JP5053568B2 - Combustion apparatus and odor gas treatment method using the same - Google Patents

Combustion apparatus and odor gas treatment method using the same Download PDF

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JP5053568B2
JP5053568B2 JP2006128133A JP2006128133A JP5053568B2 JP 5053568 B2 JP5053568 B2 JP 5053568B2 JP 2006128133 A JP2006128133 A JP 2006128133A JP 2006128133 A JP2006128133 A JP 2006128133A JP 5053568 B2 JP5053568 B2 JP 5053568B2
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功一 小林
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Description

本発明は、家畜の糞尿や生ゴミ等の有機廃棄物を堆肥化する際に発生するアンモニアガス、し尿処理施設で発生するアンモニアガスや、廃水、下水、汚泥処理などの処理槽や乾燥機、焼却炉などが排出する硫化水素などの臭気を伴ったガス(以下これらのガスを臭気ガスと総称する。)を燃焼して無臭化、無毒化するための燃焼装置およびそれを利用した臭気ガスの処理方法に関する。   The present invention relates to ammonia gas generated when composting organic waste such as manure and garbage of livestock, ammonia gas generated in human waste treatment facilities, treatment tanks and dryers for wastewater, sewage, sludge treatment, Combustion equipment for deodorizing and detoxifying gases with odors such as hydrogen sulfide (hereinafter collectively referred to as odor gas) discharged from incinerators and the like, and odor gas using the same It relates to the processing method.

従来より、家畜の糞尿や生ゴミ等の有機廃棄物は、堆肥化させて再び肥料として利用されている。この堆肥化を短時間で行う方法として、醗酵槽内へ有機廃棄物を投入して、ファン等により醗酵槽内へ送風するとともに機械的に撹拌して好気的醗酵を促し、醗酵熱によって自然に水分を蒸発させつつ醗酵させる撹拌式堆肥化方法がある。たとえば、処理槽内の有機廃棄物に送風して有機廃棄物に含まれる水分を蒸発させる方法(例えば特許文献1参照)、加温した糞尿処理菌の醗酵熱で水分を蒸発させる方法(例えば特許文献2参照)、糞尿を固分と液分に分離し、水分含有量を小さくした糞尿を醗酵させる方法(例えば特許文献3参照)などが知られている。
特開2002−274989号公報((0023)、(0060)など) 特開2002−355694号公報(請求項1、(0022)など) 特開平11−268982号公報(請求項1、(0005)など)
Conventionally, organic wastes such as livestock manure and garbage are composted and reused as fertilizer. As a method of performing this composting in a short time, organic waste is introduced into the fermenter, blown into the fermenter with a fan or the like, mechanically stirred to promote aerobic fermentation, and naturally produced by fermentation heat. There is a stirring type composting method in which water is fermented while evaporating water. For example, a method of blowing the organic waste in the treatment tank to evaporate the water contained in the organic waste (for example, refer to Patent Document 1), a method of evaporating the water with the fermentation heat of the heated excreta treating bacteria (for example, patent) Document 2), a method of separating manure into solid and liquid and fermenting manure with a reduced water content (see, for example, Patent Document 3) is known.
Japanese Patent Laid-Open No. 2002-274899 ((0023), (0060), etc.) JP 2002-355694 A (Claim 1, (0022), etc.) JP-A-11-268982 (Claim 1, (0005), etc.)

これらの特許文献1から特許文献3に記載された攪拌式堆肥化方法は、醗酵前または醗酵中に有機廃棄物に含まれる水分を蒸発させ乾燥させるものである。この有機廃棄物の乾燥時には、有機廃棄物からアンモニアなどの臭気を伴う臭気ガスが発生する。このときのアンモニアの発生量は300ppm〜400ppmに達する。したがって、空気汚染などの環境面や良好な作業環境を保つために、有機廃棄物の乾燥時における臭気を除き無毒化することが必要である。   These agitation composting methods described in Patent Document 1 to Patent Document 3 evaporate and dry moisture contained in organic waste before or during fermentation. When the organic waste is dried, an odor gas accompanied by an odor such as ammonia is generated from the organic waste. The amount of ammonia generated at this time reaches 300 ppm to 400 ppm. Therefore, in order to maintain an environmental aspect such as air pollution and a good working environment, it is necessary to detoxify the organic waste except for odors when it is dried.

そこで本発明は、有機廃棄物を熟成醗酵させる際に発生するアンモニアなどの臭気ガスに起因する臭気を除去するとともに、空気汚染や人体へ悪影響を引き起こす臭気ガスを適切に処理して無臭化、無毒化することができる燃焼装置を提供することを目的とする。
また、臭気ガスの燃焼時に発生するダイオキシン、SOxおよびNOxの量を飛躍的に低減させることができる燃焼装置を提供することを目的とする。
また、臭気ガスを簡単な方法で燃焼して確実に無臭化、無毒化する臭気ガスの処理方法を提供することを目的とする。
Therefore, the present invention eliminates odors caused by odorous gases such as ammonia generated when organic waste is aged and fermented, and appropriately treats odorous gases that cause adverse effects on air pollution and the human body so that they are not brominated and nontoxic. It is an object of the present invention to provide a combustion device that can be made into a gas.
It is another object of the present invention to provide a combustion apparatus capable of dramatically reducing the amount of dioxin, SOx and NOx generated during combustion of odor gas.
It is another object of the present invention to provide a method of treating odor gas that burns odor gas by a simple method to reliably make it odor-free and non-toxic.

