JP2006116529A - Drying method for organic matter, product by the method and its drying device - Google Patents

Drying method for organic matter, product by the method and its drying device Download PDF

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JP2006116529A
JP2006116529A JP2005271748A JP2005271748A JP2006116529A JP 2006116529 A JP2006116529 A JP 2006116529A JP 2005271748 A JP2005271748 A JP 2005271748A JP 2005271748 A JP2005271748 A JP 2005271748A JP 2006116529 A JP2006116529 A JP 2006116529A
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organic
drying
organic matter
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fermented
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JP5144884B2 (en
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Hisakazu Ikeda
久和 池田
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    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P60/00Technologies relating to agriculture, livestock or agroalimentary industries
    • Y02P60/80Food processing, e.g. use of renewable energies or variable speed drives in handling, conveying or stacking
    • Y02P60/87Re-use of by-products of food processing for fodder production
    • 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

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  • Fertilizers (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a technology which ferments and dries an organic waste at a low cost in a short time by making the best use of the properties of microorganisms, and to provide a technology which can prevent environmental destruction by using materials obtained by the fermentation and drying. <P>SOLUTION: In a drying method for the organic waste, corncob meal or its fermentation product is mixed in the organic waste to adjust the water content to 30-80% to prepare a raw material 20, a fermentation tank having a hollow floor made so that a hollow space 15 occupying ≥30% of a floor area is formed under the floor is provided, the raw material 20 is piled up on the hollow floor to a height of 20-120 cm, an environmental condition for introducing air into the upper and lower sides at the same time is made, and the raw material is turned, fermented and dried. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、生ゴミ等の有機廃棄物を代表的なものとする有機物を、低コストで処理する方法や、処理後の生産物の利用に関し、さらに地球温暖化防止の対策を始めとして環境汚染を解決することに関する。   The present invention relates to a method for processing organic materials such as organic waste, such as garbage, at low cost, and the use of processed products. Relating to solving.

従来の生ゴミや有機物質の乾燥方法では、一部で太陽熱の利用もあるが、大量の処理ができないことから、大部分は火力によって高いコストをかけて乾燥処理がなされている。また、有機廃棄物等の有機物処理の技術では、生ゴミ等を、発酵槽で発酵させて堆肥化して土壌へ還元するか、焼却等によって高いコストをかけて処理していた。
しかし、経済の行き詰まりや、環境汚染等により、生ゴミ等の焼却は出来なくなってきた。また、堆肥化にしても、塩分や有害物質を含有するために肥料としての消費が困難な場合がある。
また、今までの堆肥の発酵方法は、アンモニア化成菌や硫酸還元菌による腐敗発酵か枯草菌等の高熱菌による分解発酵であるため、それを土壌に還元してもそれらの菌では農地の表土の環境条件に適さない。そのため、それらを農地に入れることによって、環境汚染による悪玉菌による腐敗発酵が先行し、土壌障害となって急速に病虫害が発生することになり、農地を蝕んでいる。
また、水分の多い生ゴミを無理に乾燥又は焼却処理してきたことにより、大気を汚染するだけでなく、炭酸ガスの温室効果により地球規模での環境破壊を招いている。
Some conventional methods for drying garbage and organic materials use solar heat, but since they cannot be processed in large quantities, most of them are dried at high cost by thermal power. Further, in the technology for treating organic matter such as organic waste, raw garbage or the like is fermented in a fermenter and composted to be reduced to the soil, or treated at high cost by incineration or the like.
However, due to economic stagnation and environmental pollution, it has become impossible to incinerate garbage. Even if composting, consumption as fertilizer may be difficult because it contains salt and harmful substances.
In addition, the compost fermentation method used so far is septic fermentation with ammonia-forming bacteria or sulfate-reducing bacteria, or decomposition fermentation with hyperthermic bacteria such as Bacillus subtilis. Not suitable for environmental conditions. Therefore, by putting them in the farmland, spoilage fermentation by bad bacteria due to environmental pollution precedes, causing soil damage and causing pest damage rapidly, and eroding the farmland.
In addition, forcibly drying or incinerating raw garbage with a lot of moisture not only pollutes the atmosphere, but also causes environmental destruction on a global scale due to the greenhouse effect of carbon dioxide.

なお、本願出願人は、キノコ菌を培養してキノコを収穫した後に廃棄されるキノコ廃培地を原料とする土壌改質肥料及びその製造法について提案をしている(特許文献1参照)。また、コーンコブを生ゴミの処理に利用する方法も提案してある(特許文献2参照)。
特開平1−270584号公報(第1頁) 特開平7−214034号公報(第1頁)
The applicant of the present application has proposed a soil-modified fertilizer using a mushroom waste medium discarded as a raw material after culturing mushrooms and harvesting mushrooms, and a method for producing the same (see Patent Document 1). In addition, a method of using corn cob for processing garbage is also proposed (see Patent Document 2).
JP-A-1-270584 (first page) Japanese Unexamined Patent Publication No. 7-214034 (first page)

食品工場から大量に排出する有機廃棄物や、家庭から排出する生ゴミ又は上下水道の汚泥の多くは、焼却処理するか又は火力乾燥によって乾燥して処理してきた。しかし、これでは、コストがかかるだけではなく、無駄なエネルギーを消費することになり、地球環境の破壊をもたらし、国際問題にもなっている。
本発明の目的は、上記の既知技術の欠点を克服しようとするもので、微生物の特性を最大限に応用し、短時間で且つ低コストで発酵乾燥させる技術を提供することにある。また、その発酵乾燥によって得られた資材を利用することによって、環境破壊を防止することができる技術を提供することにある。また、無駄な炭酸ガスの発生を抑え、地球環境の温暖化を防止することにもある。
Many organic waste discharged from food factories, household garbage discharged from households, and water and sewage sludge have been incinerated or dried by thermal drying. However, this is not only costly, but also consumes wasted energy, causing the destruction of the global environment and becoming an international issue.
An object of the present invention is to overcome the above-mentioned drawbacks of the known technique, and to provide a technique for applying the characteristics of microorganisms to the maximum and fermenting and drying in a short time and at a low cost. Moreover, it is providing the technique which can prevent environmental destruction by utilizing the material obtained by the fermentation drying. In addition, the generation of useless carbon dioxide gas is suppressed, and global warming is prevented.

本発明は、上記目的を達成するために次の構成を備える。
本発明にかかる有機物の乾燥方法の一形態によれば、有機廃棄物等の有機物を発酵槽内で発酵させて乾燥させる方法において、前記発酵槽の床部を、木材、炭化物、セラミック又はプラスチックのいずれか一又は組合せによる床材で設け、該床材と床材の隙間を接着剤等で埋めないで空気の通路を作り、ロータリー型回転刃を備える装置等で前記床部上の前記有機物の切り返しと移動を同時に行い、該有機物を発酵させて乾燥処理することを特徴とする。
また、本発明にかかる有機物の乾燥方法の一形態によれば、前記有機物は、コーンコブミール又はその発酵物が混合されていることを特徴とすることができる。
The present invention has the following configuration in order to achieve the above object.
According to one aspect of the method for drying organic matter according to the present invention, in the method of fermenting organic matter such as organic waste in a fermenter and drying, the floor of the fermenter is made of wood, carbide, ceramic or plastic. Provided with a flooring material of any one or a combination, create an air passage without filling the gap between the flooring material with an adhesive, etc., and use a device equipped with a rotary rotary blade etc. It is characterized in that the turning and moving are performed simultaneously, the organic matter is fermented and dried.
Moreover, according to one form of the drying method of the organic substance concerning this invention, the said organic substance can be mixed with corn cob meal or its fermented material.

