JP2631211B2 - Methane fermentation treatment method - Google Patents

Methane fermentation treatment method

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Publication number
JP2631211B2
JP2631211B2 JP62018865A JP1886587A JP2631211B2 JP 2631211 B2 JP2631211 B2 JP 2631211B2 JP 62018865 A JP62018865 A JP 62018865A JP 1886587 A JP1886587 A JP 1886587A JP 2631211 B2 JP2631211 B2 JP 2631211B2
Authority
JP
Japan
Prior art keywords
methane fermentation
gas
tank
juice
treatment method
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
JP62018865A
Other languages
Japanese (ja)
Other versions
JPS63185499A (en
Inventor
俊則 亀岡
道男 崎元
要一 因野
修平 宮内
重俊 大滝
忠明 森
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.)
MORI PURANTO JUGEN
OOSAKAFU
Takiron Co Ltd
Original Assignee
MORI PURANTO JUGEN
OOSAKAFU
Takiron Co Ltd
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Filing date
Publication date
Application filed by MORI PURANTO JUGEN, OOSAKAFU, Takiron Co Ltd filed Critical MORI PURANTO JUGEN
Priority to JP62018865A priority Critical patent/JP2631211B2/en
Publication of JPS63185499A publication Critical patent/JPS63185499A/en
Application granted granted Critical
Publication of JP2631211B2 publication Critical patent/JP2631211B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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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

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  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】 産業上の利用分野 本発明は、魚粉製造工程その他の水産加工工程で排出
される血汁や煮汁を原料とし、熱量の大きい燃料ガスを
高率で発生させることができる頗る有用なメタン醗酵処
理方法に関する。
DETAILED DESCRIPTION OF THE INVENTION Industrial Field of the Invention The present invention can generate fuel gas having a large calorie at a high rate by using blood juice or boiled juice discharged in a fish meal manufacturing process or other fishery processing processes as a raw material. It relates to a very useful methane fermentation treatment method.

従来の技術とその問題点 従来より、イワシ等の鮮魚や鮮魚商、缶詰業者その他
の加工業者等から回収された魚腸骨の多くは、魚粉製造
工程を経て飼料として利用されている。この魚粉製造工
程においては、血汁や煮汁が多量に排出されるが、これ
らは一般に次のように処理されている。
2. Description of the Related Art Conventional Techniques and Their Problems Conventionally, fresh fish such as sardines and many fish iliac bones recovered from fresh fish merchants, canners and other processors have been used as feeds through a fish meal production process. In this fish meal production process, a large amount of blood juice and boiled juice is discharged, and these are generally treated as follows.

即ち、血汁の場合は、水で希釈して生物分解処理を行
い、水質規制値以下の浄化排水として放流している。一
方、煮汁の場合は、上記の生物分解処理を行って放流す
るか、又は加熱濃縮してフィッシュソルブルとして再利
用を図っている。
That is, in the case of blood juice, it is diluted with water, subjected to biodegradation treatment, and discharged as purified wastewater having a water quality regulation value or less. On the other hand, in the case of boiling juice, the above-mentioned biodegradation treatment is carried out and discharged, or it is heated and concentrated to reuse it as a fish soluble.