請求項1に記載の本発明の燃焼装置は、燃料を燃焼させて下部から上部に向かって渦状に回転する燃焼流を発生させる一次燃焼室と、前記一次燃焼室に連設された二次燃焼室とを有する燃焼装置であって、前記二次燃焼室に空気を導入する開閉自在の空気導入口と、前記二次燃焼室に臭気ガスを導入する開閉自在のガス導入口とを設け、前記二次燃焼室は、燃焼室と、前記燃焼室の外部を覆うガス収納室とを有しており、前記燃焼室は前記一次燃焼室で燃焼した燃焼ガスを取り入れる入口部と、前記燃焼室の内部に設けられた燃焼流規制板と、燃焼した前記燃焼ガスを取り出す出口部とで構成され、前記燃焼室の前記入口部の周辺部には前記ガス収納室に連通する開口が設けられており、前記空気導入口とガス導入口は前記ガス収納室に連通していることを特徴とする。
請求項2に記載の本発明は、請求項1に記載の燃焼装置において、前記臭気ガスがアンモニアガスであることを特徴とする。
請求項3に記載の本発明の臭気ガス処理方法は、燃料を燃焼させる一次燃焼室と、前記一次燃焼室に連設された二次燃焼室とを有し、前記二次燃焼室に空気を導入する開閉自在の空気導入口と、前記二次燃焼室に臭気ガスを導入する開閉自在のガス導入口とを設け、前記二次燃焼室は、燃焼室と、前記燃焼室の外部を覆うガス収納室とを有しており、前記燃焼室は前記一次燃焼室で燃焼した燃焼ガスを取り入れる入口部と、燃焼した前記燃焼ガスを取り出す出口部とで構成され、前記燃焼室の前記入口部の周辺部には前記ガス収納室に連通する開口が設けられており、前記空気導入口と前記ガス導入口は前記ガス収納室に連通している燃焼装置を用いた臭気ガス処理方法であって、前記一次燃焼室で燃料を燃焼させて下部から上部に向かって渦状に回転する燃焼流を発生させる第1の工程と、前記一次燃焼室に連設された前記二次燃焼室で前記燃焼流を高温化させる第2の工程と、前記二次燃焼室に前記臭気ガスを導入して燃焼させる第3の工程を有し、前記第3の工程に先立って、前記空気導入口から前記ガス収納室に導入された前記空気を前記開口から前記燃焼室内に導入して燃焼を行い、燃焼が高温で安定した状態になったときに前記ガス導入口を開いて前記第3の工程による前記臭気ガスの燃焼を行うことを特徴とする。
請求項4に記載の本発明は、請求項3に記載の臭気ガス処理方法において、前記第3の工程において前記空気の導入を停止して臭気ガスを導入することを特徴とする。
A combustion apparatus according to a first aspect of the present invention includes a primary combustion chamber that combusts fuel and generates a combustion flow that rotates in a spiral shape from a lower portion to an upper portion, and a secondary combustion that is connected to the primary combustion chamber. a combustion apparatus having a chamber, the openable air inlet for introducing air, and openable gas inlet for introducing an odor gas into the secondary combustion chamber provided in the secondary combustion chamber, wherein The secondary combustion chamber has a combustion chamber and a gas storage chamber covering the outside of the combustion chamber, and the combustion chamber has an inlet for taking in combustion gas burned in the primary combustion chamber, and the combustion chamber Composed of a combustion flow regulating plate provided inside and an outlet portion for taking out the burned combustion gas, an opening communicating with the gas storage chamber is provided in the periphery of the inlet portion of the combustion chamber. The air inlet and the gas inlet communicate with the gas storage chamber. And wherein the are.
The present invention described in claim 2 is the combustion apparatus according to claim 1, wherein the odorous gas is ammonia gas.
The odor gas processing method of the present invention according to claim 3 has a primary combustion chamber for burning fuel, and a secondary combustion chamber connected to the primary combustion chamber, and air is supplied to the secondary combustion chamber. An openable / closable air inlet for introduction and an openable / closable gas inlet for introducing odorous gas into the secondary combustion chamber are provided, and the secondary combustion chamber is a gas that covers the combustion chamber and the outside of the combustion chamber. A storage chamber, and the combustion chamber includes an inlet portion for taking in the combustion gas burned in the primary combustion chamber and an outlet portion for taking out the burned combustion gas. The peripheral portion is provided with an opening communicating with the gas storage chamber, and the air inlet and the gas inlet are odor gas treatment methods using a combustion device communicating with the gas storage chamber, toward the bottom to top by the fuel is combusted in the primary combustion chamber A first step of generating a combustion flow which rotates Jo, a second step of high temperature of the combustion stream by the secondary combustion chamber provided continuously to the primary combustion chamber, the said secondary combustion chamber by introducing odorous gases have a third step of burning, prior to the third step, introducing the air introduced into the gas storage chamber from said air inlet openings into the combustion chamber from the opening Combustion is performed, and when the combustion becomes stable at a high temperature, the gas inlet is opened, and the odorous gas is combusted in the third step .
The present invention described in claim 4 is the odorous gas treatment method according to claim 3, characterized by introducing the odor gas by stopping the introduction of the air in the third step.

本発明の燃焼装置によれば、有機廃棄物を熟成醗酵させる際に発生するアンモニアなどの臭気ガスに起因する臭気を除去するとともに、空気汚染や人体へ悪影響を引き起こす臭気ガスを無臭化、無毒化することができる。
また、臭気ガスの燃焼時に発生するダイオキシン、SOxおよびNOxの量を飛躍的に低減させることができる。
また、本発明の臭気ガスの処理方法によれば、臭気ガスを簡単な方法で燃焼して確実に無臭化、無毒化することができる。
According to the combustion apparatus of the present invention, odor gas caused by odor gas such as ammonia generated when aging fermentation of organic waste is removed, and odor gas that causes adverse effects on air pollution and human body is not brominated and detoxified. can do.
In addition, the amount of dioxin, SOx and NOx generated during the combustion of odor gas can be drastically reduced.
In addition, according to the odor gas treatment method of the present invention, the odor gas can be burned by a simple method and reliably deodorized and non-toxic.

