JP2002154887A - Treatment of raw material to be supplied to gaseous methane generator and compost manufacturing method - Google Patents

Treatment of raw material to be supplied to gaseous methane generator and compost manufacturing method

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Publication number
JP2002154887A
JP2002154887A JP2000381090A JP2000381090A JP2002154887A JP 2002154887 A JP2002154887 A JP 2002154887A JP 2000381090 A JP2000381090 A JP 2000381090A JP 2000381090 A JP2000381090 A JP 2000381090A JP 2002154887 A JP2002154887 A JP 2002154887A
Authority
JP
Japan
Prior art keywords
raw material
fermentation
methane gas
aerobic fermentation
residue
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
JP2000381090A
Other languages
Japanese (ja)
Inventor
Yaichi Obara
弥一 小原
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP2000381090A priority Critical patent/JP2002154887A/en
Publication of JP2002154887A publication Critical patent/JP2002154887A/en
Pending 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • 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
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)
  • Fertilizers (AREA)

Abstract

PROBLEM TO BE SOLVED: To achieve the normalization of resource recovery and nitrogen circulation and the vigor intensification of soil by subjecting incessantly increasing industrial waste resources of food processing residues, livestock waste resources, and the like, to aerobic fermentation treatment, supplying these resources to an anaerobic fermentation equipment, efficiently collecting gaseous methane and subjecting the residues to activated composting. SOLUTION: Many and diversified food processing residue-like resources containing much of silicic acid like low-temperature crushed chaff containing many matured vegetable fibers, bean curd lees, waste mushroom medium sawdust and beer lees are subjected to the aerobic fermentation treatment using 'Eocommit (R)' as a fermentation initiator, by which the silicic acid is activated and the product (A) propagated with useful microorganism groups is obtained. A 'Marinext (R)' extractant is added and mixed to and with the livestock wastes, wastes of fish and meat, or the like, using the product (A) as a base material to obtain the methane fermented raw materials having high nitrogen convertibility through the maturation of aerobic fermentation, in combination with which a dilute liquid of 'Eocommit (R)' is added to livestock urine and the urine is subjected to anaerobic treatment and the urine is supplied together with the raw materials to a methane fermentation equipment to obtain the gaseous methane. The integral treating and manufacturing method finishes the residue after the gas collection to the compost to enhance the vigor of soil by dehydrating the residue, adding plural organic materials thereto and again subjecting the materials to aerobic fermentation.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【発明の属する技術分野】本発明は植物、動物有機質資
源や、畜産廃棄物資源を、再生循環の為の好気発酵操作
を経て、メタンガス発生装置に供給する原料化し、メタ
ンガスを効率よく採集し更に残渣を堆肥化しようとする
技術に関するものである。
The present invention relates to a method for efficiently collecting methane gas by converting plant, animal organic resources and livestock waste resources into raw materials to be supplied to a methane gas generator through an aerobic fermentation operation for recycling. Further, the present invention relates to a technique for composting residues.

【従来技術】生活や産業活動の結果生み出される副生物
である廃棄物は増大し環境に負荷を与えている。しかし
それを資源化し、再生する為嫌気発酵によってメタンガ
ス化して活用する試みはその可能性が極めて高いことか
ら競って開発提案の増加が著しい。しかし多くは化学的
粋を極めて大型化の傾向を示しており、その原料資源の
発生の多い地域で即応出来る小型で多数か所が利用出来
る装置方法が少なく、更にその残渣を有効な状態の堆肥
化して耕地に還元するまでの一貫した資源再生循環技術
が少なくその出現が求められている。
2. Description of the Related Art Waste products, which are by-products produced as a result of living and industrial activities, are increasing and imposing loads on the environment. However, attempts to convert methane gas into methane gas by anaerobic fermentation to recycle and recycle it are extremely likely, and competition has been extremely high, and the number of development proposals has increased significantly. However, in many cases, the chemical trend is extremely large, and there are few small and many equipment methods that can be used immediately in the area where the raw material resources are generated. There is little integrated resource recycling technology until it is transformed into cultivated land and its appearance is required.