しかしながら、かかる方法で血汁や煮汁を処理する場
合は、以下に述べるような種の問題がある。今、煮汁を
例にとって説明すると、この煮汁の性状は一般に、固形
物が約10%(重量%、以下同様)、有機物が約9%、BO
Dが約60000mg/、CODが約11000mg/、全窒素が約1200
0mg/、全炭素が約48000mg/で、炭素率(C/N比)が
4と低いものであるため、生物分解処理を行っても速や
かに分解せず、効率よく処理できないといった問題があ
る。これに対し、加熱濃縮してフィッシュソルブルとす
る場合は、煮汁中の水分量が多く多量の熱エネルギーを
必要とするため、エネルギーコストが高くつくといった
問題があり、特にフィッシュソルブルの価格が低迷して
いる昨今では全く収支がとれなくなっている。それで
も、鮮魚を原料として魚粉を製造している場合は、得ら
れるフィッシュソルブルを魚粉製造途中の乾燥工程に投
入することによって、ホールミールの製造に利用できる
のでまだよいが、鮮度の悪い魚腸骨を原料として魚粉を
製造している場合は、得られるフィッシュソルブルが油
分の酸化等、品質面での問題を有するため、ホールミー
ルの製造に利用することもできず、その処理に頭を痛め
ているのが実情である。
However, when blood or boiled juice is treated by such a method, there are the following kinds of problems. Taking the broth as an example, the properties of the broth are generally about 10% solids (wt%, the same applies hereinafter), about 9% organic matter,
D is about 60000mg /, COD is about 11000mg /, total nitrogen is about 1200
0 mg /, the total carbon is about 48000 mg /, and the carbon ratio (C / N ratio) is as low as 4; On the other hand, when heat-concentrating into a fish-solvable, there is a problem that the amount of water in the broth is large and a large amount of heat energy is required, so that the energy cost is high. In recent years, which has been sluggish, it has become impossible to make a profit or loss at all. Still, when fish meal is produced using fresh fish as a raw material, the obtained fish soluble can be used for the production of whole meal by inputting it into the drying process during the production of fish meal, but it is still good, When fish meal is manufactured using bone as a raw material, the resulting fish solvable has problems in quality, such as oxidation of oil, and cannot be used for the production of whole meal. It is the fact that it is hurt.

このような事情から、煮汁や血汁をメタン醗酵処理す
ることにより、エネルギー資源として回収、利用しよう
とする試みも行われているようである。しかしながら、
煮汁等は前述のように炭素率が低く、また含硫アミノ酸
等も多く含まれているため、機械撹拌型単槽式のメタン
醗酵槽による通常の中温醗酵法では、メタン醗酵菌に悪
影響を及ぼすアンモニアや硫化水素の濃度が経時的に高
くなって正常なメタン醗酵が困難となり、ガス発生量が
著しく低下するといった問題がある。しかも消化液のBO
D値やCOD値が高いため、この消化液の後処理が容易でな
いといった問題もある。
Under such circumstances, attempts have been made to recover and use as an energy resource by subjecting boiled juice and blood juice to methane fermentation. However,
As mentioned above, broth and the like have a low carbon content and contain a large amount of sulfur-containing amino acids, etc., so that ordinary mesophilic fermentation using a mechanically stirred single-tank methane fermentation tank adversely affects methane fermentation bacteria. There is a problem that the concentration of ammonia and hydrogen sulfide increases with time, making normal methane fermentation difficult, and the amount of gas generated is significantly reduced. And BO of digestive juice
Since the D value and COD value are high, there is also a problem that the post-treatment of the digestive juice is not easy.

そこで、本発明者らは、煮汁や血汁からコロイド状の
蛋白質を分離回収することにより、メタン醗酵の処理効
率を向上させると共に、分離回収蛋白質を飼料として有
効利用する一石二鳥の処理システムを着想し、研究を進
めた。けれども、煮汁等からコロイド状蛋白質を分離す
るだけでは、メタン醗酵の改善効果がある程度認められ
るというものの、まだ溶存している含窒素化合物や含硫
化合物からアンモンニアや硫化水素が相当発生するの
で、満足なメタン醗酵を行わせることが難しく、そのた
めメタン醗酵処理そのものを抜本的に改良することが必
要になってきた。
Thus, the present inventors have conceived a system for treating two birds per stone, which improves the processing efficiency of methane fermentation by separating and recovering colloidal proteins from boiled juice and blood juice, and effectively utilizes the separated and recovered proteins as feed. , Advanced the research. However, although the effect of improving methane fermentation is recognized to some extent only by separating colloidal proteins from broth, etc., ammonium nitrate and hydrogen sulfide are considerably generated from the dissolved nitrogen-containing compounds and sulfur-containing compounds. It is difficult to perform methane fermentation, and it has become necessary to drastically improve the methane fermentation process itself.

発明の目的 本発明は上記事情に基づいてなされたもので、これま
で正常にメタン醗酵処理することが困難であった煮汁や
血汁を原料とし、それから熱量の大きいガスを高率で安
定して発生させることができる画期的なメタン醗酵処理
方法を提供せんとするものである。
Object of the Invention The present invention has been made based on the above circumstances, and uses a broth or blood juice as a raw material, which has been difficult to normally perform methane fermentation processing, and then stably supplies a large amount of calorific gas at a high rate. It is an object of the present invention to provide an innovative methane fermentation treatment method that can be generated.

