JPS58128198A - Method and device for methane fermentation - Google Patents

Method and device for methane fermentation

Info

Publication number
JPS58128198A
JPS58128198A JP57009361A JP936182A JPS58128198A JP S58128198 A JPS58128198 A JP S58128198A JP 57009361 A JP57009361 A JP 57009361A JP 936182 A JP936182 A JP 936182A JP S58128198 A JPS58128198 A JP S58128198A
Authority
JP
Japan
Prior art keywords
methane
tank
base material
methane fermentation
bacteria
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
Application number
JP57009361A
Other languages
Japanese (ja)
Inventor
Kuninori Azuma
東 国徳
Haruhisa Furuishi
古石 治久
Takaishi Muranaka
村中 高石
Teiji Takashima
高島 禎治
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.)
KANDA KOGYO KK
Panasonic Holdings Corp
Original Assignee
KANDA KOGYO KK
Matsushita Electric Industrial Co Ltd
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 KANDA KOGYO KK, Matsushita Electric Industrial Co Ltd filed Critical KANDA KOGYO KK
Priority to JP57009361A priority Critical patent/JPS58128198A/en
Publication of JPS58128198A publication Critical patent/JPS58128198A/en
Pending 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

Landscapes

  • Treatment Of Sludge (AREA)

Abstract

PURPOSE:To ferment methane effectively even from base material such as animal org. waste by supplying the liquid base material obtained by making org. waste soluble into a methane fermenting tank in a way as to contact successively with the bacteria held in said tank. CONSTITUTION:First, a 3-way valve 7 is operated to communicate a suction pipe 9 with a circulating pipe 2, and the liquid base material 4 which is beforehand made soluble in a tank 8 is sucked up with a pump 3 into a methane fermenting tank 1. Then, the valve 7 is operated to disconnect the pipe 7 and to open the pipe 2. Thereafter, the material 4 in the tank 1 is circulated with the pump 3 and the solubilized liquid base material 4 is subjected to required methane fermentation by the facultative anaerobic bacteria and methane bacteria held in bacterium holding members 5, whereby methane is formed. The formed methane is removed with a removing pipe 11, and the overflow liquid is discharged into a settling tank 13. The sludge accumulated in the inside bottom is discharged with a drain part 10.

Description

【発明の詳細な説明】 本発明は蓄産加工廃棄物、水産廃棄物、その他農産廃棄
物等を利用してメタンを得るメタン発酵方法およびその
装置に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a methane fermentation method and apparatus for producing methane using waste products such as agricultural waste, fishery waste, and other agricultural waste.

一般に畜産物、水産物、農産物等の廃棄物の処理として
は焼却が多いが、近年、これをエネルギー資源として利
用することが開発されてきている。
In general, incineration is often used to dispose of waste such as livestock products, marine products, agricultural products, etc., but in recent years, the use of this waste as an energy resource has been developed.

すなわち、前記廃棄物をメタン発酵させてメタンを得る
ものである。本発明者等は前記メタン発酵について種々
検討を加えたところ、種々の問題があることが判明した
That is, methane is obtained by subjecting the waste to methane fermentation. The present inventors conducted various studies on the methane fermentation and found that there were various problems.

メタンの生成は周知のように炭水化物、脂肪。As is well known, methane is produced by carbohydrates and fats.

たん白などの有機基材をあらかじめ好気性菌によって腐
敗して可溶化し、これに通性嫌気性菌を作用させて高級
脂肪酸、アミノ酸、糖類、低級脂肪酸となし、さらにこ
れらを水素、二酸化炭素、酢酸、プロピオン酸、低級脂
肪酸、アルコール化し、これらにメタン菌を作用させて
メタンを得るものである。そしてメタン菌は嫌気性菌で
あることから、密閉した槽内でメタン発酵をさせるのが
一般的である。
Organic base materials such as proteins are decomposed and solubilized by aerobic bacteria in advance, and then facultative anaerobic bacteria are applied to produce higher fatty acids, amino acids, sugars, and lower fatty acids, which are then converted into hydrogen and carbon dioxide. , acetic acid, propionic acid, lower fatty acids, are alcoholized, and methane bacteria are applied to these to obtain methane. Since methane bacteria are anaerobic bacteria, methane fermentation is generally carried out in a sealed tank.

