JP2009167063A - Method of composting organic waste and apparatus therefor - Google Patents

Method of composting organic waste and apparatus therefor Download PDF

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JP2009167063A
JP2009167063A JP2008008738A JP2008008738A JP2009167063A JP 2009167063 A JP2009167063 A JP 2009167063A JP 2008008738 A JP2008008738 A JP 2008008738A JP 2008008738 A JP2008008738 A JP 2008008738A JP 2009167063 A JP2009167063 A JP 2009167063A
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hot air
deodorizing
organic waste
combustion
composting
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Manabu Hidaka
学 桧高
Masamitsu Nakagawa
正光 中川
Akio Mukai
章夫 向井
Takashi Kashiwamura
崇 柏村
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Satake Engineering Co Ltd
Satake Corp
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Satake Engineering Co Ltd
Satake Corp
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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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method of composting organic wastes which can be suitably used for saving the consumption of fossil fuels largely and for cutting down on the running cost and an apparatus therefor. <P>SOLUTION: The method of composting organic wastes comprises a maturing and fermenting step of maturing and fermenting organic wastes such as dung and kitchen garbage, a deodorizing step of recovering malodor gases occurring at the maturing and fermenting step and to deodorize the gases by adsorbing them in a deodorizer, and a pre-drying step preceding the maturing and fermenting step of vaporizing the moisture in the organic wastes using hot air produced in a hot air chamber in order to prepare the conditions suited for the fermentation. The heat source for the hot air used in the pre-drying step is the heat of combustion generated by burning the deodorizer which have lost deodorizing ability as it adsorbed the malodor gases at the deodorizing step. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

本発明は、有機廃棄物の堆肥化処理方法およびその装置に関する。 The present invention relates to a method and apparatus for composting organic waste.

従来、家畜の糞尿や生ゴミ等の有機廃棄物は、堆肥化処理して再び肥料として利用されている。堆肥化処理には、堆積式(有機廃棄物に籾殻などの水分調整剤を混合して水分60〜70%に調整し、これを堆積させて自然発酵、腐熟させる方式)や、機械的攪拌式(有機廃棄物に熱風を送風しながら攪拌して好気的発酵を施し、この発酵熱によって有機廃棄物中の水分を蒸発させて発酵させる方式)などが知られている(例えば、特許文献1参照)。しかしながら、堆積式にあっては、家畜の糞尿におが屑や籾殻などを混合させて堆積させるので、その容量が大きくなり、広い保管場所が必要となる問題がある。また、攪拌式にあっては、熱風を生成するための重油バーナを使用しており、昨今の化石燃料の高騰などにより、大幅にランニングコストがかかる問題がある。 Conventionally, organic waste such as livestock manure and garbage is composted and reused as fertilizer. For composting, there is a sedimentation method (a method in which organic waste is mixed with a moisture adjusting agent such as rice husk to adjust the moisture to 60-70%, and this is deposited and naturally fermented and matured), or a mechanical stirring method (A method in which organic waste is stirred while blowing hot air to perform aerobic fermentation, and water in the organic waste is evaporated and fermented by the heat of fermentation) is known (for example, Patent Document 1). reference). However, the accumulation type has a problem in that it increases the capacity and necessitates a wide storage place because the wastes and rice husks are mixed and accumulated in the excrement of livestock. Moreover, in the stirring type, a heavy oil burner for generating hot air is used, and there is a problem that a running cost is greatly increased due to a recent rise in fossil fuel.

一方、バイオマスを利用した熱風発生炉も周知であるが、燃料となるバイオマス原料は水分40〜50%の高水分であり、熱風発生炉の前段において別途乾燥装置を設けて、温度100〜300℃で加熱して原料を乾燥させなければ着火して燃焼させることができず、原料を乾燥するためにバーナに供する重油などの化石燃料が必要であった(特許文献2参照)。 On the other hand, although a hot air generating furnace using biomass is also well known, the biomass raw material used as fuel has a high water content of 40 to 50%, and a separate drying device is provided at the front stage of the hot air generating furnace, and the temperature is 100 to 300 ° C. If the raw material was not dried by heating at 1, it could not be ignited and burned, and fossil fuel such as heavy oil to be used for the burner was necessary to dry the raw material (see Patent Document 2).

特開2005-231912号公報JP 2005-231912 A 特開2006-328326号公報JP 2006-328326 A

本発明は上記問題点にかんがみ、化石燃料の使用を大幅に削減し、ランニングコストを低減することが可能な堆肥化処理方法およびその装置を提供することを技術的課題とする。 In view of the above problems, it is a technical object of the present invention to provide a composting method and apparatus capable of significantly reducing the use of fossil fuels and reducing running costs.

上記課題を解決するため請求項1記載の発明は、家畜の糞尿や生ゴミ等の有機廃棄物を熟成発酵処理する熟成発酵工程と、該熟成発酵工程で生じる臭気ガスを回収して脱臭剤により吸着・脱臭処理する脱臭工程と、前記熟成発酵工程の前工程に、熱風発生室にて生成した熱風を用いて前記有機廃棄物の水分を蒸発させ、発酵条件を整える乾燥前処理工程と、を具備した有機廃棄物の堆肥化処理方法であって、前記乾燥前処理工程で使用する熱風の熱源として、前記脱臭工程にて臭気ガスを吸着・脱臭処理した後の脱臭能力が低下した脱臭剤を燃焼したときの燃焼熱を利用する、という技術的手段を講じた。 In order to solve the above-mentioned problems, the invention according to claim 1 is an aging fermentation process for subjecting organic waste such as livestock manure and garbage to an aging fermentation process, and recovering odorous gas generated in the aging fermentation process by using a deodorizing agent. A deodorization step for adsorption / deodorization treatment, and a pre-drying treatment step for adjusting the fermentation conditions by evaporating the moisture of the organic waste using hot air generated in a hot-air generating chamber in the pre-step of the aging fermentation step. An organic waste composting method comprising a deodorizer having reduced deodorizing ability after adsorbing and deodorizing odorous gas in the deodorizing step as a heat source of hot air used in the pre-drying processing step. Technical measures were taken to use the heat of combustion when burned.

また、請求項2記載の発明は、前記脱臭剤は、木の樹皮を粉砕したバークチップ、籾殻又はおが屑チップなどの木質系バイオマスとなし、前記乾燥前処理工程で使用する熱風の熱源として、前記脱臭工程にて吸着・脱臭処理した後の水分25%未満に低下した脱臭剤を燃焼したときの燃焼熱を利用することを特徴とする。 Moreover, the invention according to claim 2 is characterized in that the deodorizer is made of woody biomass such as bark chips, rice husks or sawdust chips obtained by pulverizing tree bark, and as a heat source of hot air used in the drying pretreatment process, It is characterized by utilizing the heat of combustion when burning the deodorizer whose water content has decreased to less than 25% after the adsorption / deodorization process in the deodorization step.