目的を達成するための手段 かかる目的を達成するため、本発明のメタン醗酵処理
方法は、血汁や煮汁をメタン醗酵槽内でメタン醗酵させ
る前に除蛋白処理を行い、この除蛋白処理を行った血汁
や煮汁の液をメタン醗酵槽内でメタン醗酵させる際に、
発生するガスを循環させてメタン醗酵液のガス撹拌を行
うと共に、このガス循環の途中でアンモニアと硫化水素
の除去処理を行う構成としたことを要旨としている。
Means for Achieving the Object In order to achieve the object, the methane fermentation treatment method of the present invention performs a deproteinization treatment before performing methane fermentation of blood juice or broth in a methane fermentation tank. When fermenting blood juice or broth in a methane fermentation tank,
The gist is that the generated gas is circulated to perform gas agitation of the methane fermentation liquid, and that ammonia and hydrogen sulfide are removed during the gas circulation.

発明の作用 本発明のように発生ガスを循環させてメタン醗酵液の
ガス撹拌を行い、ガス循環の途中でアンモニアと硫化水
素の除去処理を行うと、メタン醗酵液中で発生したアン
モニアや硫化水素が撹拌ガスに保有されて循環し、その
循環の途中で除去されるため、メタン醗酵槽内における
有害なアンモニアと硫化水素の濃度は大幅に減少する。
従って、メタン醗酵菌が盛んに活動し、正常なメタン醗
酵が持続して行われるので、高熱量のガスが高率で安定
して発生するようになり、また消化液のBO値やCOD値も
極めて小さくなる。
Effect of the Invention As in the present invention, when the generated gas is circulated and the methane fermentation solution is agitated and ammonia and hydrogen sulfide are removed during gas circulation, the ammonia and hydrogen sulfide generated in the methane fermentation solution are removed. Is circulated in the stirring gas and removed in the course of the circulation, so that the concentration of harmful ammonia and hydrogen sulfide in the methane fermentation tank is greatly reduced.
Therefore, since methane fermentation bacteria are active and normal methane fermentation is continuously performed, high calorific gas comes to be generated stably at a high rate, and the BO value and COD value of digestive juice are also increased. Extremely small.

実施例 以下、実施例を挙げて本発明のメタン醗酵処理方法を
詳細に説明する。
Examples Hereinafter, the methane fermentation treatment method of the present invention will be described in detail with reference to examples.

第1図は本発明の一実施例にかかるメタン醗酵処理の
フローチャート、第2図は本発明に用いるガス循環装置
付きメタン醗酵槽の概略構成図であって、第1図に示す
ように、本発明のメタン醗酵処理方法によれば、まず原
料の血汁や煮汁を水で2倍程度に希釈する。原料として
用いる血汁は、貯蔵ピットや搬送ピットより排出される
液で、魚体からの滲出液、血液、内蔵、肉片等が含まれ
ており、また煮汁は、クッカーから排出される液で、魚
体からの抽出液、血液、内蔵、肉汁成分(蛋白質)、骨
汁成分が含まれている。この煮汁の性状は既述した通り
であり、固形物中の約80%が粗蛋白質である。
FIG. 1 is a flowchart of a methane fermentation process according to one embodiment of the present invention, and FIG. 2 is a schematic configuration diagram of a methane fermentation tank with a gas circulation device used in the present invention. As shown in FIG. According to the methane fermentation treatment method of the present invention, first, blood juice or broth as a raw material is diluted about twice with water. Blood juice used as a raw material is a liquid discharged from storage pits and transport pits, and contains exudate from blood, blood, internal organs, meat pieces, and the like.Boiled juice is a liquid discharged from a cooker and is a fish liquid. Extracts, blood, internal organs, juice components (proteins), and bone juice components. The properties of the broth are as described above, and about 80% of the solid is crude protein.