また、本発明にかかる有機物の乾燥方法の一形態によれば、有機廃棄物にコーンコブミール又はその発酵物を混入し、水分30〜80%に調整して有機物原料とし、下側に中空空間が床面積の30%以上を占めるように設けられた中空床を備える発酵槽を作り、該中空床の上側に前記原料を20cm〜120cmの高さに積み上げ、上側と下側へ同時に空気を取り入れるように環境条件を作り、切り返し発酵乾燥を行うことを特徴とする。
また、本発明にかかる有機物の乾燥方法の一形態によれば、前記有機廃棄物に重量比で5〜60%のコーンコブミールを混合して有機物原料とすることを特徴とすることができる。
Moreover, according to one form of the drying method of the organic substance concerning this invention, a corn cob meal or its fermented material is mixed in an organic waste, it adjusts to 30 to 80% of water | moisture content as an organic raw material, and a hollow space is below. Make a fermenter equipped with a hollow floor provided to occupy 30% or more of the floor area, stack the raw material at a height of 20 cm to 120 cm on the upper side of the hollow floor, and simultaneously take in air to the upper side and the lower side It is characterized in that environmental conditions are created and fermented and dried.
Moreover, according to one form of the drying method of the organic substance concerning this invention, 5-60% of corn cob meal is mixed with the said organic waste by weight ratio, It can be characterized by the above-mentioned.

また、本発明にかかる発酵飼料の一形態によれば、上記の有機物の乾燥方法によって製造したこと、又は前記有機物に栄養素を加えた上で上記の有機物の乾燥方法によって製造したことを特徴とすることができる。
また、本発明にかかる有機質肥料の一形態によれば、上記の有機物の乾燥方法によって製造したこと、又は前記有機物に栄養素やミネラルを加えた上で上記の有機物の乾燥方法によって製造したことを特徴とすることができる。
また、本発明にかかる他の形態としては、上記の有機物の乾燥方法によって製造したことを特徴とする畜産用の敷料若しくは病害対策資材、農作物の病虫害対策資材、さらにまた、ダイオキシン、残留農薬、若しくは亜硝酸態窒素等の土壌中に含まれる有害物質の分解剤がある。
また、本発明にかかる他の形態としては、以上に記載された発酵飼料又は有機質肥料等の発酵物で発酵されたことを特徴とする肥料又は飼料がある。
Moreover, according to one form of the fermented feed concerning this invention, it manufactured by the drying method of said organic substance, or it manufactured by the said organic substance drying method after adding a nutrient to the said organic substance, It is characterized by the above-mentioned. be able to.
Moreover, according to one form of the organic fertilizer concerning this invention, it manufactured by the drying method of said organic substance, or it manufactured by said organic substance drying method after adding a nutrient and a mineral to the said organic substance. It can be.
In addition, as other forms according to the present invention, livestock bedding or disease control materials produced by the above-mentioned organic matter drying method, crop disease control materials, dioxins, residual agricultural chemicals, or There is a decomposing agent for harmful substances contained in soil such as nitrite nitrogen.
Moreover, as another form concerning this invention, there exists a fertilizer or feed characterized by having been fermented with fermented materials, such as the fermented feed or organic fertilizer described above.

また、本発明にかかる有機物の乾燥装置の一形態によれば、有機廃棄物等の有機物を発酵槽内で発酵させて乾燥させる有機物の乾燥装置において、前記発酵槽内に、木材、炭化物、セラミック又はプラスチックのいずれか一又は組合せによる床材で設けられた床部と、該床部の前記床材と床材の隙間を接着剤等で埋めないことで形成された空気の通路と、前記床部上の前記有機物の切り返しと移動を同時に行うようにロータリー型回転刃を備える有機物の撹拌移動装置が設けられたことを特徴とする。   Moreover, according to one form of the organic matter drying apparatus concerning this invention, in the organic matter drying apparatus which ferments organic matter, such as an organic waste, in a fermenter, in said fermenter, wood, carbide, ceramic Or a floor portion provided with a flooring material made of any one or a combination of plastic, an air passage formed by not filling a gap between the flooring material and the flooring material with an adhesive or the like, and the flooring An organic substance stirring and moving device including a rotary rotary blade is provided so that the organic substance on the part is turned back and moved simultaneously.

本発明にかかる有機物の乾燥方法、その方法による生産物及びその乾燥装置によれば、今まで焼却処分していた有機廃棄物等の有機物を極低コストで発酵乾燥させ、同時に微生物資源として、人畜の健康食品若しくは飼料、敷料、発酵剤、土壌改良剤、作物の病気治療薬等各方面に活用でき、地域環境を浄化させ、地球温暖化防止にも役立つ。
石油エネルギーを使用せず、乾燥が短時間で大量にできるため、コストの削減になり、しかも簡単な施設で製造できる。発酵乾燥した有機質はそのまま発酵飼料、肥料、畜産の敷料、各種発酵材等の高級な材料となる。
According to the method for drying organic matter, the product produced by the method and the drying apparatus according to the present invention, organic matter such as organic waste that has been incinerated until now is fermented and dried at an extremely low cost, and at the same time, It can be used in various fields such as health foods or feeds, bedding, fermenting agents, soil conditioners, crop disease treatments, etc., and it helps to purify the local environment and prevent global warming.
Without using petroleum energy, drying can be done in a large amount in a short time, thus reducing the cost and manufacturing in a simple facility. The fermented and dried organic matter is directly used as a high-grade material such as fermented feed, fertilizer, livestock bedding, and various fermented materials.

以下、本発明の有機物の乾燥方法、その方法による生産物及びその乾燥装置に係る最良の一形態を以下に詳細に説明する。
先ず、本発明の構成について概要を説明する。
食品工場から発生する生ゴミを必要に応じた微生物の適温に調整して微生物のエネルギーを最大限に活用し、原料を発酵乾燥させる。
このため、最適の発酵環境を作るため、原料の厚さを40cm〜80cm位とし、山脈形のように盛る。また、床等の原料が直接触れる部分は、コンクリートにせずに、木材、木炭、プラスチック、粘土(セラミック)等の材料を用い、多面から空気の吸入が可能な環境にする。好ましくは、床下は中空にして適度な圧の空気を挿入する。
さらに、施設はビニールハウスで太陽熱も利用できる。また、発酵を促進し、より多くの水分を微生物に吸収させ、発散させるため、コーンコブミールを添加する。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the best mode of the organic matter drying method, the product produced by the method and the drying apparatus of the present invention will be described in detail.
First, an outline of the configuration of the present invention will be described.
The raw garbage generated from food factories is adjusted to the appropriate temperature of microorganisms as needed to make maximum use of the energy of microorganisms, and the raw materials are fermented and dried.
For this reason, in order to make the optimal fermentation environment, the thickness of the raw material is set to about 40 cm to 80 cm, and it is formed like a mountain range. In addition, parts such as floors that are directly touched by raw materials are made of wood, charcoal, plastic, clay (ceramics), etc., instead of concrete, so that air can be inhaled from many sides. Preferably, the underfloor is hollow and air of appropriate pressure is inserted.
In addition, the facility is a greenhouse and can also use solar heat. In addition, corn cob meal is added to promote fermentation and allow microorganisms to absorb and release more water.