【発明が解決しようとする課題】地球上の物質循環にあ
って好気的発酵と嫌気的発酵は双璧的発酵系である。そ
の嫌気的発酵の代名詞的に云われる有機物分解の結果生
成物のうち利用価値のあるのがメタンガスである。最近
環境保全や物質循環、エネルギー対策等人の生存の根幹
に関わる功罪両面の立場から、産廃的資源再生循環の課
題解決手段としてメタンガスの生成と利用にかかる科学
的枠を極めた技術が提案されている。本発明者も課題を
しぼり込むべく発酵に関わる基本的要因を考察した。即
ち好気か嫌気に関わらず発酵は酵素微生物の法則的反応
である。又、物質循環の多くは植物の生合成反応の頂上
としての成熟があり、それを越えて土に還る道程があ
る。いづれも酵素微生物の法則的生化学的反応が機能し
なければ成り立たないことは云うまでもなく、云いかえ
ると、本案の求める効率的メタンガス発生の反応事象は
供給する原料の質と、処理する施設装置並に微生物環境
との相乗反応によることがわかった。本案はそのメタン
ガス発生装置に供給する原料が如何にあれば効率よくメ
タンガスが得られるか、更に残渣を耕地に有効な活力の
ある堆肥化する資源再生循環技術が如何にあるべきか、
段階的な処理体系を提案する。
Aerobic fermentation and anaerobic fermentation are two perfect fermentation systems in the material cycle on the earth. Methane gas is a useful product among the products of the decomposition of organic matter, synonymous with the anaerobic fermentation. Recently, from the standpoints of both the merits and demerits related to the fundamentals of human survival, such as environmental protection, material circulation, and energy measures, technology that maximizes the scientific framework for the generation and use of methane gas has been proposed as a means of solving the problem of recycling industrial waste resources. ing. The present inventor also considered basic factors related to fermentation in order to narrow down the problem. That is, fermentation, whether aerobic or anaerobic, is a lawful reaction of enzymatic microorganisms. Most of the material cycle has a maturation as the top of the biosynthetic reaction of the plant, and there is a way to return to the soil beyond it. It goes without saying that unless the law-based biochemical reaction of the enzyme microorganisms functions, it will not be feasible. In other words, the reaction event for efficient methane gas generation required by the present invention depends on the quality of the raw materials supplied and the facilities to be treated. It was found to be due to a synergistic reaction with the microbial environment as well as the device. The idea of this proposal is to find out how much methane gas can be obtained efficiently if there is a raw material to be supplied to the methane gas generator, and how there should be a resource recycling technology to make the residue into effective and compostable arable land.
We propose a stepwise processing system.