原料の煮汁等の希釈が終わると、この希釈液に酢酸を
約1容量%添加する。このように酢酸を添加すると、希
釈液中のコロイド状の蛋白質がほぼ等電点におかれた状
態となるため、速やかに凝集する。この実施例では、着
香料として好ましい酢酸を添加して蛋白質を凝集させて
いるが、この他蟻酸等の有機酸や無機酸を添加して凝集
させてもよい。ただし低濃度の原料であれば、数倍に希
釈して直接凝集物を分離してもよい。
When dilution of the raw material such as broth is completed, about 1% by volume of acetic acid is added to the diluted solution. When acetic acid is added in this manner, the colloidal protein in the diluent is in a state of being substantially at the isoelectric point, and thus rapidly aggregates. In this embodiment, acetic acid, which is preferable as a flavoring agent, is added to coagulate proteins. However, other than this, organic acids such as formic acid or inorganic acids may be added to coagulate proteins. However, if the raw material has a low concentration, the aggregate may be directly separated by diluting it several times.

蛋白質が凝集すると、次いで高速遠心分離機にかけて
凝集物を遠心分離する。このように分離回収した凝集物
は、約83%の水分を含んでおり、予乾して水分を約50%
にすればペレット状に加工することができる。そして、
これを乾燥すると、付着している酢酸の大半が揮散して
僅かの酢酸が飼料着香料として残存し、価値ある高蛋白
飼料(粗蛋白質が約80%)が得られる。
Once the protein has aggregated, the aggregate is then centrifuged through a high speed centrifuge. The aggregate separated and recovered in this way contains about 83% of water, and is predried to reduce the water to about 50%.
By doing so, it can be processed into a pellet shape. And
When this is dried, most of the attached acetic acid volatilizes, and a small amount of acetic acid remains as a feed flavoring, and a valuable high protein feed (about 80% crude protein) is obtained.

上記のように除蛋白処理を行うと、メタン醗酵に有害
な含窒素化合物や含硫化合物が約15%程度除去され、そ
の含有量が約6500mg/から約5500mg/に低下するの
で、メタン醗酵の改善効果はある程度認められるように
なるが、既述したように原料液中には溶解性の蛋白質や
含硫アミノ酸等がまだ相当量含まれているため、通常の
機械撹拌型単槽式のメタン醗酵槽に入れて中温醗酵処理
しても、正常にメタン醗酵を行わせることが困難であ
る。
When deproteinization is performed as described above, nitrogen-containing compounds and sulfur-containing compounds that are harmful to methane fermentation are removed by about 15%, and their contents are reduced from about 6500 mg / to about 5500 mg /. Although the improvement effect can be recognized to some extent, as described above, since the raw material liquid still contains a considerable amount of soluble proteins, sulfur-containing amino acids, and the like, the usual mechanical stirring type single tank methane is used. Even if it is put in a fermentation tank and subjected to medium temperature fermentation, it is difficult to perform methane fermentation normally.

そこで、本発明では除蛋白処理した液を可溶化槽に導
入して5日間ほど酸醗酵させてから、第2図に示すよう
なガス循環装置付きのメタン醗酵槽に導入し、20日間ほ
ど中温又は高温醗酵法でメタン醗酵処理を行う。このメ
タン醗酵槽1に取付けられたガス循環装置2は、図示の
ように循環パイプ21の途中に硫酸槽22と酸化鉄充填槽23
を直列に設けたもので、循環パイプ21の両端がメタン醗
酵槽1の上部と底部にそれぞれ接続されている。従っ
て、このメタン醗酵槽1内で発生するガスは、上部から
循環パイプ21を通って硫酸槽22内の硫酸3と接触し、次
いで酸化鉄充填槽23内の酸化鉄4と接触して、メタン醗
酵槽1の底部に戻り、メタン醗酵液5中をバブリングし
てガス撹拌を行いながら循環するようになっている。
Therefore, in the present invention, the solution subjected to the deproteinization treatment is introduced into the solubilization tank and subjected to acid fermentation for about 5 days, and then introduced into the methane fermentation tank equipped with a gas circulation device as shown in FIG. Alternatively, a methane fermentation treatment is performed by a high-temperature fermentation method. A gas circulation device 2 attached to the methane fermentation tank 1 includes a sulfuric acid tank 22 and an iron oxide filling tank 23 in the middle of a circulation pipe 21 as shown in the figure.
Are provided in series, and both ends of a circulation pipe 21 are connected to the top and bottom of the methane fermentation tank 1, respectively. Therefore, the gas generated in the methane fermentation tank 1 contacts the sulfuric acid 3 in the sulfuric acid tank 22 through the circulation pipe 21 from the upper part, and then contacts the iron oxide 4 in the iron oxide filling tank 23 to form methane. Returning to the bottom of the fermenter 1, the methane fermentation liquid 5 is circulated while bubbling and stirring the gas.

