digesting and decomposing activated sludge produced in large quantities at sewage treatment plants, etc., or by treating human waste or biochemical oxygen demand for various industrial wastewater containing organic matter. It is used to reduce BOD).
このメタン発酵の一つの方法として1反応槽内に菌体を
浮遊させた状態で、原液と菌体とを接触yせる方法が知
られている。しかしながら、このような先行技術では、
原水と菌体との接触が良好ではなく、発酵に長時間を必
要とするという問題がある。この問題を解決するための
他の先行技術として、菌体を担体に担持させて反応槽内
に装入し、この担体を反応槽内に固定的に配置した状態
でメタン発酵を行なう、所謂固定床式のメタン発酵が開
発されている。As one method for this methane fermentation, a method is known in which a stock solution and the bacterial cells are brought into contact with each other while the bacterial cells are suspended in a reaction tank. However, in such prior art,
There is a problem in that the contact between the raw water and the bacterial cells is not good, and fermentation requires a long time. Another prior art technique to solve this problem is a so-called immobilization method in which bacterial cells are supported on a carrier and charged into a reaction tank, and methane fermentation is performed with the carrier fixedly placed in the reaction tank. Bed-type methane fermentation has been developed.
[発明が解決しようとする問題点]
ところが固定床式のメタン発酵が有効性を発揮するのは
発酵の初期段階だけであり、発酵の進行につれて原水中
のSSが担体間に蓄積して目詰まりを起こすなどという
新たな問題が生じている。[Problems to be solved by the invention] However, fixed bed methane fermentation is effective only in the initial stage of fermentation, and as fermentation progresses, SS in the raw water accumulates between the carriers and causes clogging. New problems have arisen, such as the occurrence of
また上記目詰まりに至らないまでも、所謂チャネリング
現象が生じて原水の局部的流通を招くこともあり、いず
れにせよメタン発酵が思うように促進されていない。Furthermore, even if the clogging does not occur, a so-called channeling phenomenon may occur, leading to local distribution of raw water, and in any case, methane fermentation is not promoted as desired.
したがって本発明の目的は、−J−記現状に鑑み、メタ
ン発酵の進行が促進されるようにしたメタン発酵方法を
提供することである。Therefore, an object of the present invention is to provide a methane fermentation method that promotes the progress of methane fermentation in view of the current situation described in -J-.
E問題点を解決する為の手段]
本発明は、菌体全相持した粒径2〜15mmの担体を原
木とり(に縦型の生物反応槽に装入し、該槽内に強制御
−A流を形成して該担体を浮遊さゼることにより該Ji
1体の見掛占有体積を120%以−Lに膨張させて操業
する点に要旨を有するメタン発酵方法である。Means for Solving Problem E] In the present invention, a carrier with a particle size of 2 to 15 mm containing all bacterial cells is charged into a vertical biological reaction tank, and a strongly controlled -A The Ji is suspended by forming a stream to suspend the carrier.
This methane fermentation method is characterized in that it is operated by expanding the apparent occupied volume of one body to 120% or more.
[作用]
本発明1こ従えば、菌体を担持して粒径2〜15mn+
の担体を原水と共に縦型の生物反応槽に装入し、該槽内
に強制御−yノ流を形成して該担体を浮遊させることに
より該][1体の見掛占有体積を120%以上に膨張さ
せて操業するようにしたので、菌体を1!1持した相体
は原水中に含まれるSSによって目詰まりを生じること
なくメタン発酵が効率よ〈進行することになる。[Function] According to the present invention, particles with a particle diameter of 2 to 15 m+ can be obtained by supporting bacterial cells.
By charging the carrier together with raw water into a vertical biological reaction tank and suspending the carrier by forming a strongly controlled flow in the tank, the apparent occupied volume of one body was reduced to 120%. Since the operation was carried out with the expansion above, methane fermentation proceeded efficiently in the phase body having 1:1 bacterial cells without clogging due to SS contained in the raw water.
第1図は、本発明を実施するために構成される反応槽の
一例を示す概略図である。反応槽1内には、菌体を担持
した担体5が装入されており、この反応槽1内にはメタ
ン発酵が行なわれるべき有機性原料を含んだ原水が管路
2を通して反応槽1のFカから流入される。該反応槽1
のに1部付近(但し液面より下方)からは、前記管路2
に連続されるべき管路3が取出されており、この管路3
にはその途中に循環ポンプ4が設けられている。FIG. 1 is a schematic diagram showing an example of a reaction tank configured to carry out the present invention. A carrier 5 carrying bacterial cells is placed in the reaction tank 1, and raw water containing organic raw materials to be subjected to methane fermentation is fed into the reaction tank 1 through a pipe 2. It flows in from F. The reaction tank 1
However, from near part 1 (but below the liquid level), the pipe 2
A pipe line 3 to be connected to the
A circulation pump 4 is provided in the middle.