【課題を解決する為の手段及び作用】発明者は平成2年
の出願特許第3044326号を土台に資源再生技術と
して平成8年に特願平8−144810号を出願した。
それを改良して出願した特願2000−301228号
の資源再生循環−バイオ活性有機肥料の製造法に基く実
施例記載の方法で作られた有機肥料をベースにした複数
の圃場栽培(5ha)を試みて、確実な再現性を信じ得
る事象に巡り合った。即ち先願技術は産廃資源的な食品
加工残渣を特定酵素を発酵起剤にして好気発酵処理し、
有用微生物群が増殖して対象物材が改質されたもの(ミ
ネラルが生成)に複数種の有機質資材を加えて重複発酵
させ有機肥料化したもので、典型的な好気発酵技術の結
果生成物である。水田に施用すると光合成菌叢(車軸
藻)の発現が顕著で、畑に施用すると大豆の根溜菌の着
生が顕著である。発明者が10余年前以来低温破砕モミ
ガラを基材としたいわゆるボカシ肥技法であるが、本年
特定酵素(エオコミツト)を用いた方法によったものは
上記事象に加えて、水田に於ける藻の下の耕土で典型的
な嫌気発酵が極限的に発象したのである。その嫌気発酵
事象が作土全体に及ぶ事象がメタンガス発生メカニズム
に通ずる途と軌を一にしている発見でもあったのであ
る。発酵起剤エオコミツトについては表2にその特性説
明書を示すのでここでは説明を畧す。又本願で新たに使
用する特殊腐植物質は、構造式上不飽和で塩基置換能が
あり、更に界面活性力と有機質のキレート効果機能を持
って発酵分解を助けるので、原料に食物連鎖による重金
属集積のおそれある魚等の廃棄物を利用し得たのであ
る、他の原料の説明も先願に詳しいので畧す。本願手段
の出発(請求項1)は先願と同じであるが後続手段は畜
糞や生ゴミの割合を高め好気発酵を経て原料化し、完全
な嫌気条件のもとで嫌気発酵を極度に追求してガスを採
取し、残渣も有効な活性力の強い肥料化を図る技法とな
る。本願の次元の狙いは好気発酵は有機質素材を分解
減量するが嫌気発酵は有機質素材を減量し得ないと云わ
れることと、発酵起剤に用いたエオコミツトが前述の
複多数の圃場で確認された好気発酵生成物が、嫌気条件
のもとでは嫌気発酵を強力に幇助すると共に、併せて
発酵結果として重金属を減少させる性能があるとの特性
情報があることと、好気発酵段階で窒素イオンリンサ
ンイオンを増加させる特性情報があることをふまえ直
接肥料化目的では危険を伴う窒素移行性材料素材の配合
を多くすることによって、初段階目の珪酸活性化機能
が強化された結果として有機質のキレート効果分解によ
ってメタンガス発生が効率よく行われるものである。更
にメタンガス採取後の結果としての出来る残渣である腐
植に近い物材は更に好気発酵処理を経て、窒素等含有量
の少い優良な土壌改良機能をもつ堆肥として安心して圃
場に還元出来ることとなる。総括的にまとめると、成熟
した植物を食品加工した残渣的資源と特定した酵素剤
(エオコミツト)とのめぐり合いにスタートした段階的
好気性発酵操作を経て作られた有機肥料はミネラルを含
有して有機質キレート効果を発現し環境浄化と云われる
現象を具現する。一方有機肥料としては窒素過剰となる
資材割合を高めた本案の発酵生成物はメタンガス発生装
置の原料として供給し、効率的嫌気性発酵によりメタン
ガスを発生する。結果として食品残渣資源の再生循環利
用を大きく進展させ、窒素循環系におけるアンバランス
の解消にも大きく貢献し、残渣有機物は再度活性度を高
める資材を加えた好気発酵によって優良な土の活力を高
める堆肥に仕上げる。以上の様に本願で用いる資源、資
材を原料とする好気発酵操作による結果生成物は有機質
のキレート効果が発象する特徴をふまえ、窒素移行資源
を多く配合して好気発酵させた成果物を、典型的嫌気発
酵であるメタンガス発生装置に原料として提供し、効率
的にメタンガスを採集利用すると共に、残渣を再度好気
発酵によって土壌の浄化力を付価して土に還元すると云
う、典型的な好気と嫌気の両発酵系を併用した資源再生
循環システムの完結となる。本発明の基礎となった先願
平成2年9月13日出願(特許第3044326号)成
熟植物資源からの土壌活性化剤の製造法による生成物を
分析したクロマトチャート図を表1に示す(多様なアミ
ノ酸が生成されミネラル化している)又、上記本願技法
を大きく前進させた発酵起剤のエオコミツトの特性説明
文を表2に示して参考に供する。
Means and Action for Solving the Problems The inventor of the present invention applied for Japanese Patent Application No. Hei 8-144810 in 1996 as a resource recycling technology based on Japanese Patent Application No. 3044432/1990.
A plurality of field cultivations (5ha) based on the organic fertilizer produced by the method described in the examples based on the resource recycling and the production method of the bioactive organic fertilizer of Japanese Patent Application No. 2000-301228 filed by improving the method are disclosed. I tried and came across an event where I could believe reliable reproducibility. That is, the prior application technology aerobic fermentation treatment of food processing residues as industrial waste resources using specific enzymes as fermentation initiators,
An organic fertilizer made by adding multiple types of organic materials to an organic fertilizer by adding multiple types of organic materials to a material in which useful microorganisms have grown and the target material has been modified (minerals have been produced). Things. When applied to a paddy field, the expression of photosynthetic flora (axle algae) is remarkable, and when applied to a field, the formation of soybean root bacteria is remarkable. The inventor has been using so-called “bokashi manure” technology based on low-temperature crushed hulls for more than 10 years ago. This year, the method using a specific enzyme (Eokomitsuto), in addition to the above-mentioned events, added algae in paddy fields. The typical anaerobic fermentation in the arable soil under the extremes has emerged. It was also a discovery that the anaerobic fermentation event that affected the entire soil was in line with the methane gas generation mechanism. Table 2 shows a description of the characteristics of the fermentation initiator eocommitt. In addition, the special humic substances newly used in the present application are unsaturated in structural formula, have base substitution ability, and furthermore, have a surfactant activity and an organic chelating effect function to assist fermentation decomposition, so that heavy metal accumulation by the food chain in the raw material The explanation of other raw materials, which could use fish and other wastes that could cause harm, is also detailed in the earlier application. The departure of the means of the present application (claim 1) is the same as the prior application, but the subsequent means increases the ratio of animal dung and garbage and turns it into a raw material through aerobic fermentation, and pursues anaerobic fermentation extremely under completely anaerobic conditions. Gas is collected, and the residue is also a technique that can be turned into an effective and highly active fertilizer. The aim of the dimension of the present application is that aerobic fermentation is said to decompose and reduce the amount of organic material, but anaerobic fermentation cannot reduce the amount of organic material, and that eocommit used as a fermentation initiator was confirmed in the aforementioned multiple fields. The aerobic fermentation product strongly assists anaerobic fermentation under anaerobic conditions, and at the same time, has characteristic information that it has the ability to reduce heavy metals as a result of fermentation. In view of the fact that there is characteristic information to increase the ion phosphorus san ion, by increasing the compounding of dangerous nitrogen-transporting materials for the purpose of direct fertilizer, the initial stage Methane gas is generated efficiently by chelating effect decomposition. In addition, materials similar to humus, which is a residue generated as a result of methane gas collection, can be further aerobic fermented and returned to the field as a compost with a good soil improvement function with a low nitrogen content. Become. To sum up, organic fertilizers made through a staged aerobic fermentation operation that started with a concoction between a residual resource obtained by processing a mature plant and a specified enzymatic agent (eocomit) contain minerals. It manifests the organic chelating effect and realizes a phenomenon called environmental purification. On the other hand, as an organic fertilizer, the fermentation product of the present invention, in which the proportion of material that causes nitrogen excess is increased, is supplied as a raw material for a methane gas generator, and methane gas is generated by efficient anaerobic fermentation. As a result, the recycling and recycling of food residue resources has been greatly advanced, and it has also greatly contributed to eliminating imbalances in the nitrogen circulation system. Finish with a compost that increases. As described above, the product obtained by the aerobic fermentation operation using the resources and materials used in the present application as a raw material is a product obtained by aerobically fermenting a mixture of a large amount of nitrogen transfer resources, based on the characteristic that an organic chelating effect appears. Is supplied as a raw material to a methane gas generator, which is a typical anaerobic fermentation, and methane gas is efficiently collected and used, and the residue is returned to the soil by aerobic fermentation by adding the purification power of the soil again. A resource recycling system using both aerobic and anaerobic fermentation systems is completed. Table 1 shows a chromatographic chart in which a product obtained by a method for producing a soil activator from a mature plant resource, which was based on the prior application, which was filed on September 13, 1990 (Patent No. 30444326), was based on the present invention ( Various amino acids are produced and mineralized.) In addition, Table 2 shows the description of the characteristics of Ecomit, a fermentation initiator which has greatly advanced the technique of the present invention.

