JPS5833040B2 - Anaerobic treatment equipment - Google Patents
Anaerobic treatment equipmentInfo
- Publication number
- JPS5833040B2 JPS5833040B2 JP56031210A JP3121081A JPS5833040B2 JP S5833040 B2 JPS5833040 B2 JP S5833040B2 JP 56031210 A JP56031210 A JP 56031210A JP 3121081 A JP3121081 A JP 3121081A JP S5833040 B2 JPS5833040 B2 JP S5833040B2
- Authority
- JP
- Japan
- Prior art keywords
- reaction tank
- reaction
- gas
- pipe
- 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
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
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Treatment Of Sludge (AREA)
Description
【発明の詳細な説明】 この発明は有機性汚泥や有機性廃液(原液とも記す。[Detailed description of the invention] This invention is applicable to organic sludge and organic waste liquid (also referred to as undiluted liquid).
)をメタン発酵させ、ボイラーやガスエンジン等のエネ
ルギー源としてのガスを回収する嫌気性処理装置に関し
、特に原液が硫化物を含む、例えばアミノ酸製造工程等
から排出される含硫黄蛋白質原液を効果的にメタン発酵
させる嫌気性処理装置に関する。) is used for methane fermentation to recover gas as an energy source for boilers, gas engines, etc., and is particularly effective for processing sulfur-containing protein stock solutions that contain sulfides, such as those discharged from amino acid manufacturing processes. This invention relates to an anaerobic treatment device for methane fermentation.
近年、上述の原液からエネルギーとしての含メタンガス
(消化ガスとも記す。In recent years, methane-containing gas (also referred to as digestion gas) has been produced as energy from the above-mentioned stock solution.
)を回収するためにこれをメタン発酵させることが頻繁
に行われて居り、メタン発酵を効率よく行わせるために
原液を嫌気性液化菌群により酢酸、プロピオン酸、酪酸
などの低分子の揮発性の有機酸とする液化反応(酸生戒
相)と、こうして生成した有機酸をメタン菌群によりメ
タンに転換するメタン化反応(メタン生成相)からなる
二つの反応を有する二相嫌気性消化法が公知である。) is frequently subjected to methane fermentation to recover the methane, and in order to efficiently carry out the methane fermentation, the stock solution is converted to volatile low molecules such as acetic acid, propionic acid, and butyric acid by a group of anaerobic liquefaction bacteria. A two-phase anaerobic digestion method that has two reactions: a liquefaction reaction (acidogenic phase) in which organic acids are converted into organic acids, and a methanation reaction (methane generation phase) in which the organic acids produced in this way are converted to methane by a group of methane bacteria. is publicly known.
この二相嫌気性消化法における各反応は菌群が最も活動
し易いpHや温度を維持することによって反応効率を高
めることができるものであって、そのpHは酸生成相で
は5〜6、メタン生成相では7〜8が最適である。The reaction efficiency of each reaction in this two-phase anaerobic digestion method can be increased by maintaining the pH and temperature at which bacterial groups are most active. In the production phase, 7 to 8 is optimal.
このため従来は酸生成相に消石灰などのpH調整剤を用
いているが、これを用いると薬剤費が嵩むと言う欠点の
他に、メタン生成相では揮発性有機酸が分解し、pHが
上昇しすぎると言う現象が生じ、消化ガスの生成量が低
下する欠点がある。For this reason, pH adjusters such as slaked lime have traditionally been used in the acid generation phase, but in addition to the disadvantage of increasing chemical costs, volatile organic acids decompose in the methane generation phase, causing an increase in pH. This has the disadvantage that the amount of digestive gas produced decreases due to the phenomenon of excessive water consumption.
そこで本発明は上述の欠点を解消するために酸生成相で
特別にpH調整剤を用いずにpHを最適に調整し、これ
によりメタン生成相での消化ガスの生成量を低下させな
い様に改良したのである。Therefore, in order to eliminate the above-mentioned drawbacks, the present invention optimally adjusts the pH in the acid generation phase without using a special pH adjuster, thereby improving the amount of digestion gas produced in the methane generation phase. That's what I did.