循環ポンプ4を駆動し矢印方向への強制循環を行なうこ
とによって、反応槽l内に強制上!A流を形成すること
ができる。このようにして反応槽1内に強制−1−91
流を形成すれば、担体5に担持された菌体は槽内におい
て浮遊状態を形成し、有機性原料と菌体との接触頻度が
増してメタン発酵が迅速に進行する。またSS等による
目詰まりの恐れもないから、長期間安定]7てメタン発
酵を継続することができる。メタン発酵によって生成し
たCH4,CO2およびその他WI鮭生成物は、反応槽
1の頂部に連結された管路6を通して回収容器(図示せ
ず)に回収される。またメタン発酵が行なわれた後の処
理液は反応槽lの−に1部付近に連結された排出管7か
らυ1出される。By driving the circulation pump 4 and performing forced circulation in the direction of the arrow, the inside of the reaction tank l is forcibly circulated! Stream A can be formed. In this way, the force-1-91 is forced into the reaction tank 1.
If the flow is formed, the microbial cells supported on the carrier 5 will form a floating state in the tank, and the frequency of contact between the organic raw material and the microbial cells will increase, and methane fermentation will proceed rapidly. Furthermore, since there is no fear of clogging due to SS, etc., methane fermentation can be continued for a long period of time. CH4, CO2 and other WI salmon products produced by methane fermentation are collected through a pipe 6 connected to the top of the reaction tank 1 into a collection vessel (not shown). Further, the treated liquid after methane fermentation is discharged υ1 from a discharge pipe 7 connected to the -1 part of the reaction tank 1.
前記t−!体5は一般に球状である、たとえば焼成レン
ガ製であるが、ラーシッヒリング、その他どの様なもの
でもよい。担体5の大きさについては制限があり、球状
である場合はその粒径は2〜15’mmから選ばれる。Said t-! The body 5 is generally spherical, for example made of fired brick, but may also be a Raschig ring or any other material. There are restrictions on the size of the carrier 5, and when it is spherical, the particle size is selected from 2 to 15'mm.
球形以外のものについては、最大部が15mm以下、最
小部が2fflffl以−1−であればよい。このよう
な担体5を反応槽1内に原水と共に装入し、前記循環ポ
ンプ4によって強制」−A流を形成すれば1[!体5は
原水中に浮遊され、Jr!休5体装入状態(浮遊前)に
おける見掛占有体積の1−肩が認められる。そしてこの
見掛占有体積が浮遊前の120%以4−となるように、
循環ポンプ4による循環流量が選ばれ、これによって目
詰まりの防止が確実となる。120%未満であると浮遊
不完全であり目詰まり防止の効果が不確実となる。For shapes other than spheres, the maximum part may be 15 mm or less and the minimum part may be 2fffffl or more -1-. If such a carrier 5 is charged into the reaction tank 1 together with raw water and a forced "-A flow is formed by the circulation pump 4, 1[!! Body 5 is suspended in raw water, and Jr. A 1-shoulder difference in the apparent occupied volume in the state of loading five bodies (before floating) is observed. Then, so that this apparent occupied volume is 120% or more of that before floating,
The circulation flow rate by the circulation pump 4 is selected, thereby ensuring prevention of clogging. If it is less than 120%, floating will be incomplete and the effect of preventing clogging will be uncertain.
担体5の粒径を前記範囲に限定したのは、粒径が2mm
以下のものは現在の造粒技術では製造不可能であり、一
方粒径が15filI11以−1−になると循環ポンプ
4による流速を必要量−1−に大きくしなければ相体5
の見掛占有体積を120%以上とする様な浮遊状態を得
ることが困難であり、したがって不経済となるからであ
る。担体5の粒径と槽内上昇流速LVとの関係の一例を
第2図に示す。The reason why the particle size of the carrier 5 is limited to the above range is that the particle size is 2 mm.
The following cannot be manufactured using current granulation technology; on the other hand, if the particle size exceeds 15 filI11-1-, the phase 5
This is because it is difficult to obtain a floating state in which the apparent occupied volume is 120% or more, and it is therefore uneconomical. An example of the relationship between the particle size of the carrier 5 and the upward flow velocity LV in the tank is shown in FIG.