【実施例】以下段階的順を追って実施例について詳述す
る。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The embodiments will be described in detail below step by step.

【実施例1】原料の基礎となる基材の造り方を示す。ま
ず発酵起剤エオコミツトを準備する。1缶400gを2
0リットルの水に溶解し室温で数日熟成し使用時更に1
0倍に稀釋して200リットルを得る。モミガラ200
リットルを低温破砕して得た130リットルに、豆腐粕
100リットルと、キノコ廃オガ(ブナシメジ−岩手県
矢巾町)50リットル、ビール粕(サッポロ仙台工場)
50リットルに酵素剤(商品名エオコミツト−オースト
リア産、輸入元ユニコ(株)東京都)熟成稀釋200倍
液5リットルで水分を50%以下に調整して充分混合し
5〜10日望ましくは7日以上好気的発酵をさせて有用
微生物群が生
Example 1 A method of manufacturing a base material as a basis of a raw material will be described. First, prepare a fermentation initiator Eocomit. 400g per can 2
Dissolve in 0 liter of water, aged for several days at room temperature
Dilute 0 times to get 200 liters. Fir 200
130 liters obtained by crushing liters at low temperature, 100 liters of tofu lees, 50 liters of mushroom waste ogre (Bunashimeji-Yahaba-cho, Iwate Prefecture), beer lees (Sapporo Sendai Plant)
50 liters of enzyme preparation (trade name Eocomit-Austria, importer Unico Co., Ltd., Tokyo, Japan) 5 liters of 200-fold diluted solution, adjust the water content to 50% or less and mix well, 5 to 10 days, preferably 7 days Above-mentioned aerobic fermentation produces useful microorganisms

【表1】 [Table 1]

【表2】 成されて白い菌子が見られる発酵生成物(A)250リ
ットルを得た。
[Table 2] 250 liters of a fermented product (A) which was formed and showed white mycelia was obtained.

【実施例2】(A)材を畜舎敷料として使用するに当っ
て、特殊腐植物質−商品名マリネックス抽出液(エスシ
ーアクト(株))1000倍液をA材100リットル当
り2リットルを撒布し、家畜体が汚れる前に取出し、厩
肥1m当りエオコミツト200倍液を5リットル撒布
して堆積し、撹拌しながら15日以上65℃以下の温度
帯で、強制通風を含む好気発酵を経る熟成により原料A
−1を得た。
Example 2 In using the material (A) as a livestock litter, 2 liters per 100 liters of A material was sprayed with a 1000-fold solution of a special humic substance-trade name Marinex extract (SC Act Co., Ltd.). , taken out before the livestock body soiling and deposited 5 l spraying manure 1 m 3 per Eokomitsuto 200 times solution, with stirring at 15 days or more 65 ° C. below the temperature zone, through the aerobic fermentation comprising forced draft ripening Raw material A
-1 was obtained.