さらに、請求項3記載の発明は、前記脱臭剤を燃焼したときの燃焼灰を、前記乾燥前処理工程にて処理中の有機廃棄物に水分調整剤として混合することを特徴とする。 Further, the invention according to claim 3 is characterized in that the combustion ash produced by burning the deodorizer is mixed as a moisture adjusting agent with the organic waste being treated in the pre-drying treatment step.

そして、堆肥化処理装置としての請求項4記載の発明は、家畜の糞尿や生ゴミ等の高水分の有機廃棄物に熱風を送風しながら攪拌して水分を蒸発させて発酵条件を整える乾燥機(2)と、水分を蒸発させた後の低水分の有機廃棄物を熟成発酵処理する熟成発酵機(3)と、該熟成発酵機(3)で生じた臭気ガスを回収して脱臭剤により吸着・脱臭処理する脱臭槽(4)と、を備えた有機廃棄物の堆肥化処理装置であって、前記乾燥機(2)の前工程には、前記脱臭槽(4)にて臭気ガスを吸着・脱臭処理した後の脱臭能力が低下した脱臭剤をバイオマス燃料とするバイオマス熱風発生炉(5)を備えたことを特徴とする。 The invention according to claim 4 as a composting treatment apparatus is a dryer for adjusting fermentation conditions by evaporating water by stirring while blowing hot air to high-moisture organic waste such as livestock manure and garbage (2), an aging fermenter (3) for aging and fermenting low-moisture organic waste after evaporating water, and recovering odorous gas generated in the aging fermenter (3) by using a deodorizing agent An organic waste composting device equipped with a deodorizing tank (4) for adsorbing and deodorizing, wherein odor gas is introduced into the deodorizing tank (4) before the dryer (2). A biomass hot air generating furnace (5) using as a biomass fuel a deodorizing agent having reduced deodorizing ability after adsorption and deodorizing treatment is provided.

請求項1記載の発明によれば、熱風発生室にて生成した熱風を用いて前記有機廃棄物の水分を蒸発させ、発酵条件を整える乾燥前処理工程で使用する熱風の熱源として、前記脱臭工程にて臭気ガスを吸着・脱臭処理した後の脱臭能力が低下した脱臭剤を燃焼したときの燃焼熱を利用するものであり、温度400〜500℃、風量23〜25Nm/minの熱風を乾燥前処理工程に供給することが可能であり、該乾燥前処理工程では、例えば、有機廃棄物の品温を約70〜80℃程度に維持し、投入時に水分60〜70%であった有機廃棄物を、排出時には水分50〜60%まで乾減されるような乾燥が可能となる。このときの使用燃料の燃料効率を試算すれば、日量1tonの木質系バイオマスからなる脱臭剤を原料とする熱風発生炉において、温度400〜500℃の熱風として取り出される熱量は約10000MJであり、A重油に換算して256リットル必要であるのに対し、本発明の熱風発生炉のA重油の使用量はおおよそ着火に必要なエネルギのみとなるために1リットル程度でよく、A重油の使用量を約99%以上節減することができ、化石燃料の使用を削減し、ランニングコストを低減することが可能となる。 According to invention of Claim 1, the deodorizing process is used as a heat source of the hot air used in the pre-drying process used to evaporate the moisture of the organic waste using the hot air generated in the hot air generating chamber and to adjust the fermentation conditions. It uses the heat of combustion when burning a deodorant with reduced deodorizing ability after adsorbing and deodorizing odorous gas at a temperature, drying hot air at a temperature of 400 to 500 ° C. and an air volume of 23 to 25 Nm 3 / min. It is possible to supply to the pretreatment process. In the drying pretreatment process, for example, the organic waste is maintained at a temperature of about 70 to 80 ° C., and the organic waste has a moisture content of 60 to 70% at the time of charging. When the product is discharged, it can be dried so that the moisture content is reduced to 50 to 60%. If the fuel efficiency of the fuel used at this time is estimated, the amount of heat extracted as hot air at a temperature of 400 to 500 ° C. is about 10,000 MJ in a hot air generating furnace using a deodorizer made of woody biomass of 1 ton per day as a raw material. While 256 liters are required in terms of A heavy oil, the amount of A heavy oil used in the hot-air generator of the present invention is only about 1 liter because it is only energy required for ignition. About 99% or more can be saved, the use of fossil fuel can be reduced, and the running cost can be reduced.

請求項2記載の発明によれば、前記脱臭剤は、木の樹皮を粉砕したバークチップ、籾殻又はおが屑チップなどの木質系バイオマスとなし、前記乾燥前処理工程で使用する熱風の熱源として、前記脱臭工程にて吸着・脱臭処理した後の水分25%未満に低下した脱臭剤を燃焼したときの燃焼熱を利用するので、例えば、使用済の脱臭剤は水分10%,見掛け密度200Kg/mとなっており、一般的なバイオマス熱風発生炉で使用されるバイオマス原料の水分(例えば、水分40〜50%)よりも低く、着火性がよく、前工程に何ら乾燥処理を必要とせず、直ちにバイオマス燃料として用いることができ、更なるランニングコストの低減が可能となる。 According to the invention described in claim 2, the deodorizer is made of woody biomass such as bark chips, rice husks or sawdust chips obtained by pulverizing tree bark, and as a heat source of hot air used in the drying pretreatment process, For example, the used deodorizer has a water content of 10% and an apparent density of 200 kg / m 3 because it uses the heat of combustion of the deodorizer that has been reduced to a water content of less than 25% after adsorption / deodorization treatment in the deodorization process. It is lower than the moisture (for example, moisture 40-50%) of the biomass raw material used in a general biomass hot air generator, has good ignitability, and does not require any drying treatment in the previous process, immediately It can be used as a biomass fuel, and the running cost can be further reduced.

さらに、請求項3記載の発明は、前記脱臭剤を燃焼したときの燃焼灰を、前記乾燥前処理工程にて処理中の有機廃棄物に水分調整剤として混合するものであり、脱臭剤を燃焼したときの副産物である燃焼灰を廃棄することなく、有効利用することが可能となる。 Furthermore, the invention according to claim 3 mixes the combustion ash produced when the deodorizer is burned with the organic waste being processed in the pre-drying treatment step as a moisture regulator, and burns the deodorizer. It is possible to effectively use the combustion ash, which is a by-product when the product is discarded, without being discarded.