このように循環するガスでメタン醗酵液5を撹拌する
と、メタン醗酵液5中で発生した有害なアンモニアや硫
化水素がこの撹拌ガスに保有され、そのまま循環パイプ
21を通って循環し、その途中で硫酸槽22内の硫酸3と接
触してアンモニアが硫酸アンモニウムとして除去され、
更に酸化鉄充填槽23内の酸化鉄4と接触して硫化水素が
硫化鉄として除去される。そのため、このガス循環が繰
り返されると、アンモニアと硫化水素の濃度が大幅に減
少し、メタン醗酵液5中のアンモニア量は約2700mg/
でほぼ一定し、循環ガス中の硫化水素は約78ppmまで低
下する。従って、メタン醗酵菌が盛んに活動し、正常な
メタン醗酵が持続して行われるため、高熱量のガスが約
0.63/g(約63%の分解率)の高率で安定して発生する
ようになる。
When the methane fermentation liquid 5 is stirred with the gas circulating in this way, harmful ammonia and hydrogen sulfide generated in the methane fermentation liquid 5 are retained in the stirring gas, and the circulating pipe
Circulates through 21 and, on the way, comes in contact with sulfuric acid 3 in sulfuric acid tank 22 to remove ammonia as ammonium sulfate,
Further, the hydrogen sulfide is removed as iron sulfide by contacting the iron oxide 4 in the iron oxide filling tank 23. Therefore, when this gas circulation is repeated, the concentration of ammonia and hydrogen sulfide is greatly reduced, and the amount of ammonia in the methane fermentation liquor 5 is about 2700 mg /
And hydrogen sulfide in the circulating gas drops to about 78 ppm. Therefore, since methane fermentation bacteria are active and normal methane fermentation is continuously performed, high calorific gas is consumed.
It is generated stably at a high rate of 0.63 / g (about 63% decomposition rate).

なお、この実施例では、ガス循環装置2として前述の
ごとき循環パイプ21の途中に硫酸槽22と酸化鉄充填槽23
を設けたものを使用し、アンモニアと硫化水素を個別に
除去しているが、これに代えて硫酸鉄を充填した槽を一
つだけ設けたガス循環装置を使用し、アンモニアと硫化
水素を同時に除去するようにしてもよい。また、場合に
よっては、アンモニアと硫化水素を除去したガスをメタ
ン醗酵槽に直接戻さないで、その一部又は全部を可溶化
槽を経てメタン醗酵槽に戻すようにしてもよい。
In this embodiment, the sulfuric acid tank 22 and the iron oxide filling tank 23 are provided in the middle of the circulation pipe 21 as described above as the gas circulation device 2.
Ammonia and hydrogen sulfide are removed separately, but instead of this, a gas circulation device equipped with only one tank filled with iron sulfate is used to simultaneously remove ammonia and hydrogen sulfide. It may be removed. In some cases, the gas from which ammonia and hydrogen sulfide have been removed may not be directly returned to the methane fermentation tank, but may be partially or entirely returned to the methane fermentation tank via the solubilization tank.

以上のようにして得られる消化ガスは、メタン70%、
炭酸ガス29%、その他1%の組成を有しており、熱量が
約6000Kcal/N・m3と大きいので、直接燃料として、或い
は電気に変換して、魚粉製造その他の代替エネルギーと
して充分使用することができる。
The digestion gas obtained as above is 70% methane,
Carbon dioxide 29%, has other 1% of the composition, since the amount of heat is large as about 6000Kcal / N · m 3, as direct fuel, or converted to electricity sufficiently used as a fishmeal production other alternative energy be able to.