つまり、本発明は、前述した既知技術の欠点を克服しようとするもので、微生物の特性を最大限に応用し、床材にはコンクリートを使用せず、できる限り、床上げ中空式の発酵装置を使用し、下部からも自然的な給気を行い、短時間低コストで発酵乾燥させる技術である。また、その発酵乾燥によって得られた資材を利用することによって、環境破壊を防止することができる技術である。
先ず、本発明は、生ゴミ等の有機物の石油を使用しない微生物エネルギーの効率的な活用及びロータリー型の撹拌による低コストでの乾燥方法、及び床材や原料の堆積高さ等、腐敗発酵や高温発酵を起こさない善玉微生物群の環境条件の発見という2つの技術から成り立っている。
That is, the present invention seeks to overcome the above-mentioned drawbacks of the known technology, and maximizes the characteristics of microorganisms, and does not use concrete for the flooring. It is a technology that uses and naturally feeds air from the bottom, and is fermented and dried for a short time at low cost. Moreover, it is a technique which can prevent environmental destruction by utilizing the material obtained by the fermentation drying.
First, the present invention relates to efficient utilization of microbial energy that does not use organic petroleum such as raw garbage, and a low-cost drying method by rotary stirring, and rot fermentation, It consists of two technologies: the discovery of environmental conditions for good microbial groups that do not cause high-temperature fermentation.

微生物は、増殖の過程で熱エネルギーを発生し、菌糸を張りめぐらせて行く。その過程において、水分を分離し、乾燥を促進させる。それを最も効率的に行う方法として空気を上面と下面の両面から自然的に供給する。
従来の方法も下面から空気を入れていた。しかし、それは強制的に又は集中的に送り込むため、高温菌である枯草菌が増殖し、ブザリウム菌等の悪玉菌と戦う力がない。よって病気を治す力が弱い。従って、床部は床下から床上への空気の流れが自然的になるように制限される材質又は構造とすればよい。
中空床は、自然的に空気を供給する方法で木質材等の内部を浸透する空気を利用する。そのために多少の圧力を必要とする。
また、空気を浸透しない材料を使用する場合は、無数の小さな孔や隙間を作る。なお、下面側からの空気を入り易くするため、床材の下面の角について面を大きく取るとよい。材料と材料の間は単に突き合わせても隙間はできるが、0.5mm〜2mm位の隙間を作ることが好ましい。
これによって、最も自然的に表土に順応した酵母菌、麹菌、納豆菌等が、コーンコブミールに多く含有する糖分とリグニンを餌及び住家とし、善玉菌の微生物群が増殖する。
Microorganisms generate heat energy in the process of growth and spread mycelia. In the process, moisture is separated and drying is promoted. The most efficient way to do this is to supply air naturally from both the top and bottom surfaces.
The conventional method also put air from the lower surface. However, since it is forcibly or intensively sent, Bacillus subtilis, which is a thermophilic bacterium, grows and has no ability to fight against bad bacteria such as Buzarium. Therefore, the ability to cure the disease is weak. Therefore, the floor portion may be made of a material or a structure that is restricted so that the flow of air from under the floor to the floor becomes natural.
The hollow floor uses air that permeates the inside of a wood material or the like by a method of supplying air naturally. This requires some pressure.
Also, when using materials that do not penetrate air, countless small holes and gaps are created. In addition, in order to make air from the lower surface side easy to enter, it is better to take a large surface for the corner of the lower surface of the flooring. Although a gap can be created even if the materials are merely abutted, it is preferable to create a gap of about 0.5 mm to 2 mm.
As a result, yeasts, koji molds, natto bacteria, etc. that have most naturally adapted to the topsoil feed on sugar and lignin, which are abundant in corn cobmeal, as feed and dwellers, and microorganism groups of good bacteria grow.

しかも、一気に四方八方から菌糸が増殖することによって、また、数回の切り返しによって全体が菌糸に占領されて菌が水分を吸収することによって短時間で乾燥物ができる。
発酵乾燥ラインにおける後の1/3は乾燥工程のみとする。床材には空気孔を開け、急速に乾燥させる。但し、空気は50℃以下の空気を利用する。それ以上になると微生物が死滅する。切り返しの発酵作業は1〜3日に一回、乾燥作業は1日に二回を基本とする。
In addition, when the mycelium grows from all directions at once, and the whole is occupied by the mycelium by several times of turnover, and the bacteria absorb moisture, a dry matter can be formed in a short time.
The last 1/3 in the fermentation drying line is only the drying process. The flooring is perforated and dried quickly. However, air of 50 ° C. or lower is used. Beyond that, the microorganisms die. The fermenting operation for turning back is basically once every 1-3 days, and the drying operation is basically twice a day.

床材はコンパネの利用か又は薄い木質板を利用する。できれば、表面を炭化した物を利用する。病気の防除の目的から雑菌が増すコンクリートの床や壁を作らない。アルカリ性が強いため、別の悪玉菌が増殖する。なお、床板が木材でも腐敗発酵でないため、腐ることはない。
セラミック板、又はプラスチック板を利用する場合は空気の吸入を図るため、例えば20〜50cm角の平板を利用するとよい。並べる段階で板と板の隙間が自然にできるため、空気の流通が可能である。
Use floor panels or thin wooden boards. If possible, use a carbonized surface. Do not make concrete floors or walls that increase germs for disease control purposes. Due to the strong alkalinity, other bad bacteria grow. In addition, even if the floorboard is wood, it does not rot, so it will not rot.
In the case of using a ceramic plate or a plastic plate, for example, a 20 to 50 cm square plate may be used in order to suck air. Since the gap between the plates can be made naturally at the stage of arrangement, air can be circulated.