本発明の第1の実施の形態による燃焼装置は、下部から上部に向かって渦状に回転する燃焼流を発生させる一次燃焼室に二次燃焼室を連設し、二次燃焼室に空気を導入する開閉自在の空気導入口と、臭気ガスを導入する開閉自在のガス導入口を設け、二次燃焼室は、燃焼室と、燃焼室の外部を覆うガス収納室を有しており、燃焼室は一次燃焼室で燃焼した燃焼ガスを取り入れる入口部と、燃焼室の内部に設けられた燃焼流規制板と、燃焼した燃焼ガスを取り出す出口部で構成され、燃焼室の入口部の周辺部にはガス収納室に連通する開口が設けられており、空気導入口とガス導入口はガス収納室に連通しているものである。本実施の形態によれば、一次燃焼室を渦状に回転して上昇する燃焼流が二次燃焼室へ移動して更に燃焼する。このとき、二次燃焼室に空気を導入すると、二次燃焼室においては燃焼温度は1500度以上の高温に上昇して完全燃焼する。この状態でガス導入口を開き、空気導入口を閉じると、二次燃焼室に臭気ガスが導入され、臭気ガスは高温で燃焼されるので、臭気ガスに起因する臭気を除去するとともに、空気汚染や人体へ悪影響を引き起こす臭気ガスを無臭化、無毒化することができる。また、二次燃焼室に空気および臭気ガスを選択的に導入可能であり、空気を導入しているときは燃焼ガスと空気とが攪拌されて高温で完全燃焼させることができる。また、二次燃焼室に臭気ガスを導入しているときは燃焼ガスと臭気ガスとが攪拌されて、臭気ガスを高温で燃焼させることができる。したがって、臭気ガスに起因する臭気を除去するとともに、空気汚染や人体へ悪影響を引き起こす臭気ガスを無臭化、無毒化することができる。
本発明の第2の実施の形態は、第1の実施の形態による燃焼装置において、臭気ガスをアンモニアガスとしたものである。本実施の形態によれば、家畜の糞尿や生ゴミ等の有機廃棄物を堆肥化する堆肥化施設やし尿処理施設などで発生するアンモニアガスを窒素と水に熱分解して無臭、無毒化することができる。また、廃油などを燃焼して発生するNOxを分解することができるので、排気中の公害成分を飛躍的に減少させることができる。
本発明の第3の実施の形態による臭気ガスの処理方法は、一次燃焼室で燃料を燃焼させて下部から上部に向かって渦状に回転する燃焼流を発生させ、この燃焼流を二次燃焼室で高温化させた後、二次燃焼室に臭気ガスを導入して燃焼させるもので、空気導入口からガス収納室に導入された空気を開口から燃焼室内に導入して燃焼を行い、燃焼が高温で安定した状態になったときにガス導入口を開いて臭気ガスの燃焼を行うものある。本実施の形態によれば、臭気ガスが高温で燃焼されるので、臭気ガスに起因する臭気を除去するとともに、無臭化、無毒化することができる。
本発明の第4の実施の形態は、第3の実施の形態による臭気ガスの処理方法において、空気の導入を停止するものである。本実施の形態によれば、二次燃焼室における燃焼が高温で安定した状態になってから臭気ガスを導入しているので、臭気ガスが高温で燃焼されて臭気を確実に除去するとともに、無臭化、無毒化することができる。
The combustion apparatus according to the first embodiment of the present invention has a secondary combustion chamber connected to a primary combustion chamber that generates a combustion flow that rotates in a spiral shape from the bottom to the top, and introduces air into the secondary combustion chamber. The secondary combustion chamber has a combustion chamber and a gas storage chamber that covers the outside of the combustion chamber. The combustion chamber Is composed of an inlet for taking in the combustion gas burned in the primary combustion chamber, a combustion flow regulating plate provided inside the combustion chamber, and an outlet for taking out the burned combustion gas. Is provided with an opening communicating with the gas storage chamber, and the air inlet and the gas inlet are in communication with the gas storage chamber . According to this embodiment, the combustion flow that rises by rotating the primary combustion chamber in a vortex shape moves to the secondary combustion chamber and further burns. At this time, when air is introduced into the secondary combustion chamber, the combustion temperature in the secondary combustion chamber rises to a high temperature of 1500 ° C. or higher and complete combustion occurs. When the gas inlet is opened and the air inlet is closed in this state, the odor gas is introduced into the secondary combustion chamber and the odor gas is burned at a high temperature, so that the odor caused by the odor gas is removed and air pollution is caused. And odorous gases that cause adverse effects on the human body can be made non-bromide and non-toxic. In addition, air and odor gas can be selectively introduced into the secondary combustion chamber. When air is being introduced, the combustion gas and air can be agitated and completely burned at a high temperature. Further, when the odor gas is introduced into the secondary combustion chamber, the combustion gas and the odor gas are agitated, and the odor gas can be burned at a high temperature. Therefore, it is possible to remove the odor caused by the odor gas, and to make the odor gas causing air pollution and a bad influence on the human body non-brominated and non-toxic.
The second embodiment of the present invention is such that the odor gas is ammonia gas in the combustion apparatus according to the first embodiment. According to the present embodiment, ammonia gas generated in composting facilities and manure processing facilities that compost organic waste such as livestock manure and garbage is thermally decomposed into nitrogen and water to make it odorless and nontoxic. be able to. Further, since NOx generated by burning waste oil or the like can be decomposed, pollution components in the exhaust gas can be drastically reduced.
In the odor gas processing method according to the third embodiment of the present invention, fuel is combusted in the primary combustion chamber to generate a combustion flow rotating in a spiral shape from the lower portion to the upper portion, and this combustion flow is generated in the secondary combustion chamber. The odor gas is introduced into the secondary combustion chamber and burned after being heated at a high temperature, and the air introduced into the gas storage chamber from the air inlet is introduced into the combustion chamber through the opening to perform combustion. Some of them burn odorous gas by opening the gas inlet when it becomes stable at high temperature . According to the present embodiment, since the odor gas is burned at a high temperature, it is possible to remove the odor caused by the odor gas and to make it non-bromide and non-toxic.
Fourth embodiment of the present invention, in the processing method of odorous gases according to the third embodiment, a shall which abolish stop the introduction of air. According to the present embodiment, since the odor gas is introduced after the combustion in the secondary combustion chamber becomes stable at a high temperature, the odor gas is burned at a high temperature and the odor is surely removed and odorless. Can be made non-toxic.