また、請求項4記載の発明は、家畜の糞尿や生ゴミ等の高水分の有機廃棄物に熱風を送風しながら攪拌して水分を蒸発させて発酵条件を整える乾燥機(2)と、水分を蒸発させた後の低水分の有機廃棄物を熟成発酵処理する熟成発酵機(3)と、該熟成発酵機(3)で生じた臭気ガスを回収して脱臭剤により吸着・脱臭処理する脱臭槽(4)と、を備えた有機廃棄物の堆肥化処理装置であって、前記乾燥機(2)の前工程には、前記脱臭槽(4)にて臭気ガスを吸着・脱臭処理した後の脱臭能力が低下した脱臭剤をバイオマス燃料とするバイオマス熱風発生炉(5)を備えた堆肥化処理装置であり、脱臭槽(4)での使用済の脱臭剤をバイオマス熱風発生炉(5)の燃料として有効利用すること、及びバイオマス熱風発生炉(5)での燃焼後の燃焼灰を乾燥機(2)に投入して、処理中の有機廃棄物の水分調整剤として有効利用することが可能となり、廃棄予定の脱臭剤及び燃焼灰からなる副産物を有効利用して循環型の堆肥化処理装置を実現することが可能となる。 Further, the invention described in claim 4 includes a drier (2) that adjusts fermentation conditions by evaporating water by stirring hot air to a high-moisture organic waste such as livestock manure and garbage, and moisture. Aged fermenter (3) for aging and fermenting low-moisture organic waste after evaporating odor, and deodorizing for recovering odorous gas generated in the aged fermenter (3) and adsorbing and deodorizing with a deodorizer An organic waste composting apparatus comprising a tank (4), wherein the odor gas is adsorbed and deodorized in the deodorizing tank (4) before the dryer (2). This is a composting device equipped with a biomass hot air generator (5) using biomass as a deodorant whose deodorizing ability has been reduced, and used deodorizer in the deodorizing tank (4) as a biomass hot air generator (5) After being burned in a biomass hot air generator (5) Combustion ash can be put into the dryer (2) for effective use as a water conditioner for organic waste during processing. By-products consisting of deodorizers and combustion ash to be disposed of can be used effectively to circulate. It becomes possible to realize a composting apparatus.

以下、本発明を実施するための最良の一実施形態について図面を参照して説明する。図1は本発明の堆肥化処理方法およびその装置の実施の一形態を示す概要図であり、家畜の糞尿や生ゴミ等の高水分の有機廃棄物1(wet)に熱風を送風しながら攪拌して水分を蒸発させて発酵条件を整える二軸式多目的乾燥機2と、水分を蒸発させた後の低水分の有機廃棄物1(dry)を熟成発酵処理する熟成発酵機3と、該熟成発酵機3で生じた臭気ガスを回収して脱臭剤により吸着・脱臭処理する脱臭槽4と、前記二軸式多目的乾燥機2の前工程に設けられ、該二軸式多目的乾燥機2に送り込む熱風を生成するため、籾殻,おが屑,木質チップなどのバイオマス燃料(再生可能な生物由来の有機性資源であって、化石燃料を除いたもの)を燃焼させて得られる熱を利用して熱風を生成するバイオマス熱風発生炉5と、を備えている。 DESCRIPTION OF EXEMPLARY EMBODIMENTS Hereinafter, an exemplary embodiment for carrying out the invention will be described with reference to the drawings. FIG. 1 is a schematic diagram showing an embodiment of the composting method and apparatus of the present invention, and stirring while blowing hot air to high-moisture organic waste 1 (wet) such as livestock manure and garbage. The biaxial multi-purpose dryer 2 that evaporates moisture and adjusts the fermentation conditions, the aged fermenter 3 that aged and ferments the low-moisture organic waste 1 (dry) after evaporating the moisture, and the aging The odor gas generated in the fermenter 3 is collected and adsorbed and deodorized with a deodorizer, and is provided in a pre-process of the twin-screw multipurpose dryer 2 and fed into the twin-screw multipurpose dryer 2 In order to generate hot air, hot air is generated by using the heat obtained by burning biomass fuel such as rice husk, sawdust, and wood chips (renewable organic organic resources excluding fossil fuel). And a biomass hot-air generating furnace 5 to be generated.

上記二軸式多目的乾燥機2は、例えば、図1のように直方体状の機枠6内に形成した発酵処理槽7と、該処理槽7内に回転自在に支持される回転軸9と、該回転軸9に対して放射状に植設された多数の攪拌パドル8…と、前記処理槽7と機枠6の外殻との間に介装され、前記バイオマス熱風発生炉5から送給される熱風と前記処理槽(7)内の有機廃棄物との熱交換を行う熱交換部10と、を備えて構成される。前記発酵処理槽7は半円筒状ドラムを複数横設して、横断面を略W字状に形成した発酵処理槽7とするのが好ましく、この処理槽7の凹部長手方向にそれぞれ回転軸9を回転可能に軸架して二軸式の処理槽7とするとよい。
前記発酵処理槽7の上部には、有機廃棄物1(wet)の投入口11が、処理槽7の一側部下方には処理済みの有機廃棄物の排出口12がそれぞれ設けられ、各開口には、シリンダ等によって開閉自在に形成された開閉扉13,14が被着される。処理槽7の他側部には、前記回転軸9を回転駆動するギアモータ15が設けられる。また、処理槽7と機枠6の外殻との間に介装される熱交換部10は、処理槽7の底部7a側に設けた底部熱交換部10aと、処理槽7の横断面W字の両側面部7b,7b側にそれぞれ設けられる側面部側熱交換部10b,10bとからなり、機外から送給される熱風との熱交換が十分に行われるように構成されている。なお、符号16は機外から送給される熱風を供給するための熱風供給管であり、符号17は熱交換部10を通過した後の空気を排出する熱風排出管であり、符号18は機外から送給される熱風を熱交換部10に導入し、かつ、排気を行うための吸引排気ファンである。
The biaxial multipurpose dryer 2 includes, for example, a fermentation treatment tank 7 formed in a rectangular parallelepiped machine frame 6 as shown in FIG. 1, a rotating shaft 9 that is rotatably supported in the treatment tank 7, and A large number of stirring paddles 8, which are radially installed on the rotating shaft 9, are interposed between the treatment tank 7 and the outer shell of the machine frame 6, and are fed from the biomass hot air generating furnace 5. And a heat exchanging unit 10 that performs heat exchange between the hot air and the organic waste in the treatment tank (7). The fermentation treatment tank 7 is preferably a fermentation treatment tank 7 in which a plurality of semicylindrical drums are provided horizontally and the cross section is formed in a substantially W shape. It is preferable to mount the shaft 9 so as to be rotatable to form a biaxial treatment tank 7.
An organic waste 1 (wet) inlet 11 is provided at the top of the fermentation treatment tank 7, and a treated organic waste outlet 12 is provided below one side of the treatment tank 7. Opening and closing doors 13 and 14 formed to be openable and closable by a cylinder or the like are attached. A gear motor 15 that rotationally drives the rotary shaft 9 is provided on the other side of the processing tank 7. Moreover, the heat exchange part 10 interposed between the processing tank 7 and the outer shell of the machine casing 6 includes a bottom heat exchange part 10a provided on the bottom part 7a side of the processing tank 7, and a cross section W of the processing tank 7. It is comprised from the side part side heat exchange part 10b, 10b each provided in the both-sides surface part 7b, 7b side of a character, and it is comprised so that heat exchange with the hot air supplied from the outside of an apparatus may fully be performed. Reference numeral 16 is a hot air supply pipe for supplying hot air supplied from outside the apparatus, reference numeral 17 is a hot air discharge pipe for discharging air after passing through the heat exchanging section 10, and reference numeral 18 is a machine. It is a suction exhaust fan for introducing hot air fed from outside into the heat exchanging unit 10 and exhausting.