側壁は基本的に必要がない。発酵原料(材料)をかまぼこ型に盛り上げて堆積させれば、材料の両側が側壁に触れることによる雑菌の侵入を最小限にできる。撹拌機はトラクターに用いられるロータリー型のかき混ぜ装置を用いる。それによって、中高のかまぼこ型の撹拌と、材料の移動が自動的に行われる。なお、側壁に材料が触れた場合、その接触面は水分を周囲から吸収し、発散を防止するため、水分過多となる。そのため、悪玉微生物が多数発生してしまう。
以上が、病虫害の対策資材の製造に必要な善玉菌増殖の最適な環境条件である。
Side walls are basically unnecessary. If the fermentation raw material (material) is raised and deposited in a kamaboko shape, the invasion of germs due to both sides of the material touching the side wall can be minimized. The stirrer uses a rotary type stirring device used for a tractor. As a result, medium-high kamaboko-type stirring and material movement are automatically performed. When the material touches the side wall, the contact surface absorbs moisture from the surroundings and prevents divergence, resulting in excessive moisture. Therefore, many bad microorganisms are generated.
The above is the optimal environmental conditions for the growth of good bacteria necessary for the production of disease and pest control materials.

有機廃棄物とは、農産、畜産、食品産業、家庭から出るゴミ、ホテル・レストラン等から出る植物質及び動物質の廃棄物であって、例えば、もみ殻、麦皮、コーンコブミール、汚泥、バガス、そば殻、豆ガラ、米ぬか、オカラ、果実ジュースの搾りかす、調理で生ずる生ゴミ、牛、羊、豚、鶏、その他の飼養動物の糞等を包含する。   Organic waste is agricultural, livestock, food industry, household waste, vegetable and animal waste from hotels and restaurants, such as rice husk, barley, corn cob meal, sludge, bagasse , Buckwheat husk, bean shell, rice bran, rice bran, squeezed fruit juice, raw garbage produced by cooking, cattle, sheep, pigs, chickens, feces of other domestic animals, etc.

上記は、発酵熱を利用する操作を述べたが、所望により発酵を外部からの加熱及びより多い給気下で行って促進させることもでき、加温空気を用いて加熱と給気を同時に行うこともできる。
処理される有機物は必要に応じて水分調整をする。調整材は乾燥物の利用用途によって異なるが、乾燥物の草質材(もみ殻、コーンコブ、わら、そば殻、麦皮等)、米ヌカ、フスマ、乾燥オカラ等で水分調整を行う。水分率は50%を最適として最高で60%以下にする。また、戻し堆肥ができる2度目以降は、微生物の発酵基材として、その戻し堆肥を利用してコストを抑える。
The above describes the operation using the heat of fermentation, but if desired, the fermentation can be promoted by external heating and more air supply, and heating and air supply are simultaneously performed using warmed air. You can also.
The organic matter to be treated is moisture-adjusted as necessary. The adjustment material varies depending on the usage of the dried product, but the moisture is adjusted with herbaceous material (rice husk, corn cob, straw, buckwheat, barley, etc.), rice bran, bran, dried okara, etc. The moisture content is optimally 50% and the maximum is 60% or less. In addition, after the second time when returning compost can be produced, the cost is reduced by using the returning compost as a fermentation base material for microorganisms.

病気を治す善玉菌群は、食用菌群であるが、これは高温菌ではない。そのため、発酵温度が57℃以下になるように、切り返し回数等の作業によって調整する。水分が多過ぎる場合は、アンモニア化成菌が増殖した後に、枯草菌が発生して温度が上昇する。それは堆肥としての効果はあるが、病気を治すことができない。
かつて、作物の病気は農薬等の化学薬品によって処理されてきた。しかし、現在の農地はその多用によって土壌環境が破壊され、病気を抑えることができなくなった。化学農薬の対症療法による農業の限界が見えてきた。そのような現実に直面し、本発明者は、病気における根本的問題解決のため、微生物群による病気の対応に取り組み、ようやくその菌群の培養とその菌群の最も好む環境条件の発見に成功したのである。
The good fungus group that cures the disease is an edible fungus group, but it is not a thermophilic bacterium. Therefore, it adjusts by work, such as the frequency | count of reversal, so that fermentation temperature may be 57 degrees C or less. When there is too much moisture, Bacillus subtilis is generated and the temperature rises after the ammonia-forming bacteria grow. It works as a compost but cannot cure the disease.
In the past, crop diseases have been treated with chemicals such as pesticides. However, the current agricultural land has destroyed the soil environment due to its heavy use, making it impossible to control the disease. The limits of agriculture through the symptomatic treatment of chemical pesticides have become visible. Faced with such a reality, the present inventor tackled the response of the disease by the microorganism group to solve the fundamental problem in the disease, and finally succeeded in culturing the fungus group and finding the most preferred environmental condition of the fungus group. It was.

好ましい水分は40〜55%、温度は35〜57℃、接地材は木材、セラミック材又は炭化物等が好ましく、原料の堆積高さ50〜70cmのかまぼこ型等の菌の好む条件を与えることにより、善玉菌群が活性化する。
それが土壌に還元されたときには、急激に活動を起こし、悪玉菌群を攻撃するのである。そのため、適度な栄養源が必要である。なお、完全発酵物は病気を治す力が弱い。以上の最適条件の基に培養した善玉菌は、今までの常識を打ち破る病気に対する治癒効果がある。そのことが、多くの栽培試験で実証された。
Preferable moisture is 40 to 55%, temperature is 35 to 57 ° C., and the grounding material is preferably wood, ceramic material, carbide or the like, and by giving conditions preferred by bacteria such as kamaboko type with a deposition height of 50 to 70 cm, The good bacteria group is activated.
When it is reduced to the soil, it takes action rapidly and attacks the bad bacteria group. Therefore, an appropriate nutrient source is necessary. Completely fermented products have a weak ability to cure diseases. The good bacteria cultured under the above optimum conditions have a healing effect on diseases that break the conventional sense. This has been demonstrated in many cultivation tests.

更に得られた発酵物は、土壌障害を解決するだけでなく、土壌中に残留するダイオキシンを分解して無害とし、また、残留農薬や化学肥料の有害物も微生物の作用によって浄化する。今、大きな問題となってきた未分解の亜硝酸態窒素が土壌中に残留し、それを吸収した作物等を食べた人畜が健康を大きく損なうことになる。これに対して、本発明に係る資材は、その亜硝酸態窒素を安定した硝酸態窒素に転換して人畜の健康を守るものであり、地球環境を浄化する最も優れた今までになかった資材である。   Furthermore, the obtained fermented product not only solves soil damage, but also decomposes dioxins remaining in the soil to make them harmless, and also removes harmful agricultural chemicals and chemical fertilizers by the action of microorganisms. Undegraded nitrite nitrogen, which has become a big problem now, remains in the soil, and human livestock that eats crops that have absorbed it will greatly impair their health. On the other hand, the material according to the present invention protects human health by converting the nitrite nitrogen to stable nitrate nitrogen, and is the most excellent unprecedented material that purifies the global environment. It is.