以下、本発明の一実施例における燃焼装置について図面に基づいて説明する。
図1は本発明の一実施例における燃焼装置の一部破断側面図、図2は同実施例における燃焼装置の一部破断平面図である。
本実施例による燃焼装置の主要部は、一次燃焼室1、二次燃焼室2、排気室3、排気ダクト4および排気ファン5で構成される。
一次燃焼室1は、円筒状で縦型に配設される燃焼壁11と、この燃焼壁11に連設された底部12と、燃焼壁11の上端部を開閉可能に閉塞する蓋部13で構成されている。底部12の近傍には点検口14と燃料供給口15が設けられ、燃焼壁11の上部には一次燃焼室1内部へ空気を供給する空気供給管16と、一次燃焼室1で燃焼された燃焼ガスを二次燃焼室2へ送る一次燃焼室出口部17が設けられている。燃焼壁11は耐圧性能面で円筒状が好ましい。
一次燃焼室1の内部には、空気供給管16と連設され、燃焼壁11のほぼ中心軸を通る位置に配置された垂直空気噴出管18と、垂直空気噴出管18の下端部に連設され、底部12の上部に配置された複数の水平空気噴出管19とから構成された空気噴出管20を備えている。
Hereinafter, a combustion apparatus according to an embodiment of the present invention will be described with reference to the drawings.
FIG. 1 is a partially broken side view of a combustion apparatus in one embodiment of the present invention, and FIG. 2 is a partially broken plan view of the combustion apparatus in the same embodiment.
The main part of the combustion apparatus according to this embodiment includes a primary combustion chamber 1, a secondary combustion chamber 2, an exhaust chamber 3, an exhaust duct 4 and an exhaust fan 5.
The primary combustion chamber 1 includes a cylindrical combustion wall 11 arranged vertically, a bottom 12 connected to the combustion wall 11, and a lid 13 that closes an upper end of the combustion wall 11 so as to be openable and closable. It is configured. An inspection port 14 and a fuel supply port 15 are provided in the vicinity of the bottom portion 12, an air supply pipe 16 for supplying air into the primary combustion chamber 1 inside the combustion wall 11, and combustion burned in the primary combustion chamber 1. A primary combustion chamber outlet 17 for sending gas to the secondary combustion chamber 2 is provided. The combustion wall 11 is preferably cylindrical in terms of pressure resistance.
Inside the primary combustion chamber 1, it is connected to the air supply pipe 16, and is connected to the vertical air jet pipe 18 arranged at a position passing through the central axis of the combustion wall 11, and the lower end of the vertical air jet pipe 18. And an air ejection pipe 20 composed of a plurality of horizontal air ejection pipes 19 arranged at the top of the bottom portion 12.

図3に空気噴出管20の構造の一例を示す。垂直空気噴出管18には、縦列に空気噴出孔18Aが略等間隔であけられ、この空気噴出孔18Aは、隣りあう縦列の空気噴出孔18Aの位置から垂直方向で所定寸法ずらして螺旋状に設けられる。空気噴出孔18Aは、空気噴出孔18Aから噴出された空気流が渦状に回転するように一方向に角度を持たせた孔であることが好ましい。複数の水平空気噴出管19の各々には複数個の空気噴出孔19Aが設けられる。これらの空気噴出孔19Aは、一次燃焼室1の中心から外方向に広がるスパイラル状の位置に空気噴出孔19Aが設けられる。空気噴出孔19Aは、噴出された空気流が渦状に回転するように斜め上方向に向いた孔であることが好ましい。
空気供給管16には、空気送風ファン(図示せず)から空気が送られ、この空気は、垂直空気噴出管18および水平空気噴出管19から一次燃焼室1に送り込まれる。このとき、空気噴出孔18Aから噴出した空気によって生じる渦の回転方向と、空気噴出孔19Aから噴出した空気によって生じる渦の回転方向が一致するように、空気噴出孔18Aの噴出方向と、空気噴出孔19Aの噴出方向を選定すると、一次燃焼室1の燃焼効率がよりよい状態が得られる。
FIG. 3 shows an example of the structure of the air ejection pipe 20. The vertical air ejection pipes 18 are provided with air ejection holes 18A arranged in a column at substantially equal intervals, and the air ejection holes 18A are spirally shifted by a predetermined dimension in the vertical direction from the position of the adjacent air ejection holes 18A. Provided. The air ejection hole 18A is preferably a hole that has an angle in one direction so that the air flow ejected from the air ejection hole 18A rotates in a spiral shape. Each of the plurality of horizontal air ejection pipes 19 is provided with a plurality of air ejection holes 19A. These air ejection holes 19 </ b> A are provided with air ejection holes 19 </ b> A at spiral positions extending outward from the center of the primary combustion chamber 1. The air ejection hole 19A is preferably a hole oriented obliquely upward so that the ejected airflow rotates in a spiral shape.
Air is sent to the air supply pipe 16 from an air blower fan (not shown), and this air is sent to the primary combustion chamber 1 from a vertical air jet pipe 18 and a horizontal air jet pipe 19. At this time, the ejection direction of the air ejection hole 18A and the air ejection so that the rotation direction of the vortex generated by the air ejected from the air ejection hole 18A and the rotation direction of the vortex generated by the air ejected from the air ejection hole 19A coincide with each other. When the ejection direction of the hole 19A is selected, a state in which the combustion efficiency of the primary combustion chamber 1 is better is obtained.