【実施例3】木炭細粉体(岩手県山形村谷地林産
(株))10kgにマリネックス1000倍液を2リッ
トルを混合10日間熟成したものと、豆腐粕、と破砕
モミガラとビール粕を3等量を原料として発酵処理した
(A)材40kgを混合して得た飼料補完材(D)を豚
又は鶏の飼料に10%混合して与える。その敷料にA材
を用いて畜体に汚れが出始める前に取出し、厩肥1m
当りエオコミツト200倍液を5リットル撒布し撹拌し
ながら15日以上、65℃以下の温度下帯で強制送風を
含む好気発酵を経る熟成により原料A−2を得た。
Example 3 A mixture of 10 kg of charcoal fine powder (Yamagata Murayachi, Iwate Co., Ltd.) and 2 liters of a 1000-fold solution of Marinex was aged for 10 days, and tofu cake, crushed green husk and beer cake were mixed in 3 kg. A feed supplement material (D) obtained by mixing 40 kg of the fermented (A) material with an equal amount as a raw material is mixed with 10% of pig or chicken feed and given. Use material A for the litter, take it out before the body begins to get dirty, remove 1m 3 of manure
The raw material A-2 was obtained by spraying 5 liters of a 200-fold solution of Ecomit, and aging through aerobic fermentation including forced air blowing at a temperature of 65 ° C. or lower for 15 days or more while stirring.

【実施例4】(A)材600リットルに肥育牛厩肥40
0リットルを加え、マリネックス抽出液1000倍液を
10リットル撒布し、練り混合し、撹拌しながら15日
以上、65℃以下の温度帯で、強制送風を含む好気発酵
を経る熟成により原料A−3を得た。
Example 4 (A) 600 liters of beef manure 40
0 liter was added, 10 liters of a 1000 times solution of Marinex extract was dispersed, kneaded and mixed, and the raw material A was ripened through aerobic fermentation including forced blast at a temperature range of not less than 65 days and not more than 15 days while stirring. -3 was obtained.

【実施例5】(A)材700リットルに魚のアラや肉ク
ズや家庭生ゴミ300リットルを細かく砕いて加え、マ
リネックス1000倍液を10リットル撒布して練り混
合し、撹拌しながら15日以上、65℃以下の温度帯で
強制送風を含む好気発酵を経る熟成により原料A−4を
得た。
Example 5 (A) To 300 liters of wood, 300 liters of fish arare, meat waste and household garbage are finely ground and added, and 10 liters of a 1000-fold solution of Marinex are dispersed, kneaded and mixed, and stirred for 15 days or more. The raw material A-4 was obtained by aging through aerobic fermentation including forced air blowing at a temperature zone of 65 ° C. or lower.

【実施例6】先各例によってつくられた原料と畜尿10
00リットル当りエオコミツト200倍液20リットル
を加えて爆気処理してアンモニア臭が軽減された尿とを
併せて、連続式温度保持桟構のメタンガス発生装置に供
給し、発酵終了槽から排出される残渣を脱水し、水分過
剰のものには破砕モミガラで水分を調整し、残渣100
0リットル当り貝化石20kg、米糠25kg、オキア
ミ10kg、マドラグアノ20kgを加え、エオコミツ
ト200倍液を10リットル撒布して練り混合し、撹拌
し乍ら15日以上65℃以下の温度帯で通制通風を含む
好気発酵を経る熟成により活性堆肥を得た。以上原料に
応じたモデル的原料処理、そしてメタン発酵後の残渣を
活性堆肥化する製造法を示した。小規模であれば複数の
原料を混合して処理することは当然可能であるが、再掲
すれば実施例1の手法によって複数の植物繊維的資源を
エオコミツト剤200倍液で発酵させる基礎菌相資材
化、詳しくは珪酸質が活性化してミネラルが生成され、
次段階の処理にその活力が継続し有機質のキレート効果
を発現したものと思料される。複段階の好気発酵による
菌相の進化に伴って有機質の分解と改質が進んだ原料は
強い嫌気条件下にも対応して大きく改質をとげてメタン
ガスを発生し、残渣は活性化好気発酵処理によってほぼ
腐植に近づいた堆肥になり、又エオコミツトとマリネッ
クスの相乗作用によって有害物質が環境負荷水準以下に
低下したものと充分期待される。
Example 6 Raw material and animal urine 10 produced by the above examples
20 liters of a 200-fold solution of Ecommitt per 100 liters is added to the methane gas generator of the continuous temperature-maintaining berth together with the urine whose ammonia smell has been reduced by explosive treatment and expelled from the fermentation termination tank. The residue was dehydrated, and water was adjusted for excess water with crushed peaches.
20 kg of shell fossils, 25 kg of rice bran, 10 kg of krill and 20 kg of madraguano are added per 0 liter, and 10 liters of a 200-fold solution of eocomit are dispersed and kneaded and mixed. Activated compost was obtained by aging through aerobic fermentation. As mentioned above, the model raw material treatment according to the raw material and the production method of turning the residue after methane fermentation into active compost have been described. If it is a small scale, it is naturally possible to mix and process a plurality of raw materials, but if it is re-listed, the basic bacterial flora material fermenting a plurality of plant fiber resources with a 200-fold solution of the eocommitant according to the method of Example 1. , Specifically, the siliceous substance is activated to generate minerals,
It is considered that the vitality continued in the next-stage treatment and an organic chelating effect was exhibited. Raw materials that have undergone decomposition and reforming of organic matter along with the evolution of the microflora by multi-stage aerobic fermentation undergo large reforming in response to strong anaerobic conditions and generate methane gas, and the residue is activated. It is expected that the compost becomes almost humus due to the gas fermentation treatment, and that the harmful substances are reduced to below the environmental load level by the synergistic action of Eocomit and Marinex.