更に、その善玉菌による発酵物は、飼料又は食料として使用できる。その効果は、善玉菌の酵素の作用により健康に育ち、肉質が良くなり、産卵率が向上する。
また、その発酵乾燥物は、畜産の敷料として使用できる。栄養源が少なく、リグニンの多い生ゴミの乾燥物は、特殊な微生物で発酵乾燥させることにより、それ自身も敷料と同時に発酵剤としても機能し、悪臭問題を解決させる。そして、その畜糞も、病気を治す土壌改良資材に転換できる。また、その地域全体もその発酵物を使用することにより、地域全体に善玉菌群が繁殖増大して、今問題化している悪い伝染病から人畜を守ることができる。但し、栄養源の多い生ゴミを利用した場合は、発酵温度が急速に上がり、夏場においては飼育環境に合わない。
Further, the fermented product of the good bacteria can be used as feed or food. The effect grows healthy by the action of the enzymes of good bacteria, the meat quality is improved, and the egg-laying rate is improved.
The fermented and dried product can be used as a livestock litter. The dried food waste with a small amount of nutrients and high lignin is used as a fermenting agent at the same time as the bedding by fermenting and drying with special microorganisms, thereby solving the problem of bad odor. And the animal manure can also be converted into soil improvement materials to cure the disease. In addition, by using the fermented product in the entire region, the good bacteria group can be propagated and increased in the entire region, and it is possible to protect human animals from the bad infectious diseases that are now problematic. However, when raw garbage with many nutrient sources is used, the fermentation temperature rises rapidly and does not suit the breeding environment in summer.

有機質肥料としての使用においては言うまでもなく、作物の増収と品質の向上に大いに役立つ。特に化学肥料の使い過ぎによって残留するリン酸分が、微生物の作用で分解吸収されて同化作用が促進され、丈夫でしっかりした作物が育ち、糖度が上がる。そのため、病気にならないし、病気を治すこともできる。従って、害虫にも犯されにくい。当然、農薬の散布回数も激減する。   Needless to say, it is useful for increasing the yield and quality of crops. In particular, the phosphoric acid residue remaining due to excessive use of chemical fertilizer is decomposed and absorbed by the action of microorganisms to promote assimilation, and a strong and solid crop grows, increasing the sugar content. Therefore, it does not get sick and can cure the disease. Therefore, it is not easily violated by pests. Naturally, the number of spraying of pesticides also decreases drastically.

種菌は、戻し堆肥のみの使用では菌が退化するため、純粋培養した種菌を必要量毎回添加して菌群を常に活性化させる。
空気(温風)の送入は、ブロアによって行うが、加温は良質の可燃ゴミの活用が理想的である。発酵する際の発熱を利用すればよい。これによれば、地球温暖化防止の意味も含め、資源の有効活用を図ることができる。
As the inoculum is used only with back compost, the bacteria are degenerated. Therefore, the inoculated bacteria are always activated by adding a purely cultured inoculum every required amount.
Air (warm air) is sent in by a blower, but it is ideal to use good quality combustible waste for heating. What is necessary is just to utilize the heat generated when fermenting. According to this, effective utilization of resources can be achieved including the meaning of prevention of global warming.

次に、実施例1について、実験結果を添付図面及び表と共に詳細に説明する。
実験区:A1区、A2区、対照区:B1区、B2区の4つの分類に分け、発酵乾燥の速度の比較試験をした。施設はパイプによるビニールハウスである。これが発酵槽となっている。
図1はA1区、A2区の施設を説明する斜視図であり、図2はA1区、A2区の施設を説明する側面図である。また、図3はB1区、B2区の施設を説明する斜視図であり、図4はB1区、B2区の施設を説明する側面図である。
図1及び図2に示すように、A1区、A2区の施設は、ビニールハウス10を用いたロータリー式発酵乾燥施設であり、床板部12の下側(床下)に中空15が設けられている。この施設では、床板部12にコンパネを用いてある。20は原料であり、かまぼこ状に堆積されている。本実施例では、中空15の高さ間隔を20cm、原料20の堆積高さを約50cmに設定した。また、かまぼこ状の原料の幅は約5m、その送り方向の長さは全体で30mとなっている。図2に示すように、前区間aの20mは発酵工程となっており、後区間bの10mが乾燥工程となっている。なお、後区間bの床板部12には、直径が5mmの孔16を多数開けてあり、通気性を高めてある。
30はロータリー型のかき混ぜ装置であり、閉ループ状の軌跡31のように移動すると共に、図2に示す矢印32のように回転刃が回転する。これにより、原料20を切り返すと共に、その原料20を白抜き矢印の方向へ順次送ることができる。このかき混ぜ装置30が、有機物の撹拌移動装置の一例となっている。また、50は製品であり、発酵乾燥の終了した資材である。
また、図3及び図4に示すように、B1区、B2区の施設も、ビニールハウス11を用いている。図1に示した施設のような床下の中空はないが、比較的高い圧力の空気を床面から吐出できるように、直径3mmの孔18が複数開いた直径50mmの樹脂パイプ17が2本敷設されている。ロータリー型のかき混ぜ装置30が、図1に示した施設と同様に設けられ、同じく作動する。また、かまぼこ状に堆積された原料の高さは、図1に示したものと同様に約50cmに設定してある。また、51は製品であり、この施設による発酵乾燥工程の終了したものである。
Next, the experimental results of Example 1 will be described in detail with reference to the accompanying drawings and tables.
The test was divided into four categories: experimental zone: A1, A2 zone, control zone: B1, B2 zone, and a comparative test of the rate of fermentation drying was conducted. The facility is a plastic greenhouse with pipes. This is the fermenter.
FIG. 1 is a perspective view illustrating facilities in the A1 and A2 zones, and FIG. 2 is a side view illustrating facilities in the A1 and A2 zones. FIG. 3 is a perspective view for explaining the facilities in the B1 and B2 wards, and FIG. 4 is a side view for explaining the facilities in the B1 and B2 wards.
As shown in FIGS. 1 and 2, the facilities in the A1 and A2 districts are rotary fermentation drying facilities using a greenhouse 10, and a hollow 15 is provided below the floorboard portion 12 (under the floor). . In this facility, a panel is used for the floor board 12. Reference numeral 20 denotes a raw material, which is deposited in a kamaboko shape. In this example, the height interval of the hollow 15 was set to 20 cm, and the deposition height of the raw material 20 was set to about 50 cm. Further, the width of the kamaboko-shaped raw material is about 5 m, and the total length in the feeding direction is 30 m. As shown in FIG. 2, 20 m in the front section a is a fermentation process, and 10 m in the rear section b is a drying process. The floor section 12 in the rear section b is provided with a number of holes 16 having a diameter of 5 mm to enhance air permeability.
Reference numeral 30 denotes a rotary type agitation device which moves as a closed loop locus 31 and rotates a rotary blade as indicated by an arrow 32 shown in FIG. Thereby, the raw material 20 can be turned back and the raw material 20 can be sequentially sent in the direction of the white arrow. This stirring device 30 is an example of an organic stirring and moving device. Reference numeral 50 denotes a product, which is a material that has been fermented and dried.
Also, as shown in FIGS. 3 and 4, the facilities in the B1 ward and the B2 ward also use the vinyl house 11. Although there is no hollow under the floor as in the facility shown in FIG. 1, two 50 mm diameter resin pipes 17 having a plurality of 3 mm diameter holes 18 are laid so that relatively high pressure air can be discharged from the floor surface. Has been. A rotary stirring device 30 is provided and operates similarly to the facility shown in FIG. Further, the height of the raw material deposited in a kamaboko shape is set to about 50 cm, similar to that shown in FIG. Reference numeral 51 denotes a product which has been subjected to the fermentation and drying process by this facility.