二次燃焼室2は、燃焼室21と、燃焼室21の外部を覆うガス収納室22の二重構造を有しており、燃焼室21はガス収納室22内においてガス収納室22の底面を兼用するベース20上に植立された支持具23により支持されている。
燃焼室21は、一次燃焼室出口部17に連設し、一次燃焼室1で燃焼した燃焼ガスの取り入れ口である二次燃焼室入口部24と、燃焼室21の内部に設けられた燃焼流規制板25と、燃焼した燃焼ガスの取り出し口である二次燃焼室出口部26で構成される。燃焼室21、二次燃焼室入口部24および二次燃焼室出口部26はいずれも円筒形状で構成している。二次燃焼室入口部24の一端は、ガス収納室22の一次燃焼室1側の壁面221に穿たれた孔を貫通して一次燃焼室出口部17に連設している。二次燃焼室入口部24の他端は、図4に示すように、燃焼室21の入り口側の壁面27の上部に設けられた孔271に接続されている。壁面27の孔271の周辺部にはガス収納室22に連通する開口272が設けられ、燃焼室21内に空気や臭気ガスを供給する。
燃焼流規制板25は、燃焼流が水平方向に渦状に回転しながら水平方向に移動するような形状に設けられている。このような形状の燃焼規制板25を設けることにより、二次燃焼室2の中の燃焼ガスは一次燃焼室における燃焼流とは異なる方向に渦状に回転しながら水平方向に移動する燃焼流を発生させる。なお、燃焼流規制板25の形状は燃焼流を渦状に回転させる代わりに、ジグザグ状に複数回屈折させるように形成してもよい。二次燃焼室出口部26は燃焼室21の他端側端面の下部に接続されている。
The secondary combustion chamber 2 has a double structure of a combustion chamber 21 and a gas storage chamber 22 that covers the outside of the combustion chamber 21, and the combustion chamber 21 covers the bottom surface of the gas storage chamber 22 in the gas storage chamber 22. It is supported by a support 23 planted on the base 20 that is also used.
The combustion chamber 21 is connected to the primary combustion chamber outlet 17 and has a secondary combustion chamber inlet 24 that is an intake port for combustion gas burned in the primary combustion chamber 1, and a combustion flow provided inside the combustion chamber 21. It consists of a regulation plate 25 and a secondary combustion chamber outlet 26 that is an outlet for the burned combustion gas. The combustion chamber 21, the secondary combustion chamber inlet 24, and the secondary combustion chamber outlet 26 are all formed in a cylindrical shape. One end of the secondary combustion chamber inlet portion 24 passes through a hole formed in the wall surface 221 on the primary combustion chamber 1 side of the gas storage chamber 22 and is connected to the primary combustion chamber outlet portion 17. As shown in FIG. 4, the other end of the secondary combustion chamber inlet section 24 is connected to a hole 271 provided in the upper portion of the wall surface 27 on the inlet side of the combustion chamber 21. An opening 272 communicating with the gas storage chamber 22 is provided around the hole 271 of the wall surface 27, and air and odor gas are supplied into the combustion chamber 21.
The combustion flow restricting plate 25 is provided in such a shape that the combustion flow moves in the horizontal direction while rotating in a spiral shape in the horizontal direction. By providing the combustion regulating plate 25 having such a shape, the combustion gas in the secondary combustion chamber 2 generates a combustion flow that moves in a horizontal direction while rotating in a spiral shape in a direction different from the combustion flow in the primary combustion chamber. Let The shape of the combustion flow restricting plate 25 may be formed so as to be refracted a plurality of times in a zigzag manner instead of rotating the combustion flow in a spiral shape. The secondary combustion chamber outlet 26 is connected to the lower portion of the other end surface of the combustion chamber 21.

ガス収納室22の上部には臭気ガスを供給するための臭気ガスダクト(ガス導入口)28が接続されている。臭気ガスダクト28にはバルブ29が設けられており、バルブ29の開閉により臭気ガスの供給を制御する。
ガス収納室22の側部には、図2に示すように、空気を供給するための空気供給ダクト(空気導入口)30、31が接続されている。空気供給ダクト30、31の各々にはバルブ32、33が設けられており、バルブ32、33の開閉により空気の供給を制御する。また、ガス収納室22の横部には、のぞき窓34、35が形成されている。
排気室3は排気筒36を介して二次燃焼室出口部26に連設され、燃焼室21で燃焼した燃焼ガスは排気ダクト4を通過して排気ファン5により強制排気される。
An odor gas duct (gas inlet) 28 for supplying odor gas is connected to the upper portion of the gas storage chamber 22. The odor gas duct 28 is provided with a valve 29, and the supply of odor gas is controlled by opening and closing the valve 29.
As shown in FIG. 2, air supply ducts (air inlets) 30 and 31 for supplying air are connected to the side of the gas storage chamber 22. Each of the air supply ducts 30 and 31 is provided with valves 32 and 33, and air supply is controlled by opening and closing the valves 32 and 33. In addition, observation windows 34 and 35 are formed in the horizontal portion of the gas storage chamber 22.
The exhaust chamber 3 is connected to the secondary combustion chamber outlet 26 via an exhaust cylinder 36, and the combustion gas burned in the combustion chamber 21 passes through the exhaust duct 4 and is forcibly exhausted by the exhaust fan 5.

つぎに、本実施例による燃焼装置の燃焼方法について説明する。以下の説明においては、臭気ガスとして有機廃棄物を熟成醗酵させる際に発生するアンモニアを例に説明する。
まず、バルブ29を閉じ、バルブ32、33を開いた状態で、一次燃焼室1の底部12に設けられた燃料供給口15から燃料となる廃油を供給する。底部12には燃焼される廃油が溜まり、底部12は燃焼皿の働きをする。つぎに、点検口14から点火用燃焼物を廃油の溜まっている底部12の上に供給し、送風ファンにより空気供給管16から空気を送り込むと、垂直空気噴出管18および水平空気噴出管19から一次燃焼室1に空気が送り込まれて燃焼を開始する。一方、底部12の近傍では、空気噴出孔19Aから空気が回転を生じるように供給され、廃油は気化しつつ燃焼し、燃焼が盛んになるにつれて燃焼温度が上昇し、空気噴出孔19Aから供給される空気によって燃焼ガスと空気の攪拌が促進される。
このとき、排気ファン5を回転させることによって一次燃焼室1、二次燃焼室2および排気室3内の燃焼ガスは吸引されるため、一次燃焼室1内の燃焼ガスは一次燃焼室1内を上昇し、渦状に回転する流れとなり、空気と燃焼ガスとの混合が促進されるとともに、空気噴出孔18Aから供給される新たな空気によって更に燃焼が促進される。
Next, a combustion method of the combustion apparatus according to the present embodiment will be described. In the following description, ammonia generated when aging fermentation of organic waste as odor gas will be described as an example.
First, in a state where the valve 29 is closed and the valves 32 and 33 are opened, waste oil as fuel is supplied from the fuel supply port 15 provided in the bottom 12 of the primary combustion chamber 1. Waste oil to be burned accumulates in the bottom portion 12, and the bottom portion 12 functions as a combustion dish. Next, when the combustion product for ignition is supplied from the inspection port 14 onto the bottom 12 where the waste oil is accumulated, and the air is sent from the air supply pipe 16 by the blower fan, the vertical air jet pipe 18 and the horizontal air jet pipe 19 Air is sent into the primary combustion chamber 1 to start combustion. On the other hand, in the vicinity of the bottom portion 12, air is supplied from the air ejection holes 19 </ b> A so as to rotate, and the waste oil is combusted while being vaporized. The combustion temperature rises as the combustion increases, and is supplied from the air ejection holes 19 </ b> A. The stirring of the combustion gas and air is promoted by the air.
At this time, the combustion gas in the primary combustion chamber 1, the secondary combustion chamber 2, and the exhaust chamber 3 is sucked by rotating the exhaust fan 5, so that the combustion gas in the primary combustion chamber 1 passes through the primary combustion chamber 1. Ascending and rotating in a spiral shape, the mixing of air and combustion gas is promoted, and combustion is further promoted by new air supplied from the air ejection holes 18A.