ところで基材のうち、特に蓄電加工廃棄物あるいは水産
廃棄物等の動物性有機廃棄物は脂肪含有率が高く、これ
をそのまま、前記一般的なメタン発酵を効率的に、ある
いは継続的に行なわせることはほとんど不可能である。
By the way, among the base materials, especially animal organic wastes such as electricity storage processing wastes and fishery wastes have a high fat content, and this can be used as it is to efficiently or continuously carry out the general methane fermentation mentioned above. That is almost impossible.

これは動物性有機廃棄物が一般に脂肪を10〜26%、
と多く含有しており、これらの脂肪類がグリセリンと高
級脂肪酸に分解されるが、前記高級脂肪酸であるパルミ
チン酸、ステアリン酸、オレイン酸等は化学的、生物化
学的に安定であり、その低分子化が遅れる。
This means that animal organic waste generally contains 10-26% fat;
These fats are decomposed into glycerin and higher fatty acids, but the higher fatty acids such as palmitic acid, stearic acid, and oleic acid are chemically and biochemically stable, and their low Molecularization is delayed.

そして廃棄物を日々処理することで新らしい基材を添加
していくと槽内に高級脂肪酸が沈澱、蓄積され、しかも
菌体表面に吸着されてメタン発酵を□1n6 阻害する。
As new substrates are added through the daily treatment of waste, higher fatty acids precipitate and accumulate in the tank, and are adsorbed onto the bacterial surface, inhibiting methane fermentation.

これら動物性有機廃棄物全効果的にメタン発酵させるに
は、槽内の脂肪濃度を500 PPM以下にような低い
脂肪濃度にすることは発酵原液を最低200倍程度に稀
めなければならず、廃棄物を日々数トンと処理するにお
いて、装置がきわめて大きなものとなり、実際には実現
不可能である。
In order to effectively methane ferment all of these animal organic wastes, it is necessary to reduce the fat concentration in the tank to a low fat concentration of 500 PPM or less, which requires diluting the fermentation stock solution by at least 200 times. In processing several tons of waste every day, the equipment would be extremely large, making it practically unfeasible.

本発明はこのような問題に留意し、基材が動物性有機廃
棄物であっても効果的にメタン発酵を行なわせることを
目的とするものである。
The present invention takes these problems into consideration and aims to effectively carry out methane fermentation even when the base material is animal organic waste.

この目的を達成するため、本発明はメタン発酵槽内に菌
を保持部材で保持し、前記菌に対し、有機廃棄物を可溶
化してなる液状の原材を順次接するように供給すること
を基本的方法とするものである。
In order to achieve this object, the present invention holds bacteria in a methane fermentation tank with a holding member, and sequentially supplies liquid raw materials made by solubilizing organic waste to the bacteria so that they come into contact with the bacteria. This is the basic method.

また前記目的を達成するために、本発明はメタン発酵槽
内に菌を保持した苗保持部材を配置し、前記メタン発酵
槽にメタン発酵槽内の基材を循環する循環パイプ全一け
、前記循環パイプにポンプを設けたことを基本的構成と
するものである。
Further, in order to achieve the above object, the present invention includes a seedling holding member that holds bacteria in a methane fermentation tank, a circulation pipe that circulates the base material in the methane fermentation tank, The basic configuration is that a pump is provided in the circulation pipe.

前記方法および構成により、メタン発酵槽内に−おける
菌は流出あるいは沈澱することがなく、苗保持部材にお
いて増殖することはもとよシ、基材が順次菌に接し良好
にメタン発酵が行なわれる効果がある。
With the above method and configuration, the bacteria in the methane fermentation tank will not flow out or settle, and will not only multiply on the seedling holding member, but the substrate will come into contact with the bacteria one after another and methane fermentation will be carried out well. effective.