A1区とB1区は給気をせずに自然発酵によって発酵乾燥を行い、A2区とB2区は0.5kwのブロアによって給気を行うと共に上部は開放して発酵させる。
原料は、各区共に、エノキの廃培地(水分49%)、お茶ガラ(水分70%)、コーヒーカス(水分80%)を、毎日各3立方メートル、0.5立方メートル、0.5立方メートルずつ投入し、また、0.5立方メートルの戻し堆肥(水分25%)と、種菌となるキノコーソ(商品名:池田農興(長野県埴科郡坂城町大字上平305番地44−17号)の製造品)20kgを投入して水分を50%に調整したものを発酵させた。1日1回の撹拌で原料を60cm/日ずつ移動させ、水分25%まで乾燥させるためにかかる日数の実験を行った。結果は下記のとおりである。

Figure 2006116529
なお、B1区では、下面から水分を吸収するため、最長50日間行っても30%以下にならなかった。 The A1 and B1 districts are fermented and dried by natural fermentation without supplying air, and the A2 and B2 districts are supplied with 0.5 kW blower and the upper part is opened and fermented.
The raw materials for each ward are 3 m3, 0.5 m3, and 0.5 m3 of enoki waste medium (49% water), tea gala (70% water), and coffee residue (80% water) each day. In addition, 0.5 cubic meters of return compost (water 25%) and inoculum mushroom (Product name: Noriaki Ikeda (Manufactured No. 305, Kamihira 305, No. 305, Sadaki-cho, Nagano) Was added and the water adjusted to 50% was fermented. The experiment was performed for the number of days required to move the raw material by 60 cm / day by agitation once a day and dry it to a moisture content of 25%. The results are as follows.
Figure 2006116529
In B1, the moisture was absorbed from the lower surface, so that it did not become 30% or less even after 50 days maximum.

以上の実験から明らかなように対照区と実験区の間には大きな時間差が生じている。A1区とB1区との間は無限大の差となり、A2区とB2区との間においても4倍の時間的差が生じた。これが即コスト差と成り、微生物のエネルギー利用が生ゴミの乾燥技術に結びつかず、実用化ができなかった要因となっている。
B1区においては、土中の水分を、コンクリート床を通じて吸い上げ、常に原料と床の接地面は水分によって腐敗臭をもよおし、乾燥状態になることはない。そのため、土中の悪玉菌が上昇し、コンクリートの成分的特性と重なり、悪玉菌による腐敗発酵へと移行する。そのため、糸状菌やコロニーによる菌糸の発生は抑えられ、水分が分離せずに中にこもってしまう。以上の理由によって、中空床式発酵乾燥方法は最も理にかなった今までにない省エネ低コストの発酵乾燥方式と言える。
低温発酵で短期間に乾燥物製品となるため、有機廃棄物のリグニンや物質が分解消滅することなく、原形を残した発酵物となる。このため、家畜の敷料等としての発酵基材としても最適である。
As is clear from the above experiment, there is a large time difference between the control group and the experimental group. There was an infinite difference between the A1 ward and the B1 ward, and a four-fold time difference occurred between the A2 ward and the B2 ward. This immediately becomes a cost difference, and the use of microbial energy does not lead to garbage drying technology, which is a factor that could not be put to practical use.
In the B1 district, moisture in the soil is sucked up through the concrete floor, and the raw material and the ground contact surface of the floor always have a rotting odor due to moisture and never become dry. Therefore, bad bacteria in the soil rise, overlap with the component characteristics of concrete, and shift to rot fermentation by bad bacteria. Therefore, the generation of mycelia due to filamentous fungi and colonies is suppressed, and moisture is trapped inside without being separated. For the above reasons, the hollow bed fermentation drying method is the most reasonable and energy-saving and low-cost fermentation drying method that has never been made before.
Since it becomes a dry product in a short period of time by low-temperature fermentation, the organic waste lignin and substances do not decompose and disappear, resulting in a fermented product that retains its original form. For this reason, it is optimal as a fermentation base material for livestock bedding and the like.

次に、実施例2について、実験結果を表と共に詳細に説明する。
実施例1で生産されたA1区、A2区、B1区、B2区の各発酵物を肥料として用い、野沢菜の栽培試験を行った。試験圃場は、野沢菜の根こぶ病の特にひどい圃場で、1坪ずつに4区画に分けた。周りからは外部の水が流れ込まないよう、深さ50cmの溝を掘り分離した。それによって、周りからの病原菌の新たな進入を防いだ。各区に10kgの発酵物を散布し、土中で混合した。10日後に再度撹拌のため耕起し、散布後20日後に播種した。参考区としてC区を設け、根こぶ病対策の土壌消毒剤「フロンサイド」(商品名:全農の販売品)を10アール当たり20kg散布して一般農家の慣行法で栽培を行った。いずれも播種後40日で収穫した結果は下記の通りである。

Figure 2006116529
A1区とA2区の実験区は完全に根こぶ病害が完治した。なお、C区の参考区は、病気にはなったが収穫ができた。農薬効果と思われる。 Next, about Example 2, an experimental result is demonstrated in detail with a table | surface.
Using the fermented products of A1, A2, B1, and B2 produced in Example 1 as fertilizers, Nozawana's cultivation test was conducted. The test field was a particularly terrible field of Nozawana's root-knot disease and was divided into 4 sections per square meter. A groove having a depth of 50 cm was dug and separated so that external water did not flow from the surroundings. This prevented new pathogens from entering. 10 kg of fermented material was sprayed on each section and mixed in soil. Ten days later, it was cultivated again for stirring and sown 20 days after spraying. C ward was established as a reference ward, and soil disinfectant “Fronside” (trade name: sold by all farmers) for root-knot disease was sprayed at 20 kg per 10 ares and cultivated in accordance with the general farming method. The results of harvesting 40 days after sowing are as follows.
Figure 2006116529
The A1 and A2 experimental plots were completely cured from the root-knot disease. In addition, although the reference zone of C district became ill, it was able to harvest. It seems to be a pesticide effect.