一次燃焼室1の上部に至った燃焼ガスは、一次燃焼室出口部17から二次燃焼室入口部20を通って二次燃焼室2の燃焼室21に導入される。二次燃焼室2内に導入された燃焼ガスは、燃焼流規制板25によって渦状に回転する流れとなって二次燃焼室出口部26に移動する。このとき、空気供給ダクト30、31からガス収納室22に導入された空気がガス供給孔272から燃焼室21内に導入され、燃焼ガスは渦状に回転する流れによって、燃焼ガスと空気の攪拌が更に促進され、燃焼が盛んになり、燃焼温度は1500度以上に上昇して完全燃焼する。
燃焼室21内で燃焼した燃焼ガスは、排気ファン5により二次燃焼室出口部26から排気室3に導かれ、排気室3内を熱を奪われながら上昇して燃焼温度を低下させつつ排気ダクト4から外部に放出される。このとき、燃焼は完全燃焼しているので、廃油は完全分解されて、ダイオキシン、SOxなどの公害物質の含有量が数10分の1〜数百分の1と非常に小さいきれいな排気が得られる。NOxはダイオキシンやSOxよりも減少割合は小さいものの、数分の1に減少する。
Combustion gas reaching the upper portion of the primary combustion chamber 1 is introduced from the primary combustion chamber outlet portion 17 into the combustion chamber 21 of the secondary combustion chamber 2 through the secondary combustion chamber inlet portion 20. The combustion gas introduced into the secondary combustion chamber 2 moves to the secondary combustion chamber outlet portion 26 as a flow rotating in a spiral shape by the combustion flow regulating plate 25. At this time, the air introduced into the gas storage chamber 22 from the air supply ducts 30 and 31 is introduced into the combustion chamber 21 through the gas supply holes 272, and the combustion gas and the air are stirred by the flow rotating in a spiral shape. Further, the combustion is promoted and the combustion temperature rises to 1500 ° C. or more to complete combustion.
The combustion gas burned in the combustion chamber 21 is led from the secondary combustion chamber outlet 26 to the exhaust chamber 3 by the exhaust fan 5 and rises while taking heat away from the exhaust chamber 3 to reduce the combustion temperature. It is discharged from the duct 4 to the outside. At this time, since the combustion is complete combustion, the waste oil is completely decomposed, and a clean exhaust with a content of pollutants such as dioxin and SOx as small as several tenths to one hundredths is obtained. . Although NOx is smaller than dioxin and SOx, it decreases to a fraction.

こうして一次燃焼室1および二次燃焼室2内における燃焼が高温で安定した状態になったとき、バルブ29を開き、バルブ32、33を閉じると、臭気ガスダクト28からガス収納室22に導入されたアンモニアガスがガス供給孔272から燃焼室21内に導入される。導入されたアンモニアガスは一次燃焼室1からの燃焼ガスとともに渦状に回転する流れになって攪拌されながら高温で燃焼する。アンモニアは高温で燃焼されると水とNOxに分解されるが、NOxはさらに供給されるアンモニアとともに燃焼されると、4NH+4NO+O→4N+6HOで表わされる化学反応により窒素ガスと水に分解されるので、完全に無臭化、無毒化される。 Thus, when the combustion in the primary combustion chamber 1 and the secondary combustion chamber 2 became stable at a high temperature, when the valve 29 was opened and the valves 32 and 33 were closed, the odor gas duct 28 was introduced into the gas storage chamber 22. Ammonia gas is introduced into the combustion chamber 21 from the gas supply hole 272. The introduced ammonia gas combusts at a high temperature while being stirred in a flow rotating in a spiral with the combustion gas from the primary combustion chamber 1. Ammonia is decomposed into water and NOx when burned at a high temperature. However, when NOx is further burned together with the supplied ammonia, nitrogen gas and nitrogen gas are decomposed by a chemical reaction represented by 4NH 3 + 4NO + O 2 → 4N 2 + 6H 2 O. Since it is decomposed into water, it is completely non-brominated and detoxified.