[実施例コ
第1表は本発明実施例及び比較例の各結果を併記して示
すものである。比較例としては担体5を用いずに菌体を
反応槽l内に浮遊させたときのものを示す。ここで反応
槽1は内径が100mmφ。[Example Table 1 shows the results of the present invention examples and comparative examples. As a comparative example, an example in which bacterial cells were suspended in the reaction tank 1 without using the carrier 5 is shown. Here, the reaction tank 1 has an inner diameter of 100 mmφ.
高さ2mmφの円筒である。但し第1表においてLVは
循環ポンプ4による強制1二昇流の流速を、またTOC
は全有機炭素を、更にVSは原水に含有されている有機
物質を夫々示しており、反応温度は37°Cであった。It is a cylinder with a height of 2 mmφ. However, in Table 1, LV is the flow rate of forced upward flow by circulation pump 4, and TOC
indicates total organic carbon, and VS indicates organic substances contained in the raw water, and the reaction temperature was 37°C.
第1表
第1表から理解されるように、本発明に適用される反応
槽lを用いてメタン発酵を行なうと、生菌体を浮遊した
だけの従来のメタン発酵と比較して、処理時間が短時間
となり、メタン発酵が迅速に行なわれた。また本発明に
従えば、従来見られていた目詰まりやチャネリング現象
が見られず、したがってメタン発酵が効率よく進行する
。Table 1 As can be understood from Table 1, when methane fermentation is carried out using the reaction tank 1 applied to the present invention, the processing time is longer than in the conventional methane fermentation in which live bacterial cells are simply suspended. The time was short, and methane fermentation took place quickly. Further, according to the present invention, clogging and channeling phenomena that were conventionally observed are not observed, and therefore methane fermentation proceeds efficiently.
[発明の効果]
本発明では、菌体を担持した担体の粒径を2〜15mm
に限定し、この範囲の粒径を有する押体の反応槽内にお
ける見掛占有体積が120%以上となるように浮遊させ
ることによって、従来の問題点を解消し、1」詰まりや
チャネリング現象が生じるのを防ぎ、効率良くメタン発
酵が進行することとなった。[Effect of the invention] In the present invention, the particle size of the carrier supporting bacterial cells is 2 to 15 mm.
By limiting the size of particles in this range and suspending them so that the apparent occupied volume in the reaction tank is 120% or more, the conventional problems can be solved and 1. This prevents this from occurring, allowing methane fermentation to proceed efficiently.
第1図は木発す1を実施するために構成される反応槽1
の概略図、第2図は担体5の粒径と流速LVとの関係を
示すグラフである。
■・・・反応槽 4・・・循環ポンプ5・・・担
体Figure 1 shows a reaction tank 1 configured to carry out Kiwasu 1.
FIG. 2 is a graph showing the relationship between the particle size of the carrier 5 and the flow rate LV. ■...Reaction tank 4...Circulation pump 5...Carrier
Claims (1)
型の生物反応槽に装入し、該槽内に強制上昇流を形成し
て該担体を浮遊させることにより該担体の見掛占有体積
を120%以上に膨張させて操業することを特徴とする
メタン発酵方法。A carrier with a particle size of 2 to 15 mm carrying bacterial cells is charged into a vertical biological reaction tank together with raw water, and a forced upward flow is formed in the tank to suspend the carrier, thereby reducing the apparent occupation of the carrier. A methane fermentation method characterized by operating by expanding the volume to 120% or more.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP60085250A JPS61242696A (en) | 1985-04-19 | 1985-04-19 | Method for fermenting methane |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP60085250A JPS61242696A (en) | 1985-04-19 | 1985-04-19 | Method for fermenting methane |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS61242696A true JPS61242696A (en) | 1986-10-28 |
Family
ID=13853320
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP60085250A Pending JPS61242696A (en) | 1985-04-19 | 1985-04-19 | Method for fermenting methane |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS61242696A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH01224099A (en) * | 1988-03-03 | 1989-09-07 | Pub Works Res Inst Ministry Of Constr | Anaerobic digestion method with fluidized bed |
WO2014156216A1 (en) * | 2013-03-27 | 2014-10-02 | 栗田工業株式会社 | Anaerobic treatment method |
-
1985
- 1985-04-19 JP JP60085250A patent/JPS61242696A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH01224099A (en) * | 1988-03-03 | 1989-09-07 | Pub Works Res Inst Ministry Of Constr | Anaerobic digestion method with fluidized bed |
WO2014156216A1 (en) * | 2013-03-27 | 2014-10-02 | 栗田工業株式会社 | Anaerobic treatment method |
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