次に、実施例3について、実験結果を添付図面及び表と共に詳細に説明する。
実施例1のA1区及びA2区のロータリー式発酵乾燥機を、実験区A3区の施設とし、一般堆肥製造機であるスクープ式発酵機を対照区B3の施設とする。図5はB3区の施設を説明する斜視図である。図5に示すように、対照区B3の原料20の堆積高さは150cmとなっている。また、対照区B3の壁はコンクリートで形成されている。
一日の投入量4立方メートルに統一して発酵乾燥速度の比較試験を行った。なお、対照区B3区は下面から空気を挿入した。
原料は両区とも、家庭の生ゴミ1立方メートル(水分80%)、エノキ廃培地2立方メートル(水分50%)、豚糞1立方メートル(水分68%)、戻し堆肥0.5立方メートル(水分30%)、キノコーソ(商品名:池田農興(長野県埴科郡坂城町大字上平305番地44−17号)の製造品)20kg(水分25%)を混合したところ、水分が61%になった。それを施設の違いを除いて同じ条件の下で同時に試験を開始した。
ちなみに、A3区の施設費は350万円、B3区の施設費は1050万円である。結果は下記の通りである。

Figure 2006116529
Next, about Example 3, an experimental result is demonstrated in detail with an accompanying drawing and a table | surface.
The rotary fermentation dryers in the A1 and A2 zones of Example 1 are set as the facilities in the experimental zone A3, and the scoop type fermenter that is a general compost manufacturing machine is set as the control zone B3. FIG. 5 is a perspective view for explaining a facility in B3. As shown in FIG. 5, the deposition height of the raw material 20 in the control section B3 is 150 cm. Further, the wall of the control section B3 is made of concrete.
A fermentative drying rate comparison test was conducted with a daily input of 4 cubic meters. In the control group B3, air was inserted from the lower surface.
In both areas, the raw materials are 1 cubic meter of household garbage (80% moisture), 2 cubic meters of enoki waste medium (50% moisture), 1 cubic meter of pig manure (68% moisture), and 0.5 cubic meters of back compost (30% moisture). , Mushroom sono (product name: Ikeda Norioki (manufactured by No. 305, Kamihira, No. 305, 44-17, Sakagi-machi, Tateshina-gun, Nagano)) was mixed with 20 kg (water content: 25%), and the water content became 61%. It was started simultaneously under the same conditions except for the difference in facilities.
By the way, the facility cost of A3 ward is 3.5 million yen, and the facility cost of B3 ward is 10.5 million yen. The results are as follows.
Figure 2006116529

以上の実験結果から見ると、A3区は水分が60%以上の物でもわずか5日間の延長で水分を25%まで低下させることが可能である。堆積層を150cmとしたB3区においては、下からの水分の吸い上げは少ない。よって、80日で水分30%まで乾燥させることは可能であるが、それ以下に乾燥することは困難である。これは、発酵温度が下がって、堆積層が厚いことも重なって、水分の放散が激減するためであり、80日以上における水分の下降は困難であることが理解できる。また、コスト面からも施設費は3倍の差があり、水分30%以下にすることができないことは、別工程で乾燥工程が必要となり、更にコストと時間を必要とする。A3区の実験結果は問題化している生ゴミの資源化における無限の可能性を引き出す新技術である。   From the above experimental results, it is possible to reduce the water content to 25% in the A3 section even if the water content is 60% or more by extending only 5 days. In B3 section with a deposited layer of 150 cm, there is little uptake of moisture from below. Therefore, it is possible to dry to a moisture of 30% in 80 days, but it is difficult to dry below that. This is due to the fact that the fermentation temperature is lowered and the accumulated layer is also overlapped, so that the diffusion of moisture is drastically reduced, and it can be understood that it is difficult to lower the moisture after 80 days. In addition, there is a three-fold difference in facility costs from the viewpoint of cost, and the fact that the moisture content cannot be reduced to 30% or less requires a drying process as a separate process, and further requires cost and time. The result of the experiment in A3 is a new technology that draws infinite possibilities in the recycling of garbage that is a problem.

次に、実施例4について、実験結果を表と共に詳細に説明する。
実施例3で生産された実験区A3及びB3の各発酵物を肥料として用い、野沢菜の栽培試験を行った。試験圃場は、実施例2と同じ圃場で、特に根こぶ病の障害の出ている畑である。1坪ずつの2区画:A4区、B4区に分け、参考区としてC区を設け、慣行栽培での試験を行った。
周りからは外部の水が流れ込まないよう、深さ50cmの溝を掘った。A4区とB4区は各区の発酵物をそれぞれ10kg散布撹拌して10日後に再度耕起し、散布20日後に播種した。参考区C区は根こぶ病の土壌障害対策として「フロンサンド(商品名:全農の販売品)」を10アール当たり20kg散布して慣行法でおこなった。収穫は播種後40日であった。結果は下記の通りである。

Figure 2006116529
A区は18%の根こぶ病が発生した。実施例2で完治したものと比較すると、水分の多い場合は良い発酵ができないと考えられる。
B区及びC区も病気には勝てない。同じ種菌を入れても環境条件を変えるとその菌が働かないことがわかる。 Next, about Example 4, an experimental result is demonstrated in detail with a table | surface.
Using the fermented products of the experimental sections A3 and B3 produced in Example 3 as fertilizers, Nozawana's cultivation test was conducted. The test field is the same field as in Example 2, and is a field that is particularly affected by clubroot disease. Two sections of 1 tsubo each were divided into A4 ward and B4 ward, C ward was provided as a reference ward, and a test in conventional cultivation was performed.
A 50 cm deep groove was dug so that outside water would not flow from the surroundings. In A4 and B4, 10 kg of each fermented product was sprinkled and stirred, plowed again 10 days later, and seeded 20 days after spraying. In the Reference Zone C, “Freon Sand” (trade name: all agricultural products sold) was sprayed at 20 kg per 10 ares as a measure for soil damage caused by clubroot. Harvest was 40 days after sowing. The results are as follows.
Figure 2006116529
In District A, 18% of clubroot occurred. Compared with what was completely cured in Example 2, when there is much water | moisture content, it is thought that good fermentation cannot be performed.
B and C wards can't beat the disease. It can be seen that even if the same inoculum is added, it does not work if the environmental conditions are changed.

次に、実施例5について、実験結果を詳細に説明する。
実験区A5:鶏糞(水分72%)100kgに対し、コーンコブミール(水分14%)30kgの割合で水分59%に調整した。
対照区B5:鶏糞(水分72%)100kgに対し、松のオガ粉(水分14%)30kgの割合で水分59%に調整した。
上記のように実験区A5、対照区B5を設け、どちらも実施例1のA区のハウス型乾燥機で、30mの距離を1日二回の撹拌によって原料を120cm/日移動させ、22日目における乾燥状態について試験を行った。結果は下記の通りである。
A5区:22日目の水分が24%、B5区:22日目の水分が32%。
以上の結果から水分の乾燥度はコーンコブミールを水分調整材として使用した場合、今までの水分調整材のオガ粉よりも効率的に乾燥できることがわかった。
Next, the experimental results of Example 5 will be described in detail.
Experimental group A5: 100 kg of chicken manure (water content 72%) was adjusted to a moisture content of 59% at a ratio of 30 kg of corn cobmeal (water content 14%).
Control group B5: 100 kg of chicken manure (water 72%) was adjusted to 59% water at a ratio of 30 kg of pine sawdust (14% water).
As described above, the experimental section A5 and the control section B5 are provided, both of which are house-type dryers in the section A of Example 1, and the material is moved 120 cm / day by stirring twice a day at a distance of 30 m, 22 days Tests were performed for dryness in the eyes. The results are as follows.
A5 district: 24% moisture on the 22nd day, B5 district: 32% moisture on the 22nd day.
From the above results, it was found that when corn cob meal was used as a moisture conditioner, the moisture dryness could be dried more efficiently than the conventional moisture conditioner sawdust.