このように、二次燃焼室2内にアンモニアを導入して燃焼させることによりアンモニアは無臭化、無毒化されて、窒素ガスと水が排気ダクト4から外部に放出される。同時に、一次燃焼室1内で廃油を燃焼したときに生じるNOxも二次燃焼室2内でアンモニアとともに燃焼させることにより窒素ガスと水に分解することができる。したがって、本実施例による燃焼装置は、NOxの発生量を数10分の1〜数百分の1に大きく低減させることができる。
本実施例による燃焼装置は、底部12に溜めた液体燃料を気化して燃焼する一次燃焼室1と、一次燃焼室1に連設された二次燃焼室2とを有する燃焼装置であり、一次燃焼室1を、縦型の燃焼壁11と、液体燃料を溜める底部12と、燃焼壁11の上部で二次燃焼室2に連設される一次燃焼室出口部17と、一次燃焼室1のほぼ中心に配置される垂直空気噴出管18とから構成し、二次燃焼室2を、横型の燃焼室21と、一次燃焼室出口部17に連設して一次燃焼室1で燃焼した燃焼ガスを取り入れる二次燃焼室入口部24と、二次燃焼室2の内部に設けられた燃焼流規制板25と、燃焼ガスの取り出し口である二次燃焼室出口部26とから構成し、二次燃焼室入口部24を燃焼室21の一端側端面に、二次燃焼室出口部26を燃焼室21の他端側端面にそれぞれ接続し、燃焼流を排気ダクト4外へ導く排気ファン5を二次燃焼室2の下流側に設け、複数の空気噴出孔19Aを水平空気噴出管19に設け、燃焼流規制板25を螺旋形状とし、一次燃焼室1では空気噴出孔18A、19Aによって燃焼ガスを渦状に回転させて上昇させ、二次燃焼室2では一次燃焼室1の上部に至った燃焼ガスを二次燃焼室2の一端側端部から他端側端部の方向に、螺旋形状の燃焼流規制板25によって回転させて移動させるものである。
このように本実施例による燃焼装置は、一次燃焼室1を縦型の燃焼壁11、二次燃焼室2を横型の燃焼室21で構成し、一次燃焼室1では空気噴出孔19によって燃焼ガスを渦状に回転させて上昇させ、二次燃焼室2では一次燃焼室1の上部に至った燃焼ガスを二次燃焼室2の一端側端部から他端側端部の方向に移動させることで、一次燃焼室1を上昇した燃焼ガスは、水平方向に流れ方向を変えて、二次燃焼室2の一端側端部から他端側端部に向かって流れ、また、二次燃焼室2では、螺旋形状の燃焼流規制板25によって渦状に回転する燃焼流を発生させることで、渦状に回転する流れとなる。更に、燃焼流を排気ダクト4外へ導く排気ファン5を二次燃焼室2の下流側に設けることで、燃焼ガスを強制的に水平方向に向かわせることができる。
また、本実施例による燃焼装置は、底部12に溜めた液体燃料を気化して燃焼する一次燃焼室1と、一次燃焼室1に連設された二次燃焼室2とを有する燃焼装置であり、一次燃焼室1を、縦型の燃焼壁11と、液体燃料を溜める底部12と、燃焼壁11の上部で二次燃焼室2に連設される一次燃焼室出口部17と、一次燃焼室1のほぼ中心に配置される垂直空気噴出管18とから構成し、二次燃焼室2を、横型の燃焼室21と、一次燃焼室出口部17に連設して一次燃焼室1で燃焼した燃焼ガスを取り入れる二次燃焼室入口部24と、二次燃焼室2の内部に設けられた燃焼流規制板25と、燃焼ガスの取り出し口である二次燃焼室出口部26とから構成し、二次燃焼室入口部24を燃焼室21の一端側端面に、二次燃焼室出口部26を燃焼室21の他端側端面にそれぞれ接続し、燃焼流を排気ダクト4外へ導く排気ファン5を二次燃焼室2の下流側に設け、複数の空気噴出孔19Aを水平空気噴出管19に設け、燃焼流規制板25を複数の板から構成し、一次燃焼室1では空気噴出孔19Aによって燃焼ガスを渦状に回転させて上昇させ、二次燃焼室2では一次燃焼室1の上部に至った燃焼ガスを二次燃焼室2の一端側端部から他端側端部の方向に、燃焼流規制板25によって流れ方向を屈折させて移動させるものである。
本実施例の燃焼装置によれば、一次燃焼室1の底部で気化した燃焼ガスは、一次燃焼室1の内部で渦状に回転するため、燃焼ガスと空気が攪拌される。従って、一次燃焼室1での燃焼は完全燃焼に近づく。そして一次燃焼を終えた燃焼ガスは二次燃焼室2へ移動する。この二次燃焼室2に移行した燃焼ガスは、二次燃焼室の内部において更に渦状の回転によって、燃焼ガスと空気とは攪拌されるため更に完全燃焼に近づかせることができる。
そして本実施例による燃焼装置は、二次燃焼室2に空気を導入する開閉自在の空気供給ダクト(空気導入口)30、31と、臭気ガスを導入する開閉自在の臭気ガスダクト(ガス導入口)28を設け、まず空気供給ダクト(空気導入口)30、31から二次燃焼室に空気を導入することで、二次燃焼室2において燃焼温度が1500度以上の高温に上昇して完全燃焼する。その後、臭気ガスダクト(ガス導入口)28を開き、空気供給ダクト(空気導入口)30、31を閉じると、二次燃焼室2に臭気ガスが導入され、臭気ガスは高温で燃焼されるので、臭気ガスに起因する臭気を除去するとともに、空気汚染や人体へ悪影響を引き起こす臭気ガスを無臭化、無毒化することができる。
また本実施例による燃焼装置における二次燃焼室2は、燃焼室21と、燃焼室21の外部を覆うガス収納室22を有しており、燃焼室21は一次燃焼室1で燃焼した燃焼ガスを取り入れる二次燃焼室入口部24と、燃焼室21の内部に設けられた燃焼流規制板25と、燃焼した燃焼ガスを取り出す二次燃焼室出口部26で構成され、二次燃焼室入口部24の周辺部にはガス収納室22に連通する開口27が設けられており、空気供給ダクト(空気導入口)30、31と臭気ガスダクト(ガス導入口)28はガス収納室22に連通している。上記構成によれば、二次燃焼室2に空気および臭気ガスを選択的に導入可能であり、空気を導入しているときは燃焼ガスと空気とが攪拌されて高温で完全燃焼させることができ、二次燃焼室に臭気ガスを導入しているときは燃焼ガスと臭気ガスとが攪拌されて、臭気ガスを高温で燃焼させることができる。
また本実施例による燃焼装置に導入する臭気ガスとして、家畜の糞尿や生ゴミ等の有機廃棄物を堆肥化する堆肥化施設やし尿処理施設などで発生するアンモニアガスとすることで、アンモニアガスを窒素と水に熱分解して無臭、無毒化することができる。また、廃油などを燃焼して発生するNOxを分解することができるので、排気中の公害成分を飛躍的に減少させることができる。
以上の説明においては、臭気ガスとしてアンモニアを例に説明したが、硫化水素などの臭気ガスも同様に無臭化、無毒化することができる。
Thus, ammonia is made non-bromide and non-toxic by introducing ammonia into the secondary combustion chamber 2 and burning it, and nitrogen gas and water are discharged from the exhaust duct 4 to the outside. At the same time, NOx generated when the waste oil is burned in the primary combustion chamber 1 can also be decomposed into nitrogen gas and water by burning together with ammonia in the secondary combustion chamber 2. Therefore, the combustion apparatus according to the present embodiment can greatly reduce the amount of NOx generated to 1/10 to 1/100.
The combustion apparatus according to the present embodiment is a combustion apparatus having a primary combustion chamber 1 that vaporizes and burns the liquid fuel stored in the bottom 12 and a secondary combustion chamber 2 that is connected to the primary combustion chamber 1. The combustion chamber 1 includes a vertical combustion wall 11, a bottom portion 12 for storing liquid fuel, a primary combustion chamber outlet 17 connected to the secondary combustion chamber 2 at the top of the combustion wall 11, and the primary combustion chamber 1. Combustion gas composed of a vertical air jet pipe 18 disposed substantially at the center and combusting in the primary combustion chamber 1 with the secondary combustion chamber 2 connected to the horizontal combustion chamber 21 and the primary combustion chamber outlet 17. Is composed of a secondary combustion chamber inlet portion 24 for taking in gas, a combustion flow restricting plate 25 provided in the secondary combustion chamber 2, and a secondary combustion chamber outlet portion 26 which is a combustion gas outlet. The combustion chamber inlet 24 is at one end of the combustion chamber 21 and the secondary combustion chamber outlet 26 is at the combustion chamber 21. An exhaust fan 5 that is connected to each end face and leads the combustion flow to the outside of the exhaust duct 4 is provided on the downstream side of the secondary combustion chamber 2, and a plurality of air injection holes 19A are provided in the horizontal air injection pipe 19 to restrict combustion flow. The plate 25 has a spiral shape, and in the primary combustion chamber 1, the combustion gas is swirled and raised by the air ejection holes 18 </ b> A and 19 </ b> A, and in the secondary combustion chamber 2, the combustion gas reaching the upper portion of the primary combustion chamber 1 is secondary. The combustion chamber 2 is rotated and moved in the direction from one end to the other end by the helical combustion flow restricting plate 25.