【発明の効果】低温破砕したモミガラが、成熟した植物
資源素材のもどり分解−即ち土に還る法則的分解系に大
きな先導役をもつことに気づいてから10余年の試行の
時が流れた。その技術思想に基くと巷にあふれる有機物
資源の大方は貴重な資源として循環系に参画出来る素質
をもつ。本願がエコシステムサイクルの完成に一歩近づ
いたとすれば、自然が現代に遺してくれた資源の資質に
目を向けざるを得なかった、それ等を必要とする世相の
お陰である。物質循環における好気発酵、嫌気発酵それ
ぞれの範疇は広くそれに対応すると称する資材は数多
い。しかし自然界における反応は言葉で云う程別々のも
のでないことを本案に至る事象が教えてくれたことの意
義は大きい。即ち物質循環において好気発酵は物材の量
を減らしながらその質を大きく変えるが、嫌気発酵は物
材の量を大きく減らさず、その質を徹底して大きく変え
る事象は明確で、消化と云う言葉通りである。本案に至
る植物繊維を多く含有する大量素材を主体とする複数を
組合せ特定の発酵起剤酵素を加えて発酵させると、その
中の珪酸が活性化してミネラルが生成され、2次、3次
で動物質も加わる発酵で蛋白体の分解に伴う異臭が極め
て少く、健全な土における反応に近い。本案に基く原料
化処理をなされた好気発酵生成物が、厳格な嫌気状態に
おかれるとその環境に順応して極限的嫌気発酵をする。
(前記述の水田に発生した藻の下の嫌気発酵状態は徹底
した深水管理で顕著) 自然界における本案事象にかくされた自然の妙理は、物
質循環における資源再生循環分野の産業進展に新たな可
能を教唆する事象でそれを中心とする産業に大きく貢献
出来るものである。
It has been more than 10 years since trials have been carried out after noticing that low temperature crushed firgrass has a major role in the return decomposition of mature plant resource material-that is, the law-based decomposition system that returns to soil. Most of the organic resources in the streets have the potential to participate in the circulatory system as precious resources based on the technical idea. If this application were a step closer to the completion of the ecosystem cycle, we would have to look to the qualities of the resources that nature has left behind today, thanks to the world's need for them. The categories of aerobic fermentation and anaerobic fermentation in the material cycle are wide, and there are many materials that are said to correspond to them. However, it is significant that the events leading up to the present invention have shown that reactions in nature are not as distinct as words. That is, in the material cycle, aerobic fermentation greatly changes the quality while reducing the amount of material, but anaerobic fermentation does not significantly reduce the amount of material, and the phenomenon that drastically changes the quality is clear, called digestion. This is true. When the fermentation is carried out by combining a plurality of materials mainly containing a large amount of plant fiber leading to the present invention and adding a specific fermentation initiator enzyme, the silicic acid therein is activated to generate minerals, and secondary and tertiary. The fermentation, which also includes animal quality, has very little off-flavor due to the decomposition of protein, and is close to the reaction in healthy soil. When the aerobic fermentation product which has been processed as a raw material based on the present invention is subjected to severe anaerobic conditions, it undergoes extreme anaerobic fermentation adapted to the environment.
(The anaerobic fermentation state under the algae that occurred in the paddy field described above is remarkable by thorough deep water management.) The natural philosophy of the nature of the present invention in the natural world is a new development in the industrial development of the resource recycling cycle in the material cycle. It is an event that inspires the possibility and can greatly contribute to the industry centered on it.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C05F 5/00 C05F 15/00 11/08 B09B 3/00 D 15/00 ZABC Fターム(参考) 4D004 AA02 AA03 AA04 BA03 BA04 CA15 CA18 CA19 CA48 CB04 CC07 CC08 DA02 DA03 DA06 4D059 AA01 AA07 BA02 BA03 BA12 BA26 BA29 BE00 BF15 BJ00 BK01 CC01 CC03 DA56 DA70 DB31 DB32 EB06 EB16 4H061 AA02 BB45 CC11 CC32 CC36 CC41 CC42 CC45 CC47 EE64 EE66 EE70 FF06 GG41 GG43 GG48 GG49 GG70 LL02 LL05 LL26 ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C05F 5/00 C05F 15/00 11/08 B09B 3/00 D 15/00 ZABC F-term (Reference) 4D004 AA02 AA03 AA04 BA03 BA04 CA15 CA18 CA19 CA48 CB04 CC07 CC08 DA02 DA03 DA06 4D059 AA01 AA07 BA02 BA03 BA12 BA26 BA29 BE00 BF15 BJ00 BK01 CC01 CC03 DA56 DA70 DB31 DB32 EB06 EB16 4H061 AA02 BB45 CC41 CC32 CG45 CC41 CC32 CG45 CC41 CC32 CG45 CC41 CC32 CG45 CC41 CC32 CG45 CC41 CC32 GG GG48 GG49 GG70 LL02 LL05 LL26