以下本発明の一実施例を図面にもとづき説明する0 第1図において、1はメタン発酵槽であシ、上部と下部
間に循環パイプ2を接続し、前記循環ノくイブ2中にポ
ンプ3を設け、前記メタン発酵槽1内の可溶化した液状
の基材4が循環するように構成している。1IfI記メ
タン発酵槽1内には複数の苗保持部材6を配置している
。前記苗保持部材5はメタン菌その他通性嫌気性菌が付
着しやすい形状としている。たとえば第4図aのように
1oo〜400デニールのサラン繊維あるいはプラスチ
ック繊維を数本から数10本合わせたもの、同図すのよ
うに枝状に形成したもの、同図Cのように繊維セコ−イ
ル状にしたもの、さらには同図dのようにジグザグ状に
、同図eのように多孔シート状等にする。
An embodiment of the present invention will be described below with reference to the drawings. In FIG. is provided so that the solubilized liquid base material 4 in the methane fermentation tank 1 is circulated. 1IfI A plurality of seedling holding members 6 are arranged in the methane fermentation tank 1. The seedling holding member 5 has a shape that allows methane bacteria and other facultative anaerobic bacteria to easily adhere thereto. For example, as shown in Figure 4a, a combination of several to several dozen Saran fibers or plastic fibers of 10 to 400 deniers, a branch-like structure as shown in Figure 4, and a fiber separator as shown in Figure C. - It can be made into a zigzag shape as shown in the figure d, or a perforated sheet shape as shown in the figure e.

これらの苗保持部材6の配置は、第2図図示のように基
材4の流れに並行に配置する以外に、第3図のように水
平に配置してもよい。
The seedling holding members 6 may be arranged in parallel to the flow of the base material 4 as shown in FIG. 2, or may be arranged horizontally as shown in FIG. 3.

前記メタン発酵槽1内における前記苗保持部材5の上下
部に対応する位置には均流板6を設けている。したがっ
て、液状の基材4は各苗保持部材6に対し、一定の流速
で接しながら流れる。前記循環パイプ2の一部には三方
弁7を設けるとともに基材タンク8よシ液状の基材4を
吸上げパイプ9をもって吸上げ自在にしている0また、
メタン発酵槽1の下部にはドレイ/部1oが設けられて
いる。前記メタン発酵槽1の上部にはメタン取出パイプ
11および溢流パイプ12が接続され、溢流パイプ12
は沈澱槽13に接続されている。
Equalizing plates 6 are provided in the methane fermentation tank 1 at positions corresponding to the upper and lower portions of the seedling holding member 5. Therefore, the liquid base material 4 flows while contacting each seedling holding member 6 at a constant flow rate. A three-way valve 7 is provided in a part of the circulation pipe 2, and the liquid base material 4 can be freely sucked up from the base material tank 8 using a suction pipe 9.
A drain/section 1o is provided at the bottom of the methane fermentation tank 1. A methane extraction pipe 11 and an overflow pipe 12 are connected to the upper part of the methane fermentation tank 1.
is connected to the settling tank 13.

上記構成において、まず三方弁7を操作して吸上げパイ
プ9を循環パイプ2に連通させる。この状態においてポ
ンプ3を運転させることにより、基材タンク8内のあら
かじめ可溶化された液状の基材4をメタン発酵槽1内に
吸い上げる。メタン発酵槽1内に所要量の基材4が流入
すれば、三方弁7を操作して吸上げパイプ9を遮断し、
循環バイブ2を開通させる。
In the above configuration, first, the three-way valve 7 is operated to connect the suction pipe 9 to the circulation pipe 2. By operating the pump 3 in this state, the pre-solubilized liquid base material 4 in the base material tank 8 is sucked into the methane fermentation tank 1. When the required amount of base material 4 flows into the methane fermentation tank 1, the three-way valve 7 is operated to shut off the suction pipe 9.
Open the circulation vibrator 2.

次にメタン発酵槽1内の基材4はポンプ3の運転によシ
循環する。この循環は1日に4回転というゆっくりした
循環あるいは2時間ごとに10分間間欠的に急速循環1
回/分させるが基材4に脂肪が多い場合は循環回数を多
くすることが好ましい。
Next, the base material 4 in the methane fermentation tank 1 is circulated by the operation of the pump 3. This circulation can be carried out either slowly (4 rotations per day) or rapidly (1) intermittently for 10 minutes every 2 hours.
The number of cycles per minute is preferably increased if the base material 4 has a large amount of fat.

可溶化されて液状の基材4は苗保持部材6に保持された
ところの通性嫌気成苗、メタン菌によって所要のメタン
発酵し、メタンを生成する。この生成されたメタンはメ
タン取出パイプ11によって取出される。また、適宜溢
流液は溢流パイプ12を通じて沈澱槽13に排出され、
メタン発酵槽1の内底にたまるスラッジはドレイン部1
oより排出される。
The solubilized and liquid base material 4 undergoes the required methane fermentation by the facultative anaerobic adult seedlings held by the seedling holding member 6 and methane bacteria to produce methane. This generated methane is taken out by a methane take-out pipe 11. In addition, the overflow liquid is appropriately discharged to the settling tank 13 through the overflow pipe 12,
The sludge that accumulates on the inner bottom of the methane fermentation tank 1 is removed from the drain section 1.
It is discharged from o.