二軸式多目的乾燥機2の前工程に設けられるバイオマス熱風発生炉4は、機枠19内に耐火煉瓦等の耐火物を使用して築造(築炉)された横型円筒状の燃焼炉20と、該燃焼炉20内に供給されたバイオマス燃料に着火を行うためのガンタイプバーナ21と、前記燃焼炉20内部へ燃焼空気を供給する燃焼空気供給管22と、該燃焼空気供給管22を囲繞するように配設され、熱風発生炉4全体を空冷するための冷却管23と、で構成され、前記燃焼炉20の一端には、バイオマス燃料を燃焼炉20内に繰り出すための燃料供給機24が配設され、他端側には、バイオマス燃料を燃焼させる際に生じる熱風と燃焼灰とをそれぞれ回収する分離室25が配設される。該分離室25の下部には燃焼灰を回収するための回収ホッパー26及び排出スクリュー27が設けられ、回収ホッパー26の下流側には、燃焼灰を機外に搬出するための搬送スクリュー28が連絡されている。
一方、分離室25の上部には熱風を回収するためのフード状の排気ダクト29が設けられ、該排気ダクト29の下流側には、回収した熱風から微細粉塵を分離・除去するためのサイクロン30が連絡されている。符号31は前記冷却管23内の空気を吸気するとともに、前記燃焼空気供給管22内及び排気ダクト29内にそれぞれ送風する送風ファンであり、符号32は前記排出スクリュー27の熱変形を防止すべく、排出スクリュー27の中空部に通水を行って水冷を行うためのクーリングタワーであり、符号33はバイオマス燃料の貯留ホッパーである。
The biomass hot air generating furnace 4 provided in the pre-process of the biaxial multipurpose dryer 2 includes a horizontal cylindrical combustion furnace 20 built (built) using a refractory material such as refractory bricks in a machine frame 19. A gun type burner 21 for igniting the biomass fuel supplied into the combustion furnace 20, a combustion air supply pipe 22 for supplying combustion air into the combustion furnace 20, and surrounding the combustion air supply pipe 22 And a cooling pipe 23 for air-cooling the entire hot air generating furnace 4, and a fuel supply machine 24 for feeding biomass fuel into the combustion furnace 20 at one end of the combustion furnace 20. And a separation chamber 25 for collecting hot air and combustion ash generated when the biomass fuel is burned, respectively, is disposed on the other end side. A recovery hopper 26 and a discharge screw 27 for recovering the combustion ash are provided at the lower part of the separation chamber 25, and a conveying screw 28 for carrying the combustion ash out of the apparatus communicates with the downstream side of the recovery hopper 26. Has been.
On the other hand, a hood-like exhaust duct 29 for collecting hot air is provided in the upper part of the separation chamber 25, and a cyclone 30 for separating and removing fine dust from the collected hot air is provided downstream of the exhaust duct 29. Has been contacted. Reference numeral 31 denotes a blower fan that sucks air in the cooling pipe 23 and blows air into the combustion air supply pipe 22 and the exhaust duct 29, respectively, and reference numeral 32 denotes to prevent thermal deformation of the discharge screw 27. A cooling tower for passing water through the hollow portion of the discharge screw 27 for water cooling. Reference numeral 33 denotes a biomass fuel storage hopper.

前記二軸式多目的乾燥機2の後工程に設けられ、低水分の有機廃棄物を熟成発酵処理する熟成発酵機3は、例えば、図1のように、発酵槽34と、該発酵槽34に設けられて原料を投入するための一端側の原料投入部35と、堆肥が搬出される他端側の堆肥搬出部36と、投入された堆肥を攪拌するためのロータリー撹拌機37と、建家38などから構成されている。
発酵槽34は、低水分の有機廃棄物1(dry)を堆積するためにコンクリート製の長い溝形状をなしており、該発酵槽34の長手方向に沿って固定されるレールが設けられ、該レール上にロータリー攪拌機37が搭載される。そして、発酵槽34の底部には、堆積された有機廃棄物1(dry)に空気を供給して、発酵を促進するために空気供給ダクト39が敷設されている。この空気供給ダクト39には、送風機40が接続され、所定の圧力で空気が送出される構成となっている。
建家38は、発酵槽34の上方をフードなどで覆うことで構成され、発酵槽34の保温のほか、発酵の際に生じる悪臭空気などが外に出ないように多数の吸引ノズル41…が垂設され、さらに、該各吸引ノズル41…には、吸引ファン42と連絡した排気管43が接続されている。
An aging fermenter 3 that is provided in a subsequent process of the biaxial multipurpose dryer 2 and ripens and ferments low-moisture organic waste is, for example, a fermenter 34 and a fermenter 34 as shown in FIG. A raw material input unit 35 provided at one end for supplying raw materials, a compost carry-out unit 36 at the other end from which compost is carried out, a rotary stirrer 37 for stirring the input compost, and a building 38 or the like.
The fermenter 34 has a long groove shape made of concrete for depositing low-moisture organic waste 1 (dry), and a rail fixed along the longitudinal direction of the fermenter 34 is provided. A rotary stirrer 37 is mounted on the rail. An air supply duct 39 is laid at the bottom of the fermenter 34 to supply air to the deposited organic waste 1 (dry) and promote fermentation. A blower 40 is connected to the air supply duct 39 so that air is sent out at a predetermined pressure.
The building 38 is configured by covering the top of the fermenter 34 with a hood or the like, and in addition to keeping the fermenter 34 warm, a number of suction nozzles 41 are provided so that odorous air generated during fermentation does not go outside. Further, an exhaust pipe 43 communicating with the suction fan 42 is connected to each of the suction nozzles 41.