以下、図面を参照して本発明を説明すると、1は酸生成
相である第1反応槽2はメタン生成相である第2反応槽
であって、含硫黄蛋白質原液は第1反応槽1に供給され
、こXで嫌気性消化菌群により液化反応を行い、次に第
2反応槽2に供給され、こ5ではメタン菌群によりメタ
ン化反応を行い、消化ガスを発生して脱離液となる。Hereinafter, the present invention will be described with reference to the drawings. The first reaction tank 1 is an acid production phase and the second reaction tank 2 is a methane production phase. The gas is supplied, undergoes a liquefaction reaction by a group of anaerobic digestive bacteria in this X, and is then supplied to the second reaction tank 2, where a methanation reaction is performed by a group of methane bacteria to generate digestive gas and remove the desorbed liquid. becomes.
こうして第2各反応槽で発生した消化ガスは配管3で公
知の脱硫装置4、例えばアルカリ性溶液と接触させる気
液接触型脱硫装置に導いて脱硫し、それから配管5で消
化ガス貯溜タンク6に導いて貯え、ボイラーやガスエン
ジンにエネルキーとして適宜供給する。The digestion gas generated in each of the second reaction tanks is desulfurized by being desulfurized through a pipe 3 to a known desulfurization device 4, such as a gas-liquid contact type desulfurization device in which it is brought into contact with an alkaline solution, and then led to a digestion gas storage tank 6 through a pipe 5. It is stored and supplied as energy key to boilers and gas engines as needed.
又、第2反応槽2に生じた脱離液は図示してないが公知
の好気性処理装置に導いて処理した後、放流等する。Further, the desorbed liquid generated in the second reaction tank 2 is led to a known aerobic treatment device (not shown), treated, and then discharged.
さて、従来は第1反応槽1に消石灰などのpH調整剤を
薬注装置で注入してpHを5〜6に保つため前述した様
な問題点、特に第2反応槽での消化ガスの生成量が低下
すると言う致命的な欠点を生じたのである。Now, conventionally, a pH adjusting agent such as slaked lime was injected into the first reaction tank 1 using a chemical dosing device to maintain the pH at 5 to 6, which caused the problems mentioned above, especially the production of digestion gas in the second reaction tank. This resulted in a fatal drawback: the amount decreased.
そこで本発明は脱硫した消化ガスを第1反応槽1にフィ
ードバックして槽内の原液に気曝し、液化反応によって
第1反応槽中に生じる硫化水素(H2S)をストリッピ
ングするために例えば消化ガス貯溜タンク6と第1反応
槽1との間に配管7を設ける。Therefore, the present invention feeds back the desulfurized digestion gas to the first reaction tank 1, aerates the raw solution in the tank, and strips hydrogen sulfide (H2S) generated in the first reaction tank by the liquefaction reaction. A pipe 7 is provided between the storage tank 6 and the first reaction tank 1.
これにより発生する硫化水素によって下ろうとする第1
反応槽でのpHは硫化水素が消化ガスでストリッピング
されるので下がらない。The first layer that tries to fall due to the hydrogen sulfide generated by this
The pH in the reactor does not drop because the hydrogen sulfide is stripped off by the digestion gas.
事実、この気曝によって硫化水素は容易にストリッピン
グ可能であり、従って、第1反応槽1にフィードバック
する消化ガスの量を調整し酸生成相でのpHを最適に保
てる。In fact, hydrogen sulfide can be easily stripped by this aeration, and therefore the amount of digestion gas fed back to the first reaction tank 1 can be adjusted to keep the pH in the acid production phase optimal.