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】成熟した植物繊維を多く含む低温破砕モミ
ガラと、豆腐粕と、人工培地のキノコ廃オガと、ビール
粕の如き有機珪酸を多く含有する複多数の食品加工残渣
的素材に、発酵起剤としての特定酵素稀釈液を加えて水
分を40〜50%望ましくは45%程度に調製しながら
充分に混合し、50〜70℃望ましくは65℃以下の温
度で5〜10日望ましくは7日以上好気発酵をさせて、
有用微生物群が誘導生成された発酵生成物(A)を得る
構成に成ることを特徴とするメタンガス発生装置に供給
する原料の処理並びに堆肥製造法。
1. Fermentation into low-crushed firgrass rich in mature plant fiber, tofu cake, waste mushrooms of artificial medium, and a large number of food processing residue materials containing a large amount of organic silicic acid such as beer cake. A specific enzyme diluent as a propellant is added to the mixture to adjust the water content to 40 to 50%, preferably about 45%, and sufficiently mixed, and the mixture is heated at a temperature of 50 to 70 ° C, preferably 65 ° C or less, for 5 to 10 days, preferably 7 to 10 days. Aerobic fermentation for more than a day
A method for treating a raw material supplied to a methane gas generator and producing a compost, wherein the fermentation product (A) is obtained by induction of a useful microorganism group.
【請求項2】請求項1の(A)材を畜舎敷料として使用
するに当って特殊腐植物質抽出液を定率撒布し有意の期
間排泄された糞尿を吸着させながら、(A)材有用微生
物群を増殖せしめ、畜舎より取出し後特定酵素稀釋液を
撒布して混合堆積し撹拌しながら強制送風を含む65℃
以下の温度の好気発酵によって緩かに分解熟成する構成
に成ることを特徴とする請求項1記載のメタンガス発生
装置に供給する原料の処理並びに堆肥製造法。
2. The useful microorganism group of the material (A) while using the material (A) of claim 1 as a livestock litter and spraying a special humic substance extract at a constant rate to adsorb excrement excreted for a significant period of time. After taking out from the barn, sprinkle a specific enzyme dilution solution and mix and deposit.
The method for treating a raw material supplied to a methane gas generator and the method for producing compost according to claim 1, wherein the composition is configured to be slowly decomposed and matured by aerobic fermentation at the following temperature.
【請求項3】木炭細粉体に特殊腐植物質抽出液を噴霧吸
着せしめたものと、特定種類の素材を用いた請求項1の
(A)材とを混合した飼料補完材(D)を家畜飼料に混
合して与え、請求項1の(A)材を畜舎敷料として使用
し、有意の期間排出される糞尿を吸着させながらA材の
有用微生物群を増殖せしめ畜舎より取出し後特定酵素稀
釋液を撒布して混合堆積し撹拌しながら強制送風を含む
65℃以下の温度の好気発酵によって緩かに分解熟成す
る構成に成ることを特徴とする請求項1記載のメタンガ
ス発生装置に供給する原料の処理並びに堆肥製造法
3. A feed supplement material (D) obtained by mixing a special humic substance extract spray-adsorbed on fine charcoal powder and a material (A) according to claim 1 using a specific kind of material. The mixture is given to a feed, the material (A) according to claim 1 is used as a livestock litter, and the useful microorganisms of the material A are proliferated while adsorbing manure discharged for a significant period of time. The raw material supplied to the methane gas generator according to claim 1, characterized in that the raw material is slowly decomposed and matured by aerobic fermentation at a temperature of 65 ° C or less including forced air blowing while mixing, depositing, and stirring. Processing and compost production method
【請求項4】請求項1の(A)材に、比較少量の畜糞を
加え、特殊腐植物質抽出液を定率撒布して望ましくは充
分に練り混合し、撹拌しながら強制送風を含む65℃以
下の温度の好気発酵によって、緩やかに分解熟成せしめ
ることを特徴とする請求項1記載のメタンガス発生装置
に供給する原料の処理並びに堆肥製造法
4. A small amount of livestock dung is added to the material (A) according to claim 1, and a special humic substance extract is sprayed at a constant rate, preferably kneaded and mixed well, and the mixture is stirred at 65 ° C. or lower including forced air blowing. The method for treating a raw material supplied to a methane gas generator and the method for producing compost according to claim 1, characterized in that the raw material is slowly decomposed and aged by aerobic fermentation at a temperature.
【請求項5】請求項1の(A)材に比較少量の魚や肉或
は生ゴミの如き残渣を細かく砕いて加え、更に特殊腐植
物質抽出液を定率撒布して望ましくは充分に練り混合
し、撹拌しながら強制送風を含む65℃以下の温度の好
気発酵によって、緩やかに分解熟成せしめることを特徴
とする請求項1記載のメタンガス発生装置に供給する原
料の処理並びに堆肥製造法。
5. A comparatively small amount of a residue such as fish, meat or garbage is added to the material (A) of claim 1 by finely pulverizing it, and a special humic extract is sprayed at a constant rate, and preferably thoroughly kneaded and mixed. 2. The method for treating a raw material supplied to a methane gas generator and a method for producing compost according to claim 1, wherein the mixture is slowly decomposed and aged by aerobic fermentation at a temperature of 65 ° C. or lower including forced air while stirring.
【請求項6】前各項に因って処理された原料物材と特定
酵素稀釋液を加えて爆気処理した畜尿を併せてメタンガ
ス発生装置に原料として供給しメタンガスの発生を効率
的ならしめた後、その残渣を脱水し、貝化石、穀実糠、
甲殻類、有機燐酸(鶏糞を原料としたものは不要)を加
え、特定酵素稀釋液を撒布し望ましくは充分に練り混合
し、撹拌しながら強制送風を含む65℃以下の温度の好
気発酵によって緩かに分解熟成して活性力の強い堆肥化
する構成に成ることを特徴とする請求項1記載のメタン
ガス発生装置に供給する原料の処理並びに堆肥製造法。
6. A raw material material treated according to each of the preceding items and a specific enzyme dilution liquid, followed by explosion-treated animal urine, are supplied together as a raw material to a methane gas generating device to efficiently generate methane gas. After squeezing, the residue is dehydrated, shell fossils, grain bran,
Add crustaceans and organic phosphoric acid (not necessary to use chicken dung as raw material), sprinkle with a specific enzyme dilution solution, mix well, and mix well. The method for treating a raw material supplied to a methane gas generator and a method for producing compost according to claim 1, characterized in that the composition is formed into a compost having a strong activity by being slowly decomposed and aged.
JP2000381090A 2000-11-09 2000-11-09 Treatment of raw material to be supplied to gaseous methane generator and compost manufacturing method Pending JP2002154887A (en)