前記脱臭槽4には、前記熟成発酵機3で生じた悪臭空気を槽体44の下方から送り込むよう、前記排気管43から分岐した多数の噴出管45…を、槽体44,44の底面部44a,44aに臨ませてある。そして、槽体44の内部には、下部に玉石や砂利又はスノコ等で空間部を形成し、その上にバーク(木の樹皮のチップ)、籾殻又はおが屑チップ等からなる脱臭剤47を約1〜2m堆積し、該脱臭剤47に悪臭空気が下方から送り込まれ、その堆積層を通過した後に大気へ放出されるように形成されている。なお、符号46は噴出管45…を閉鎖するための閉鎖弁である。この脱臭槽4において、例えば、脱臭剤47の堆積高さを約1m、見掛風速を2mm/秒とすると、悪臭空気と脱臭剤47とが接触する時間は500秒となり、悪臭空気のアンモニア濃度が300ppm程度であれば20日間位で脱臭剤47表面からアンモニアが検出され始め、以後、脱臭能力は低下することになる。また、見掛風速を10mm/秒,アンモニア濃度が300ppm程度であるとすれば4日間程度で脱臭剤47表面からアンモニアが検出し始めることになる。 The deodorizing tank 4 is provided with a number of jet pipes 45 branched from the exhaust pipe 43 so that malodorous air generated in the aging fermenter 3 is fed from below the tank body 44. 44a and 44a. Then, in the tank body 44, a space is formed in the lower part with cobblestone, gravel, slats, or the like, and a deodorant 47 made of bark (wood bark chips), rice husks or sawdust chips or the like is formed thereon for about 1 ˜2 m is deposited, and malodorous air is sent into the deodorizer 47 from below, and after passing through the deposited layer, it is formed so as to be released to the atmosphere. Reference numeral 46 is a closing valve for closing the ejection pipes 45. In this deodorization tank 4, for example, if the deposition height of the deodorant 47 is about 1 m and the apparent wind speed is 2 mm / second, the time of contact between the malodorous air and the deodorant 47 is 500 seconds, and the ammonia concentration of the malodorous air If it is about 300 ppm, ammonia starts to be detected from the surface of the deodorizer 47 in about 20 days, and thereafter the deodorizing ability is lowered. If the apparent wind speed is 10 mm / second and the ammonia concentration is about 300 ppm, ammonia starts to be detected from the surface of the deodorizer 47 in about 4 days.

図2は、本発明の実施形態の工程について模式的に示した図である。本実施形態において、家畜等から排出されるし尿等の汚水は、バキュームカー48によって回収され、これをスクリーンユニット49に搬送して汚水中のごみが除去され、次いで、一時貯留槽50に貯留して曝気処理が行われ、好気性条件を作成して臭気の低減が図られる。そして、原料貯留槽51による活性汚泥法等の浄化処理を行い、上澄み液は河川等に放流する一方、沈殿した高水分汚泥は二軸式多目的乾燥機2に搬送されて堆肥化処理が行われることになる。   FIG. 2 is a diagram schematically showing the steps of the embodiment of the present invention. In this embodiment, sewage such as human waste discharged from livestock and the like is collected by a vacuum car 48, transported to the screen unit 49 to remove waste in the sewage, and then stored in the temporary storage tank 50. Then, aeration processing is performed, and aerobic conditions are created to reduce odor. Then, purification treatment such as an activated sludge method is performed in the raw material storage tank 51, and the supernatant liquid is discharged to a river or the like, while the precipitated high moisture sludge is conveyed to the twin-screw multipurpose dryer 2 and subjected to composting treatment. It will be.

一方、生ゴミ等の食品残渣と、稲わら、籾がら、米ぬか、又はくず米等の農業残渣とは、回収車52等により回収して生ゴミ・農業残渣置場53に貯留するとともに、バーク、又はおが屑チップ等からなる若干の水分調整剤が加えられて水分が調整されて好気発酵が行われる。そして、数日間好気発酵された食品残渣及び農業残渣は、ホイルローダ等の運搬車54によって粉砕機55に供給されて一定粒度に整えられた後、上記同様の二軸式多目的乾燥機2に搬送されて堆肥化処理が行われることになる。また、バーク、又はおが屑チップ等の一部は、チップ置場56に一時貯留された後、前記脱臭槽4の脱臭剤として利用されることになる。 On the other hand, food residues such as raw garbage and agricultural residues such as rice straw, rice bran, rice bran, or waste rice are collected by the recovery vehicle 52 and stored in the garbage / agricultural residue storage 53, or A slight moisture adjusting agent made of sawdust chips or the like is added to adjust the moisture, and aerobic fermentation is performed. The food residue and agricultural residue that have been aerobically fermented for several days are supplied to the grinder 55 by a transporter 54 such as a wheel loader and adjusted to a certain particle size, and then transported to the same twin-screw multipurpose dryer 2 as described above. The composting process will be performed. In addition, a part of bark, sawdust chips or the like is temporarily stored in the chip storage place 56 and then used as a deodorizing agent for the deodorizing tank 4.

二軸式多目的乾燥機2に供給された汚泥、食品残渣及び農業残渣は、該二軸式多目的乾燥機2にて所定水分まで乾燥されて発酵条件を整えられた後、熟成発酵機3に供給されて熟成発酵処理される。そして、熟成発酵機3から排出された堆肥化処理物は、ホイルローダ等の運搬車57によって貯留槽58に堆積し、堆肥化処理物を完熟させる。貯留槽58で完熟した堆肥化処理物は出荷するまで待機され、堆肥製品として出荷する際は、運搬車57によりホッパー59に搬送すると、篩装置60によって粒度が整えられる。そして、整粒された堆肥化製品は、製品出荷場に設けられた袋詰装置61に搬送して袋詰加工を行った後、ロボットパレタイザ62等によりパレットに積み付けられ、製品として出荷されることになる。 The sludge, food residue, and agricultural residue supplied to the twin-screw multipurpose dryer 2 are dried to a predetermined moisture by the twin-screw multipurpose dryer 2 and adjusted to fermentation conditions, and then supplied to the aging fermenter 3. Aged and fermented. And the composting processed material discharged | emitted from the aging fermenter 3 accumulates in the storage tank 58 with the transport vehicles 57, such as a wheel loader, and completes the composting processed material. The composted product fully ripe in the storage tank 58 is on standby until shipped, and when shipped as a compost product, the particle size is adjusted by the sieving device 60 when transported to the hopper 59 by the transport vehicle 57. The sized composted product is transported to a bagging device 61 provided at the product shipping site and subjected to bagging processing, and then stacked on a pallet by a robot palletizer 62 and shipped as a product. Will be.

次に、本発明の要部である、二軸式多目的乾燥機2、熟成発酵機3、脱臭槽4、及びバイオマス熱風発生炉5の動作について図1を参照して説明する。 Next, operations of the biaxial multipurpose dryer 2, the aging fermenter 3, the deodorizing tank 4, and the biomass hot air generating furnace 5, which are the main parts of the present invention, will be described with reference to FIG.