以上、本発明につき好適な実施例を挙げて種々説明してきたが、本発明はこの実施例に限定されるものではなく、発明の精神を逸脱しない範囲内で多くの改変を施し得るのは勿論のことである。   As described above, the present invention has been described in various ways with reference to preferred embodiments. However, the present invention is not limited to these embodiments, and it goes without saying that many modifications can be made without departing from the spirit of the invention. That is.

本発明にかかる有機廃棄物の発酵乾燥施設を示す斜視図である。It is a perspective view which shows the fermentative drying facility of the organic waste concerning this invention. 図1の発酵乾燥施設の側面図である。It is a side view of the fermentation drying facility of FIG. 図1の発酵乾燥施設の対照試験に用いた施設を示す斜視図である。It is a perspective view which shows the plant | facility used for the control test of the fermentation drying facility of FIG. 図3の発酵乾燥施設の側面図である。It is a side view of the fermentation drying facility of FIG. 一般堆肥製造機であるスクープ式発酵機の施設を示す斜視図である。It is a perspective view which shows the facility of the scoop type fermenter which is a general compost manufacturing machine.

符号の説明Explanation of symbols

10 ビニールハウス
12 床板部
15 中空
20 原料
30 ロータリー型のかき混ぜ装置
DESCRIPTION OF SYMBOLS 10 Greenhouse 12 Floor board part 15 Hollow 20 Raw material 30 Rotary type stirring apparatus

Claims (12)

有機廃棄物等の有機物を発酵槽内で発酵させて乾燥させる方法において、
前記発酵槽の床部を、木材、炭化物、セラミック又はプラスチックのいずれか一又は組合せによる床材で設け、該床材と床材の隙間を接着剤等で埋めないで空気の通路を作り、ロータリー型回転刃を備える装置等で前記床部上の前記有機物の切り返しと移動を同時に行い、該有機物を発酵させて乾燥処理することを特徴とする有機物の乾燥方法。
In a method of fermenting organic matter such as organic waste in a fermenter and drying,
The floor portion of the fermenter is provided with a floor material made of any one or a combination of wood, carbide, ceramic or plastic, and an air passage is formed without filling the gap between the floor material and the floor material with an adhesive, etc. A method for drying an organic material, comprising: simultaneously turning and moving the organic material on the floor with an apparatus having a mold rotary blade, etc., fermenting the organic material, and drying the organic material.
前記有機物は、コーンコブミール又はその発酵物が混合されていることを特徴とする請求項1記載の有機物の乾燥方法。   2. The organic matter drying method according to claim 1, wherein the organic matter is mixed with corn cob meal or a fermented product thereof. 有機廃棄物にコーンコブミール又はその発酵物を混入し、水分30〜80%に調整して有機物原料とし、下側に中空空間が床面積の30%以上を占めるように設けられた中空床を備える発酵槽を作り、該中空床の上側に前記原料を20cm〜120cmの高さに積み上げ、上側と下側へ同時に空気を取り入れるように環境条件を作り、切り返し発酵乾燥を行うことを特徴とする有機物の乾燥方法。   Corn waste meal or fermented product thereof is mixed into organic waste, adjusted to a moisture content of 30 to 80%, and used as an organic raw material, and provided with a hollow floor provided so that the hollow space occupies 30% or more of the floor area on the lower side An organic substance characterized by making a fermenter, stacking the raw material at a height of 20 cm to 120 cm on the upper side of the hollow floor, creating environmental conditions so that air is simultaneously taken into the upper side and the lower side, and performing reverse fermentation drying Drying method. 有機廃棄物に重量比で5〜60%のコーンコブミールを混合して前記有機物原料とすることを特徴とする請求項3記載の有機物の乾燥方法。   The organic waste drying method according to claim 3, wherein 5 to 60% by weight of corn cob meal is mixed with the organic waste to obtain the organic raw material. 請求項1、2、3又は4記載の有機物の乾燥方法によって製造したことを特徴とする発酵飼料又は有機質肥料。   A fermented feed or organic fertilizer produced by the method for drying organic matter according to claim 1, 2, 3 or 4. 前記有機物に栄養素を加え、請求項1、2、3又は4記載の有機物の乾燥方法によって製造したことを特徴とする発酵飼料。   A fermented feed produced by adding a nutrient to the organic matter and producing the organic matter according to claim 1, 2, 3 or 4. 前記有機物に栄養素やミネラルを加え、請求項1、2、3又は4記載の有機物の乾燥方法によって製造したことを特徴とする有機質肥料。   An organic fertilizer produced by adding nutrients and minerals to the organic matter and producing the organic matter according to claim 1, 2, 3 or 4. 請求項1、2、3又は4記載の有機物の乾燥方法によって製造したことを特徴とする畜産用の敷料又は病害対策資材。   A livestock bedding or disease control material produced by the method for drying organic matter according to claim 1, 2, 3 or 4. 請求項1、2、3又は4記載の有機物の乾燥方法によって製造したことを特徴とする農作物の病虫害対策資材。   A disease and pest control material for agricultural crops produced by the method for drying organic matter according to claim 1, 2, 3 or 4. 請求項1、2、3又は4記載の有機物の乾燥方法によって製造したことを特徴とするダイオキシン、残留農薬、又は亜硝酸態窒素等の土壌中に含まれる有害物質の分解剤。   A decomposition agent for harmful substances contained in soil such as dioxin, residual agricultural chemicals, or nitrite nitrogen, which is produced by the method for drying organic matter according to claim 1, 2, 3 or 4. 請求項5、6、7、8、9、10に記載された発酵飼料又は有機質肥料等の発酵物で発酵されたことを特徴とする肥料又は飼料。   A fertilizer or feed fermented with a fermented material such as a fermented feed or an organic fertilizer according to claim 5, 6, 7, 8, 9, or 10. 有機廃棄物等の有機物を発酵槽内で発酵させて乾燥させる有機物の乾燥装置において、
前記発酵槽内に、木材、炭化物、セラミック又はプラスチックのいずれか一又は組合せによる床材で設けられた床部と、該床部の前記床材と床材の隙間を接着剤等で埋めないことで形成された空気の通路と、前記床部上の前記有機物の切り返しと移動を同時に行うようにロータリー型回転刃を備える有機物の撹拌移動装置が設けられたことを特徴とする有機物の乾燥装置。
In an organic matter drying apparatus for fermenting and drying organic matter such as organic waste in a fermenter,
In the fermenter, do not fill the gap between the floor material provided with a floor material made of any one or a combination of wood, carbide, ceramic or plastic with the adhesive or the like. An organic matter drying apparatus provided with an organic matter stirring and moving device provided with a rotary-type rotary blade so that the air passage formed in step 1 and the organic matter on the floor portion are turned back and moved simultaneously.
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