上記の装置で発酵した結果は第6図のような結果を得る
The results of fermentation using the above device are as shown in Figure 6.

基材4はハム・ソーセージ60.肉片40.で脂肪含有
率13%の材料を有機物負荷2.5 %、/p 、 D
で発酵させる。グラフの実線ムは一般の槽内に菌体保持
物を設置しない装置で発酵させたもののメタン発生状況
であり、約4週位いから発酵阻害がおこり6週日には殆
んど停止の状態となる。グラフBの破線は本発明の装置
で発酵させたものである。
Base material 4 is ham/sausage 60. Piece of meat 40. Material with fat content of 13% at organic loading of 2.5%, /p, D
Ferment it with The solid line in the graph shows the methane generation situation when fermentation was carried out using a device that does not have bacterial cell retention in a general tank. Fermentation inhibition occurs after about 4 weeks, and it has almost stopped by the 6th week. Become. The broken line in graph B indicates fermentation using the apparatus of the present invention.

この結果は、菌が苗保持部材6に安定に保持され、かつ
増殖され、一方、基材4は循環して菌に接することから
、前記菌が下方に沈澱し、あるいはこの菌に脂肪分が吸
着して菌の活動を阻害しないことによるものと考えられ
る。
This result is because the bacteria are stably held in the seedling holding member 6 and are multiplied, while the base material 4 circulates and comes into contact with the bacteria, so the bacteria settles downward or fat content is absorbed by the bacteria. This is thought to be due to the fact that it does not adsorb and inhibit bacterial activity.

また、第6週で一時低下し、8〜9週で安定しているこ
とは基材4の循環方向を逆転したことによるものと思わ
れる。すなわち循環方向はメタン発酵槽1の下から上部
の方向が基本であるが、この場合、基材4の液面にシャ
ボン状の気泡の発生が多く、メタン取出バイブ11へ出
てくるものがあったので、前記気泡を解消するため循環
を7週日で逆転させたので菌体の保持状況の変化が生じ
1 て低下したものと思う。
Moreover, the fact that it temporarily decreased in the 6th week and stabilized in the 8th to 9th week is probably due to the fact that the circulation direction of the base material 4 was reversed. That is, the circulation direction is basically from the bottom to the top of the methane fermentation tank 1, but in this case, many soap-like bubbles are generated on the liquid surface of the base material 4, and some bubbles come out to the methane extraction vibrator 11. Therefore, in order to eliminate the air bubbles, the circulation was reversed after 7 weeks, which probably caused a change in the state of bacterial cell retention and resulted in a decrease in bacterial cell retention.

以上説明したように本発明によればメタン発酵槽内にお
ける菌が安定し、この菌に対して循環する基材が順次に
接していき、すなわち、基材は攪拌された状態となって
菌による作用を受けて有効にメタン発酵をするものであ
り、特に脂肪分の多い動物性有機廃棄物でも十分にメタ
ン発酵を行なわしめるものであり、産業廃棄物処理と、
エネルギー成牛を有効に行い、その工業的効果の大きい
ものである。
As explained above, according to the present invention, the bacteria in the methane fermentation tank are stabilized, and the circulating substrate sequentially comes into contact with the bacteria, that is, the substrate is in an agitated state, and the bacteria are It is a device that effectively performs methane fermentation under the action of methane, and is particularly effective in methane fermentation even in animal organic waste with a high content of fat, and is useful for industrial waste treatment.
It is effective for energy production and has great industrial effects.