まず、バイオマス熱風発生炉5の動作を説明する。前述したように、脱臭槽4に堆積されるバークチップ、籾殻又はおが屑チップ等からなる脱臭剤47は、使用済のときは、水分10%,見掛け密度200Kg/mとなっており、一般的なバイオマス熱風発生炉で使用されるバイオマス原料の水分(例えば、水分40〜50%)よりも低く、着火性がよく、直ちにバイオマス熱風発生炉5のバイオマス燃料として用いることができる。貯留ホッパー33から燃料となる使用済脱臭剤47を供給すると、燃料供給機24により燃焼炉20内に使用済脱臭剤47が繰り出される。次に、ガンタイプバーナ21から使用済脱臭剤47に着火を行うと、使用済脱臭剤47が燃焼を開始するようになる。一方、燃焼炉20の下方からは、空気噴出孔20aから燃焼空気が供給され、燃焼が盛んになるにつれて燃焼温度が上昇し、燃焼炉20内の始端側では約1000℃の熱風が生じる。そして、燃焼炉20全体を覆う冷却管23から、管路63及び送風ファン31により吸引して空冷するとともに、送風ファン31からは管路64を介して燃焼空気供給管22及び排気ダクト29にそれぞれ分岐して送風が行われる。 First, the operation of the biomass hot air generator 5 will be described. As described above, the deodorizer 47 made of bark chips, rice husks, sawdust chips or the like deposited in the deodorization tank 4 has a water content of 10% and an apparent density of 200 kg / m 3 when used. It is lower than the moisture content (for example, 40 to 50%) of the biomass raw material used in a fresh biomass hot air generating furnace, has good ignitability, and can be used immediately as biomass fuel in the biomass hot air generating furnace 5. When the spent deodorant 47 as fuel is supplied from the storage hopper 33, the spent deodorizer 47 is fed into the combustion furnace 20 by the fuel supply unit 24. Next, when the used deodorant 47 is ignited from the gun type burner 21, the used deodorant 47 starts to burn. On the other hand, from the lower side of the combustion furnace 20, combustion air is supplied from the air ejection holes 20a, and the combustion temperature rises as the combustion increases, and hot air of about 1000 ° C. is generated on the start end side in the combustion furnace 20. Then, the cooling pipe 23 covering the entire combustion furnace 20 is sucked by the pipe line 63 and the blower fan 31 and cooled by air, and the blower fan 31 is connected to the combustion air supply pipe 22 and the exhaust duct 29 via the pipe line 64. The air is branched and blown.

燃焼の際に生じる熱風及び燃焼灰は、燃焼炉20終端側の分離室25に至り、該分離室25において燃焼灰が回収ホッパー26及び排出スクリュー27により回収される。この際に回収される燃焼灰は、前記二軸式多目的乾燥機2に供給すれば有機廃棄物の水分調整剤として利用することができる。一方、燃焼炉20終端側に至った熱風は、分離室25上部の排気ダクト29に回収される。この際に回収される熱風は、微細粉塵が混入しているので、管路64を介してサイクロン30に供給し、微細粉塵の分離・除去を行う。そして、サイクロン30により微細粉塵の分離・除去され、熱風供給管16を通過するときの熱風は、温度が400〜500℃、風量が23〜25Nm/min(ノルマル・リューベ;0℃、1気圧状態に換算したガス流量の単位)であった。 Hot air and combustion ash generated during combustion reach the separation chamber 25 at the end of the combustion furnace 20, and the combustion ash is recovered by the recovery hopper 26 and the discharge screw 27 in the separation chamber 25. The combustion ash recovered at this time can be used as a water conditioner for organic waste if supplied to the biaxial multipurpose dryer 2. On the other hand, the hot air reaching the end of the combustion furnace 20 is collected in the exhaust duct 29 at the top of the separation chamber 25. Since the hot air collected at this time is mixed with fine dust, it is supplied to the cyclone 30 via the pipe 64 to separate and remove the fine dust. Then, the fine air is separated and removed by the cyclone 30 and the hot air when passing through the hot air supply pipe 16 has a temperature of 400 to 500 ° C. and an air volume of 23 to 25 Nm 3 / min (normal lube; 0 ° C., 1 atm). Unit of gas flow rate converted into a state).

次に、二軸式多目的乾燥機2の動作について説明する。二軸式多目的乾燥機2の排気側に設置された吸引排気ファン18を作動させると、バイオマス熱風発生炉5からの温度400〜500℃、風量23〜25Nm/minの熱風が吸引され、熱風供給管16を介して底部熱交換部10a、側面部側熱交換部10b,10bに順次導入され、該各熱交換部10a,10bから発酵処理槽7への熱伝達が行われる。また、ギアモータ15を駆動させて攪拌パドル8…を回転駆動させるとともに、回収された汚泥、食品残渣及び農業残渣からなる高水分(例えば、60〜70%)の有機廃棄物1(wet)を、投入口11から発酵処理槽7に投入する。すると、攪拌パドル8…の回転、攪拌、搬送作用により、大き目の塊状物も粉砕され、均一化されて発酵のしやすい条件が整えられる。このとき、発酵槽7内は熱交換によって約80〜100℃程度に維持され、投入された有機廃棄物1(wet)が約70〜80℃程度に維持され、排出時には水分50〜60%まで乾減されるよう乾燥が行われる。なお、側面部側熱交換部10b,10bを通過した熱風は、吸引排気ファン18及び管路65を介して機外に排気される一方、排気の一部は管路66により発酵処理槽7内に直接返還される。このとき、管路65から排気されるときの熱風は、温度180〜230℃、風量19〜22Nm/minであり、管路66により発酵処理槽7内に返還される熱風は、温度180〜230℃、風量3Nm/minであった。
符号67は、発酵処理槽7内への2次空気取り込み用の管路であり、この2次空気は、温度15℃前後、風量4Nm/minであった。また、符号68は、発酵処理槽7内へ通過後の熱風を排気する排気用の管路であり、温度90℃前後、風量11Nm/minの排気であった。
Next, the operation of the biaxial multipurpose dryer 2 will be described. When the suction exhaust fan 18 installed on the exhaust side of the twin-screw multipurpose dryer 2 is operated, hot air having a temperature of 400 to 500 ° C. and an air volume of 23 to 25 Nm 3 / min from the biomass hot air generator 5 is sucked and heated. It is sequentially introduced into the bottom heat exchange unit 10a and the side surface side heat exchange units 10b, 10b through the supply pipe 16, and heat is transferred from the heat exchange units 10a, 10b to the fermentation treatment tank 7. Moreover, while driving the gear motor 15 and rotating the stirring paddles 8 ..., the organic waste 1 (wet) with high moisture (for example, 60 to 70%) composed of the collected sludge, food residue and agricultural residue, It is charged into the fermentation treatment tank 7 from the charging port 11. Then, by the rotation, stirring, and conveying action of the stirring paddles 8..., A large lump is also pulverized and uniformed to prepare conditions that facilitate fermentation. At this time, the inside of the fermenter 7 is maintained at about 80 to 100 ° C. by heat exchange, the input organic waste 1 (wet) is maintained at about 70 to 80 ° C., and the water content is 50 to 60% when discharged. Drying is performed to dry out. The hot air that has passed through the side surface side heat exchange units 10b and 10b is exhausted to the outside of the apparatus via the suction exhaust fan 18 and the pipe 65, while a part of the exhaust is passed through the fermentation pipe 7 through the pipe 66. Will be returned directly. At this time, the hot air when exhausted from the pipe 65 has a temperature of 180 to 230 ° C. and an air volume of 19 to 22 Nm 3 / min, and the hot air returned to the fermentation treatment tank 7 by the pipe 66 has a temperature of 180 to 230 ° C. It was 230 degreeC and the air volume was 3 Nm < 3 > / min.
The code | symbol 67 is a pipe line for taking in secondary air in the fermentation treatment tank 7, This secondary air was the temperature of about 15 degreeC, and the air volume was 4 Nm < 3 > / min. Reference numeral 68 denotes an exhaust pipe for exhausting the hot air after passing into the fermentation treatment tank 7, and was an exhaust having a temperature of about 90 ° C. and an air volume of 11 Nm 3 / min.