一方、消化液は、BODが約4000mg/以下で、メタン醗
酵によるBOD除去率が約90%以上と高率であり、また、C
ODは約2000mg/以下になっている。従って、この消化
液は、水で希釈して通常の活性汚泥法等で容易に浄化処
理することができるので、浄化処理により水質規制値以
下の排水として放流すればよい。また、場合によって
は、消化液温度が約35℃と比較的高いことを利用して、
送風式の蒸散処理を行うようにしてもよい。
On the other hand, the digestive juice has a high BOD removal rate of about 90% or more, with a BOD of about 4000 mg /
The OD is less than about 2000 mg /. Therefore, this digested liquid can be diluted with water and easily purified by the ordinary activated sludge method or the like. In some cases, taking advantage of the relatively high digestive fluid temperature of about 35 ° C,
You may make it perform the ventilation-type evaporation process.

参考までに、一日60tの煮汁を本発明方法でメタン醗
酵処理すると共に、回収蛋白質を飼料化する場合の一年
間の収支を計算すると、次のように43,400千円/年のプ
ラスとなり、従って従来の加熱濃縮に要していた経費3
5,000千円/年を勘案すれば、年間78,400千円の差益が
生まれることになる。
For reference, when 60 tons of broth a day is subjected to methane fermentation treatment by the method of the present invention and the recovered protein is converted into feed, the one-year balance is calculated to be 43,400,000 yen / year as follows. Expenses required for conventional heat concentration 3
Considering 55,000 yen / year, a profit of 78,400,000 yen per year will be generated.

支出 酢酸 44,000千円/年 ランニングコスト 22,600千円/年 収入 回収蛋白飼料 44,000千円/年 代替えエネルギー 65,000千円/年 差引 43,400千円/年 発明の効果 以上の説明から明らかなように、本発明のメタン醗酵
処理方法によれば、従来正常にメタン醗酵処理すること
が困難であった煮汁や血汁を原料とし、それから熱量の
大きいガスを高率で安定して発生させることができ、ま
た分離回収した蛋白質も高品質の飼料とすることができ
るといった顕著な効果が得られる。従って、本発明は水
産加工業界とりわけ魚粉製造業界に多大の利益を与える
有用な発明であり、公害防止の面でも優れた発明であ
る。
Expenditure acetate 44,000 yen / year running costs 22,600 yen / year revenue collected protein feed 44,000 yen / year alternative energy 65,000 yen / year subtraction 43,400 As is clear from the effects above description of thousand yen / year invention, the present invention According to the methane fermentation treatment method, boiled juice and blood juice, which were conventionally difficult to perform methane fermentation normally, can be used as a raw material, and then a large amount of calorific gas can be generated stably at a high rate. A remarkable effect is obtained such that the recovered protein can also be used as a high-quality feed. Therefore, the present invention is a useful invention which gives a great benefit to the marine processing industry, especially the fishmeal manufacturing industry, and is also an invention excellent in terms of pollution control.

【図面の簡単な説明】[Brief description of the drawings]

第1図は本発明の一実施例にかかるメタン醗酵処理のフ
ローチャート、第2図は本発明に用いるガス循環装置付
きメタン醗酵槽の概略構成図である。 1……メタン醗酵槽、2……ガス循環装置、21……循環
パイプ、22……硫酸槽、23……酸化鉄充填槽、3……硫
酸、4……酸化鉄、5……メタン醗酵液。
FIG. 1 is a flowchart of a methane fermentation process according to one embodiment of the present invention, and FIG. 2 is a schematic configuration diagram of a methane fermentation tank with a gas circulation device used in the present invention. 1 ... methane fermentation tank, 2 ... gas circulation device, 21 ... circulation pipe, 22 ... sulfuric acid tank, 23 ... iron oxide filling tank, 3 ... sulfuric acid, 4 ... iron oxide, 5 ... methane fermentation liquid.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 崎元 道男 羽曳野市尺度442 大阪府農林技術セン ター公舎6号 (72)発明者 因野 要一 羽曳野市高鷲4丁目2番地 春日丘団地 25号棟406号 (72)発明者 宮内 修平 泉佐野市長滝3248の1 (72)発明者 大滝 重俊 大阪市東区安土町2丁目30番地 タキロ ン株式会社内 (72)発明者 森 忠明 大阪市西区立売堀6丁目6番18号 橘ビ ル 有限会社モリプラント内 (56)参考文献 特開 昭58−74192(JP,A) 特開 昭53−62353(JP,A) 特開 昭58−150496(JP,A) 実開 昭60−24396 (JP,U) 特公 昭43−4708(JP,B1) 特公 昭56−42995(JP,B2) ──────────────────────────────────────────────────続 き Continued on the front page (72) Inventor Michio Sakimoto Habikino City Scale 442 Osaka Prefectural Agriculture and Forestry Technology Center Public Building No. 6 (72) Inventor Kazuichi Inno 4-2-2 Takasugi, Habikino City Kasugaoka Danchi No. 25, Building 406 (72) Inventor Shuhei Miyauchi 3248-1 Nagataki, Izumisano-shi (72) Inventor Shigetoshi Otaki 2-30, Azuchi-cho, Higashi-ku, Osaka Within TAKIRON Co., Ltd. (72) Inventor Tadaaki Mori 6-6-1, Nori-ku, Nishi-ku, Osaka No. Tachibana Building Inside Mori Plant Co., Ltd. (56) References JP-A-58-74192 (JP, A) JP-A-53-62353 (JP, A) JP-A-58-150496 (JP, A) 60-24396 (JP, U) JP-B 43-4708 (JP, B1) JP-B 56-42995 (JP, B2)