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007098229A (en) * 2005-09-30 2007-04-19 Kurita Water Ind Ltd Method and apparatus for treating organic waste material
CN103008323A (en) * 2012-11-01 2013-04-03 青岛农业大学 Method for preparing fuel gas and biogas manures by using beer brewing wastes
CN103708967A (en) * 2013-12-30 2014-04-09 内乡县牧原实业有限公司 Method for producing organic fertilizer by using pig manures
CN108285385A (en) * 2018-01-11 2018-07-17 河南省林业科学研究院 A kind of Europe Lee special complex fertilizer and preparation method thereof
CN112744991A (en) * 2021-01-12 2021-05-04 江西省农业科学院农业应用微生物研究所(江西省农村能源研究中心) Method for producing biogas through high-load anaerobic fermentation by fully-quantitatively collecting breeding manure

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007098229A (en) * 2005-09-30 2007-04-19 Kurita Water Ind Ltd Method and apparatus for treating organic waste material
JP4665693B2 (en) * 2005-09-30 2011-04-06 栗田工業株式会社 Method and apparatus for treating organic waste
CN103008323A (en) * 2012-11-01 2013-04-03 青岛农业大学 Method for preparing fuel gas and biogas manures by using beer brewing wastes
CN103708967A (en) * 2013-12-30 2014-04-09 内乡县牧原实业有限公司 Method for producing organic fertilizer by using pig manures
CN108285385A (en) * 2018-01-11 2018-07-17 河南省林业科学研究院 A kind of Europe Lee special complex fertilizer and preparation method thereof
CN112744991A (en) * 2021-01-12 2021-05-04 江西省农业科学院农业应用微生物研究所(江西省农村能源研究中心) Method for producing biogas through high-load anaerobic fermentation by fully-quantitatively collecting breeding manure

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