次に、水分50〜60%まで乾減された有機廃棄物1(dry)は、熟成発酵機3に移される。熟成発酵機3では、ロータリー攪拌機37が作動され、発酵槽34に堆積された有機廃棄物1(dry)が掬い上げられた後、落下される。これにより、有機廃棄物1(dry)の塊状物を小片にほぐしつつ均一に混合させ、好気性発酵に適した通気性を付与する。そして、発酵の際に生じる悪臭空気は前述と同様、吸引ノズル41…、吸引ファン42及び排気管43を介して脱臭槽4にて脱臭されることになる。 Next, the organic waste 1 (dry) dried to 50 to 60% moisture is transferred to the aging fermenter 3. In the aging fermenter 3, the rotary stirrer 37 is operated, and the organic waste 1 (dry) accumulated in the fermenter 34 is scooped up and dropped. Thereby, the lump of the organic waste 1 (dry) is uniformly mixed while being broken into small pieces, and air permeability suitable for aerobic fermentation is imparted. And the bad odor air which arises in the case of fermentation is deodorized in the deodorizing tank 4 through the suction nozzle 41 ..., the suction fan 42, and the exhaust pipe 43 like the above.

以上のような堆肥化処理方法およびその装置において、使用燃料の燃料効率を試算すれば、日量1tonの木質系バイオマスを原料とするバイオマス熱風発生炉5において、温度400〜500℃の熱風を取り出すために必要な熱量は約10000MJであり、A重油に換算して256リットルである。これに対し、本発明のバイオマス熱風発生炉5のA重油の使用量はおおよそ着火に必要なエネルギのみとなるため1リットル程度でよく、A重油の使用量を約99%以上節減することが可能となった。 In the composting method and apparatus as described above, if the fuel efficiency of the fuel used is estimated, hot air having a temperature of 400 to 500 ° C. is taken out in the biomass hot air generator 5 using 1 ton woody biomass as a raw material. The amount of heat required for this is about 10,000 MJ, which is 256 liters in terms of A heavy oil. On the other hand, the amount of heavy oil A used in the biomass hot air generator 5 according to the present invention is only about 1 liter because it is only energy required for ignition, and the amount of heavy oil A can be reduced by about 99% or more. It became.

本発明の堆肥化処理方法およびその装置の実施形態を示す概要図である。It is the schematic which shows embodiment of the composting processing method and its apparatus of this invention. 本発明の実施形態の工程について模式的に示した図である。It is the figure which showed typically about the process of embodiment of this invention.

符号の説明Explanation of symbols

1 有機廃棄物
2 二軸式多目的乾燥機
3 熟成発酵機
4 脱臭槽
5 バイオマス熱風発生炉
6 機枠
7 発酵処理槽
8 攪拌パドル
9 回転軸
10 熱交換部
11 投入口
12 排出口
13 開閉扉
14 開閉扉
15 ギアモータ
16 熱風供給管
17 熱風排出管
18 吸引排気ファン
19 機枠
20 燃焼炉
21 ガンタイプバーナ
22 燃焼空気供給管
23 冷却管
24 燃料供給機
25 分離室
26 回収ホッパー
27 排出スクリュー
28 搬送スクリュー
29 排気ダクト
30 サイクロン
31 送風ファン
32 クーリングタワー
33 貯留ホッパー
34 発酵槽
35 原料投入部
36 堆肥搬出部
37 ロータリー撹拌機
38 建屋
39 空気供給ダクト
40 送風機
41 吸引ノズル
42 吸引ファン
43 排気管
44 槽体
45 噴出管
46 閉鎖弁
47 脱臭剤
48 バキュームカー
49 スクリーンユニット
50 一時貯留槽
51 原料貯留槽
52 回収車
53 生ゴミ・農業残渣置場
54 運搬車
55 粉砕機
56 チップ置場
57 運搬車
58 貯留槽
59 ホッパー
60 篩装置
61 袋詰装置
62 ロボットパレタイザ
63 管路
64 管路
65 管路
66 管路
67 管路
68 管路
DESCRIPTION OF SYMBOLS 1 Organic waste 2 Twin-shaft multipurpose dryer 3 Aging fermenter 4 Deodorizing tank 5 Biomass hot air generating furnace 6 Machine frame 7 Fermentation processing tank 8 Stir paddle 9 Rotating shaft 10 Heat exchange part 11 Input port 12 Outlet port 13 Opening / closing door 14 Opening and closing door 15 Gear motor 16 Hot air supply pipe 17 Hot air discharge pipe 18 Suction exhaust fan 19 Machine frame 20 Combustion furnace 21 Gun type burner 22 Combustion air supply pipe 23 Cooling pipe 24 Fuel supply machine 25 Separation chamber 26 Recovery hopper 27 Discharge screw 28 Conveying screw 29 Exhaust duct 30 Cyclone 31 Blower fan 32 Cooling tower 33 Storage hopper 34 Fermenter 35 Raw material input part 36 Compost carry-out part 37 Rotary stirrer 38 Building 39 Air supply duct 40 Blower 41 Suction nozzle 42 Suction fan 43 Exhaust pipe 44 Tank body 45 Ejection Pipe 46 Shut-off valve 47 Deodorant 48 Vacuum car 4 9 Screen unit 50 Temporary storage tank 51 Raw material storage tank 52 Recovery vehicle 53 Garbage / agricultural residue storage 54 Transport vehicle 55 Crusher 56 Chip storage 57 Transport vehicle 58 Storage tank 59 Hopper 60 Sieve device 61 Bagging device 62 Robot palletizer 63 Pipe line 64 Pipe line 65 Pipe line 66 Pipe line 67 Pipe line 68 Pipe line

Claims (6)