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】水産加工工程で排出される血汁や煮汁をメ
タン醗酵槽内でメタン醗酵させる前に除蛋白処理を行
い、この除蛋白処理を行った血汁や煮汁の液をメタン醗
酵槽内でメタン醗酵させる際に、発生するガスを循環さ
せてメタン醗酵液のガス攪拌を行うと共に、このガス循
環の途中でアンモニアと硫化水素の除去処理を行うこと
を特徴とするメタン醗酵処理方法。
1. A deproteinization treatment is performed on blood juice or broth discharged in a fishery processing step before methane fermentation in a methane fermentation tank. A methane fermentation treatment method comprising: circulating the generated gas when performing methane fermentation in the methane fermentation solution, stirring the gas in the methane fermentation solution, and removing ammonia and hydrogen sulfide during the gas circulation.
JP62018865A 1987-01-28 1987-01-28 Methane fermentation treatment method Expired - Lifetime JP2631211B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP62018865A JP2631211B2 (en) 1987-01-28 1987-01-28 Methane fermentation treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP62018865A JP2631211B2 (en) 1987-01-28 1987-01-28 Methane fermentation treatment method

Publications (2)

Publication Number Publication Date
JPS63185499A JPS63185499A (en) 1988-08-01
JP2631211B2 true JP2631211B2 (en) 1997-07-16

Family

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Country Link
JP (1) JP2631211B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101906356B1 (en) * 2016-06-21 2018-10-10 경기대학교 산학협력단 Anaerobic digestion apparatus and method for treating organic waste by gas recirculation

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JP4367876B2 (en) * 2000-03-31 2009-11-18 アタカ大機株式会社 Waste treatment method and apparatus
JP4641854B2 (en) * 2005-04-15 2011-03-02 鹿島建設株式会社 Method and apparatus for methane fermentation treatment with reduced ammonia inhibition
KR100936540B1 (en) * 2009-02-16 2010-01-13 이상범 Apart-shaped anaerobic digester for producing biogas
JP2010269223A (en) * 2009-05-19 2010-12-02 Hitachi Engineering & Services Co Ltd Method and apparatus for treating organic waste
JP2014180630A (en) * 2013-03-19 2014-09-29 Tokyo Gas Co Ltd Method of and device for treating organic waste

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5362353A (en) * 1976-11-16 1978-06-03 Kurita Water Ind Ltd Method for treating coagulated sludge containing protein
JPS5642995A (en) * 1979-09-14 1981-04-21 Matsushita Electric Works Ltd Transistor inverter type discharge lamp starter
JPS5874192A (en) * 1981-10-27 1983-05-04 Ooshinotsu Shokuhin Kogyo Kk Treatment for waste of processed marine products
JPS6024396U (en) * 1983-07-27 1985-02-19 株式会社明電舎 Methane fermentation equipment

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101906356B1 (en) * 2016-06-21 2018-10-10 경기대학교 산학협력단 Anaerobic digestion apparatus and method for treating organic waste by gas recirculation

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