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

第1図は本発明の一実施例のメタン発酵装置の断面図、
第2図および第3図は同装置における苗保持部材の配置
説明図、第4図a−eは前記苗保持部材の構成図、第6
図はガス転換率特性図である。 1・・・・・・メタン発酵槽、2・・・・・・循環パイ
プ、3・・・・・・ポンプ、4・・・・・・基材、5・
・・・・・苗保持部材、7・・・・・・三方弁、8・・
・・・・基材タンク、9・・・・・・吸上げパイプ、1
1・・・・・・メタン取出パイプ。 代理人の氏名 弁理士 中 尾 敏 男 ほか1名第2
図  第3図 第4図 (tス、)  tb+   ccン (d)     
   (ε)第5図 −一十殻l■収
FIG. 1 is a cross-sectional view of a methane fermentation device according to an embodiment of the present invention;
2 and 3 are explanatory diagrams of the arrangement of the seedling holding member in the same device, FIGS. 4 a to 4 e are configuration diagrams of the seedling holding member, and FIG.
The figure is a gas conversion rate characteristic diagram. 1...Methane fermentation tank, 2...Circulation pipe, 3...Pump, 4...Base material, 5.
... Seedling holding member, 7... Three-way valve, 8...
... Base material tank, 9 ... Suction pipe, 1
1...Methane extraction pipe. Name of agent: Patent attorney Toshio Nakao and 1 other person 2nd
Figure 3 Figure 4 (tsu,) tb+ ccn (d)
(ε) Figure 5 - 10 shells 1 ■ Yield

Claims (1)

【特許請求の範囲】 (1)  メタン発酵槽内に菌を保持部材で保持し、前
記菌に対し有機廃棄物を可溶(F、 してなる液状の゛
 基材を順次接するように供給することを特徴とするメ
タン発酵方法。 (′4 基材は循環手段によって保持された菌に供給さ
れることを特徴とする特許請求の範囲第1項に記載のメ
タン発酵方法。 (3)基材の循環はその循環方向を切換えられることを
特徴とする特許請求の範囲第2項に記載のメタン発酵方
法。 (4メタン発酵槽内に菌を保持した菌保持部材を配置し
、前記メタン発酵槽に前記メタン発酵槽内の基材を循環
する循環パイプを設け、前記循環パイプにポンプを設け
てなるメタン発酵装置。 (@ 菌保持部材はメタン発酵槽内における基材の循環
流に沿うように配置されてなる特許請求の範囲第4項に
記載のメタン発酵装置。 (6)ポンプは正逆回転自在に設けられてなる特許請求
の範囲第4項に記載のメタン発酵装置。
[Claims] (1) Bacteria are held in a methane fermentation tank by a holding member, and a liquid base material made of soluble organic waste (F) is sequentially supplied to the bacteria so as to be in contact with the bacteria. ('4) The methane fermentation method according to claim 1, characterized in that the substrate is supplied to the bacteria held by a circulation means. (3) Substrate The method for methane fermentation according to claim 2, characterized in that the circulation direction of the methane fermentation tank can be switched. A methane fermentation device comprising: a circulation pipe for circulating the base material in the methane fermentation tank; and a pump provided on the circulation pipe. (6) The methane fermentation device according to claim 4, wherein the pump is provided so as to be rotatable in forward and reverse directions.
JP57009361A 1982-01-22 1982-01-22 Method and device for methane fermentation Pending JPS58128198A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57009361A JPS58128198A (en) 1982-01-22 1982-01-22 Method and device for methane fermentation

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57009361A JPS58128198A (en) 1982-01-22 1982-01-22 Method and device for methane fermentation

Publications (1)

Publication Number Publication Date
JPS58128198A true JPS58128198A (en) 1983-07-30

Family

ID=11718330

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57009361A Pending JPS58128198A (en) 1982-01-22 1982-01-22 Method and device for methane fermentation

Country Status (1)

Country Link
JP (1) JPS58128198A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4735724A (en) * 1986-07-30 1988-04-05 Gas Research Institute Solids concentrating anaerobic digestion process and apparatus
US6454944B1 (en) 2000-11-08 2002-09-24 Larry J. Raven Process and apparatus for conversion of biodegradable organic materials into product gas
JP2018065088A (en) * 2016-10-19 2018-04-26 ゼネック株式会社 Biogas generating device and biogas electric power generating system using the same
JP2021013927A (en) * 2020-11-05 2021-02-12 ゼネック株式会社 Biogas generating device and biogas electric power generating system using the same

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4735724A (en) * 1986-07-30 1988-04-05 Gas Research Institute Solids concentrating anaerobic digestion process and apparatus
US6454944B1 (en) 2000-11-08 2002-09-24 Larry J. Raven Process and apparatus for conversion of biodegradable organic materials into product gas
JP2018065088A (en) * 2016-10-19 2018-04-26 ゼネック株式会社 Biogas generating device and biogas electric power generating system using the same
JP2021013927A (en) * 2020-11-05 2021-02-12 ゼネック株式会社 Biogas generating device and biogas electric power generating system using the same

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