家畜の糞尿や生ゴミ等の有機廃棄物を熟成発酵処理する熟成発酵工程と、該熟成発酵工程で生じる臭気ガスを回収して脱臭剤により吸着・脱臭処理する脱臭工程と、前記熟成発酵工程の前工程に、熱風発生室にて生成した熱風を用いて前記有機廃棄物の水分を蒸発させ、発酵条件を整える乾燥前処理工程と、を具備した有機廃棄物の堆肥化処理方法であって、
前記乾燥前処理工程で使用する熱風の熱源として、前記脱臭工程にて臭気ガスを吸着・脱臭処理した後の脱臭能力が低下した脱臭剤を燃焼したときの燃焼熱を利用することを特徴とする有機廃棄物の堆肥化処理方法。
An aging fermentation process for aging fermentation of organic wastes such as livestock manure and garbage, a deodorization process for recovering odorous gas generated in the aging fermentation process and adsorbing and deodorizing with a deodorizer, and the aging fermentation process A pre-drying treatment step for evaporating the moisture of the organic waste using hot air generated in a hot air generation chamber in the previous step and adjusting the fermentation conditions, and a composting method for organic waste,
The heat source of hot air used in the pre-drying treatment step is characterized by using the heat of combustion when burning a deodorant having reduced deodorizing ability after adsorbing and deodorizing odor gas in the deodorization step. Method for composting organic waste.
前記脱臭剤は、木の樹皮を粉砕したバークチップ、籾殻又はおが屑チップなどの木質系バイオマスとなし、前記乾燥前処理工程で使用する熱風の熱源として、前記脱臭工程にて吸着・脱臭処理した後の水分25%未満に低下した脱臭剤を燃焼したときの燃焼熱を利用してなる請求項1記載の有機廃棄物の堆肥化処理方法。 The deodorizing agent is made of woody biomass such as bark chips, rice husks or sawdust chips obtained by pulverizing the bark of a tree, and as a heat source of hot air used in the pre-drying treatment step, after adsorption / deodorization treatment in the deodorization step The composting method of the organic waste of Claim 1 formed using the heat of combustion when the deodorizing agent reduced to less than 25% of the moisture is burned. 前記脱臭剤を燃焼したときの燃焼灰を、前記乾燥前処理工程にて処理中の有機廃棄物に水分調整剤として混合してなる請求項1又は2記載の有機廃棄物の堆肥化処理方法。   The composting method of the organic waste of Claim 1 or 2 formed by mixing the combustion ash when burning the said deodorizer with the organic waste currently processed in the said pre-drying process as a moisture adjusting agent. 家畜の糞尿や生ゴミ等の高水分の有機廃棄物に熱風を送風しながら攪拌して水分を蒸発させて発酵条件を整える乾燥機(2)と、水分を蒸発させた後の低水分の有機廃棄物を熟成発酵処理する熟成発酵機(3)と、該熟成発酵機(3)で生じた臭気ガスを回収して脱臭剤により吸着・脱臭処理する脱臭槽(4)と、を備えた有機廃棄物の堆肥化処理装置であって、
前記乾燥機(2)の前工程には、前記脱臭槽(4)にて臭気ガスを吸着・脱臭処理した後の脱臭能力が低下した脱臭剤をバイオマス燃料とするバイオマス熱風発生炉(5)を備えたことを特徴とする有機廃棄物の堆肥化処理装置。
Dryer (2) that stirs hot air to a high-moisture organic waste such as livestock manure and garbage and evaporates the water to adjust the fermentation conditions, and the low-moisture organic after evaporating the water Organic equipped with an aging fermenter (3) for aging fermentation of waste, and a deodorization tank (4) for recovering odorous gas generated in the aging fermenter (3) and adsorbing and deodorizing with a deodorizing agent A composting device for waste,
In the pre-process of the dryer (2), there is a biomass hot air generator (5) using as a biomass fuel a deodorant whose deodorizing ability is reduced after adsorbing and deodorizing odorous gas in the deodorizing tank (4). An organic waste composting apparatus characterized by comprising:
前記乾燥機(2)は、直方体状の機枠(6)内に形成した処理槽(7)と、該処理槽(7)内に回転自在に支持される回転軸(9)と、該回転軸(9)に対して放射状に植設された多数の攪拌パドル(8…)と、前記処理槽(7)と機枠(6)の外殻との間に介装され、前記バイオマス熱風発生炉(5)から送給される熱風と前記処理槽(7)内の有機廃棄物との熱交換を行う熱交換部(10)と、を備えてなる請求項4記載の堆肥化処理装置。 The dryer (2) includes a treatment tank (7) formed in a rectangular parallelepiped machine frame (6), a rotary shaft (9) rotatably supported in the treatment tank (7), and the rotation A large number of agitation paddles (8...) Radially planted with respect to the shaft (9) and interposed between the treatment tank (7) and the outer shell of the machine frame (6) to generate the biomass hot air. The composting processing apparatus of Claim 4 provided with the heat exchange part (10) which performs heat exchange with the hot air supplied from a furnace (5), and the organic waste in the said processing tank (7). 前記バイオマス熱風発生炉(4)は、機枠(19)内に築炉された横型円筒状の燃焼炉(20)と、該燃焼炉(20)内に供給されるバイオマス燃料に着火を行うためのガンタイプバーナ(21)と、前記燃焼炉(20)内部へ燃焼空気を供給する燃焼空気供給管(22)と、該燃焼空気供給管(22)を囲繞するように配設され、前記熱風発生炉(4)全体を空冷するための冷却管(23)と、前記脱臭剤からなるバイオマス燃料を前記燃焼炉(20)内に繰り出すための燃料供給機(24)と、前記燃焼炉(20)内の熱風と燃焼灰とをそれぞれ回収する分離室(25)と、該分離室(25)下部に配設される燃焼灰を回収するための回収ホッパー(26)及び排出スクリュー(27)と、前記分離室(25)上部に配設される熱風を回収するための排気ダクト(29)と、を備えてなる請求項4又は5記載の堆肥化処理装置。 The biomass hot air generating furnace (4) ignites the horizontal cylindrical combustion furnace (20) built in the machine frame (19) and the biomass fuel supplied into the combustion furnace (20). A gun type burner (21), a combustion air supply pipe (22) for supplying combustion air to the inside of the combustion furnace (20), and the hot air A cooling pipe (23) for air-cooling the entire generating furnace (4), a fuel supply machine (24) for feeding biomass fuel made of the deodorizer into the combustion furnace (20), and the combustion furnace (20 ) And a recovery hopper (26) and a discharge screw (27) for recovering the combustion ash disposed in the lower part of the separation chamber (25). The hot air disposed in the upper part of the separation chamber (25) is rotated. Exhaust duct (29) and becomes comprise claim 4 or 5 composting apparatus according to.
JP2008008738A 2008-01-18 2008-01-18 Method of composting organic waste and apparatus therefor Pending JP2009167063A (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013017926A (en) * 2011-07-08 2013-01-31 Syudensya Co Ltd Organic waste treatment device
KR20150037788A (en) 2015-03-16 2015-04-08 서희동 Method for treatment of food waste
CN104986936A (en) * 2015-06-15 2015-10-21 苏细调 Built-in temperature control type solid-liquid separator
CN106180148A (en) * 2016-08-24 2016-12-07 杨国强 A kind of waste disposal method and device thereof
CN106552817A (en) * 2017-01-11 2017-04-05 光大环保技术研究院(深圳)有限公司 A kind of changing food waste pretreatment system and method
JP2022160742A (en) * 2021-04-07 2022-10-20 株式会社カワナカ Waste disposal system and waste disposal method
CN116396846A (en) * 2023-06-09 2023-07-07 保罗蒂姆汉(潍坊)生物科技有限公司 Organic fertilizer-based decomposing inoculant production device
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