このため酸生成相での反応は消石灰などのp)l調整剤
を添加しないで良好に進行すると共に、その後第2反応
槽に供給した場合pHが上昇し過ぎることはなく、こ\
でも最適のpH7〜8を維持して反応は良好に進んで従
来に較べれば短かい時間で終ると共に収量も増大し全体
として運転は極めて順調に推移する。Therefore, the reaction in the acid generation phase proceeds well without adding a p)l regulator such as slaked lime, and when it is subsequently supplied to the second reaction tank, the pH does not rise too much.
However, by maintaining the optimum pH of 7 to 8, the reaction progresses well, and compared to conventional methods, it takes less time to complete, the yield increases, and overall the operation progresses very smoothly.
そして、第1反応槽でストリッピングされた硫化水素、
そのために供給した消化ガスの余剰分は配管8で直接に
脱硫装置に導くか、或いは図示の如く第2反応槽で発生
した消化ガスを脱硫装置4に導く配管3にこの配管8を
接続し、硫化水素を除去し、消化ガスは貯溜タンク6に
回収する。and hydrogen sulfide stripped in the first reaction tank;
For this purpose, the surplus of the digestive gas supplied is directly led to the desulfurization equipment through a pipe 8, or this pipe 8 is connected to the pipe 3 that leads the digestion gas generated in the second reaction tank to the desulfurization equipment 4 as shown in the figure. Hydrogen sulfide is removed, and the digestion gas is collected in a storage tank 6.
従って、得られる消化ガスのトータル量は伺等減少しな
い。Therefore, the total amount of digested gas obtained does not decrease.
第1反応槽は配管7でフィードバックされる消化ガスに
よって嫌気性液化菌群を含む汚泥を攪拌、分散し、原液
と混合させる型式のものでも、或いは機械的攪拌装置を
備え、消化ガスの攪拌力だけでは不足する場合にこの機
械的攪拌装置を駆動し、不足を補うものでもよい。The first reaction tank may be of a type in which the sludge containing the anaerobic liquefied bacteria is stirred and dispersed by the digestion gas fed back through the pipe 7 and mixed with the stock solution, or it may be equipped with a mechanical stirring device and the stirring power of the digestion gas may be If this alone is insufficient, this mechanical stirring device may be driven to compensate for the deficiency.
又、全体が液中に浸漬する回転円板を備え、汚泥をこの
回転円板に膜状に付着させて反応を進める回転円盤式の
固定床型反応槽とし、消化ガスは回転円板に付着した汚
泥膜を剥離しない様に槽内に供給してもよい。In addition, the reactor is equipped with a rotating disk that is entirely immersed in the liquid, and the sludge adheres to this rotating disk in a film form to advance the reaction, and the digestion gas is attached to the rotating disk. The sludge film may be fed into the tank without peeling off.
又、第2反応槽も第1反応槽と同様に実質的に酸素を含
まないガスや、機械的攪拌装置でメタン菌群を含む汚泥
を攪拌分散する反応槽、或いは回転円盤式の固定床型反
応槽とすることができる。In addition, the second reaction tank, like the first reaction tank, is a reaction tank in which substantially oxygen-free gas or sludge containing methane bacteria is stirred and dispersed using a mechanical stirring device, or a rotating disk type fixed bed type reaction tank. It can be a reaction tank.
以上の様に本発明は生成した消化ガスを用いて酸生成相
のpHを調整するので、従来の様に薬品代は不要になる
と共に、pH調整剤の溶解槽、注入装置等これに付属す
る機器も不要なので設備コストは安くなり、それでいて
生成した消化ガスの収量は減少しない。As described above, the present invention uses the generated digestive gas to adjust the pH of the acid generation phase, so there is no need for chemicals as in the past, and additional costs such as a dissolution tank and injection device for the pH adjuster are required. Since no equipment is required, equipment costs are lower, and the yield of the generated digestion gas is not reduced.
そして、従来の装置を簡単に改造して実施することもで
き、これによりランニングコスト中からpH調整用薬品
代の項目を無くすると言う大きな効果を発揮する。Furthermore, it is possible to implement the method by simply modifying a conventional device, which has the great effect of eliminating the cost of pH-adjusting chemicals from running costs.
尚、第1反応槽への消化ガスの供給量は第1反応槽のp
H計に連動して制御してもよい。The amount of digestion gas supplied to the first reaction tank is determined by the p of the first reaction tank.
It may be controlled in conjunction with the H meter.
図面は本発明の一実施例のフローシートを示し、図中、
1は第1反応槽(酸生成相)、2は第2反応槽(メタン
生成相)、4は脱硫装置、6は消化ガス貯溜槽、7は消
化ガスを第1反応槽に供給する配管、8は第1反応槽か
らガスを脱硫装置に導く配管を示す。The drawing shows a flow sheet of an embodiment of the present invention, and in the drawing,
1 is a first reaction tank (acid production phase), 2 is a second reaction tank (methane production phase), 4 is a desulfurization device, 6 is a digestion gas storage tank, 7 is a pipe that supplies digestion gas to the first reaction tank, Reference numeral 8 indicates piping that leads gas from the first reaction tank to the desulfurization device.
Claims (1)
成反応を行なわせる第1反応槽と、第1反応槽で生成し
た有機酸を受入れてメタン生成反応を行なわせる第2反
応槽を有する二つの反応を含む嫌気性処理装置において
、 第1反応槽と第2反応槽の両槽から発生するガスを導く
配管と、この配管中に設けられた脱硫装置と、脱硫装置
で処理されたガスを第1反応槽に供給する配管を有する
ことを特徴とする嫌気性処理装置。[Scope of Claims] 1. A first reaction tank that uses organic sludge or organic waste liquid as a stock solution and performs an acid production reaction thereon, and a second reaction tank that receives the organic acid produced in the first reaction tank and performs a methane production reaction thereon. In an anaerobic treatment device including two reactions having two reaction tanks, a pipe for guiding gas generated from both the first reaction tank and the second reaction tank, a desulfurization device installed in this pipe, and a desulfurization device An anaerobic treatment device characterized by having a pipe for supplying the treated gas to a first reaction tank.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP56031210A JPS5833040B2 (en) | 1981-03-06 | 1981-03-06 | Anaerobic treatment equipment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP56031210A JPS5833040B2 (en) | 1981-03-06 | 1981-03-06 | Anaerobic treatment equipment |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS57147498A JPS57147498A (en) | 1982-09-11 |
JPS5833040B2 true JPS5833040B2 (en) | 1983-07-16 |
Family
ID=12325063
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP56031210A Expired JPS5833040B2 (en) | 1981-03-06 | 1981-03-06 | Anaerobic treatment equipment |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5833040B2 (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS60180427U (en) * | 1984-05-10 | 1985-11-30 | 株式会社 エバ−ス | face steamer |
JPS60182042U (en) * | 1984-05-15 | 1985-12-03 | 株式会社 エバ−ス | face steamer |
JPS60184535U (en) * | 1984-05-18 | 1985-12-07 | 株式会社 エバ−ス | face steamer |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH03127696A (en) * | 1989-10-13 | 1991-05-30 | Kajima Corp | Desulfurizer for waste water treating acid forming tank |
JP3909329B2 (en) * | 2004-02-12 | 2007-04-25 | 住友重機械工業株式会社 | Wastewater treatment equipment |
-
1981
- 1981-03-06 JP JP56031210A patent/JPS5833040B2/en not_active Expired
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS60180427U (en) * | 1984-05-10 | 1985-11-30 | 株式会社 エバ−ス | face steamer |
JPS60182042U (en) * | 1984-05-15 | 1985-12-03 | 株式会社 エバ−ス | face steamer |
JPS60184535U (en) * | 1984-05-18 | 1985-12-07 | 株式会社 エバ−ス | face steamer |
Also Published As
Publication number | Publication date |
---|---|
JPS57147498A (en) | 1982-09-11 |
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