Thus, in the combustion apparatus according to this embodiment, the primary combustion chamber 1 is composed of the vertical combustion wall 11 and the secondary combustion chamber 2 is composed of the horizontal combustion chamber 21, and the combustion gas is formed in the primary combustion chamber 1 by the air ejection holes 19. And the combustion gas that has reached the upper part of the primary combustion chamber 1 is moved in the direction from one end of the secondary combustion chamber 2 to the end of the other end. The combustion gas rising in the primary combustion chamber 1 changes the flow direction in the horizontal direction and flows from one end of the secondary combustion chamber 2 toward the other end, and in the secondary combustion chamber 2 A spirally rotating combustion flow is generated by the spiral combustion flow restricting plate 25, whereby a spirally rotating flow is obtained. Furthermore, by providing the exhaust fan 5 for guiding the combustion flow to the outside of the exhaust duct 4 on the downstream side of the secondary combustion chamber 2, the combustion gas can be forced to be directed in the horizontal direction.
The combustion apparatus according to the present embodiment is a combustion apparatus having a primary combustion chamber 1 for vaporizing and burning the liquid fuel stored in the bottom 12 and a secondary combustion chamber 2 connected to the primary combustion chamber 1. The primary combustion chamber 1 includes a vertical combustion wall 11, a bottom 12 for storing liquid fuel, a primary combustion chamber outlet 17 connected to the secondary combustion chamber 2 above the combustion wall 11, and a primary combustion chamber The secondary combustion chamber 2 is connected to the horizontal combustion chamber 21 and the primary combustion chamber outlet 17 so as to burn in the primary combustion chamber 1. It comprises a secondary combustion chamber inlet section 24 for taking in combustion gas, a combustion flow regulating plate 25 provided inside the secondary combustion chamber 2, and a secondary combustion chamber outlet section 26 which is a combustion gas outlet, The secondary combustion chamber inlet portion 24 is at one end face of the combustion chamber 21, and the secondary combustion chamber outlet portion 26 is at the combustion chamber. 1 is connected to the end face of the other end side, the exhaust fan 5 for guiding the combustion flow to the outside of the exhaust duct 4 is provided on the downstream side of the secondary combustion chamber 2, and a plurality of air ejection holes 19A are provided in the horizontal air ejection pipe 19, Combustion flow restricting plate 25 is composed of a plurality of plates. In primary combustion chamber 1, combustion gas is swirled and raised by air ejection holes 19 </ b> A, and in secondary combustion chamber 2, combustion reaches the upper portion of primary combustion chamber 1. The gas is moved from the one end side end portion of the secondary combustion chamber 2 to the other end side end portion by refracting the flow direction by the combustion flow restricting plate 25.
According to the combustion apparatus of the present embodiment, the combustion gas vaporized at the bottom of the primary combustion chamber 1 rotates in a vortex inside the primary combustion chamber 1, so that the combustion gas and air are agitated. Therefore, the combustion in the primary combustion chamber 1 approaches the complete combustion. The combustion gas that has finished primary combustion moves to the secondary combustion chamber 2. The combustion gas transferred to the secondary combustion chamber 2 can be brought closer to complete combustion because the combustion gas and the air are agitated by further swirling rotation inside the secondary combustion chamber.
The combustion apparatus according to the present embodiment includes an openable / closable air supply duct (air inlet) 30 and 31 for introducing air into the secondary combustion chamber 2 and an openable / closable odor gas duct (gas inlet) for introducing odor gas. 28 is provided, and air is first introduced into the secondary combustion chamber from the air supply ducts (air inlets) 30 and 31, whereby the combustion temperature rises to a high temperature of 1500 ° C. or more in the secondary combustion chamber 2 and complete combustion occurs. . Thereafter, when the odor gas duct (gas introduction port) 28 is opened and the air supply ducts (air introduction ports) 30, 31 are closed, the odor gas is introduced into the secondary combustion chamber 2, and the odor gas is burned at a high temperature. The odor caused by the odor gas can be removed, and the odor gas that causes air pollution and adverse effects on the human body can be made non-brominated and non-toxic.
The secondary combustion chamber 2 in the combustion apparatus according to the present embodiment has a combustion chamber 21 and a gas storage chamber 22 that covers the outside of the combustion chamber 21, and the combustion chamber 21 is a combustion gas burned in the primary combustion chamber 1. Is composed of a secondary combustion chamber inlet 24, a combustion flow regulating plate 25 provided inside the combustion chamber 21, and a secondary combustion chamber outlet 26 for taking out the combustion gas. 24 is provided with an opening 27 communicating with the gas storage chamber 22. The air supply ducts (air introduction ports) 30 and 31 and the odor gas duct (gas introduction port) 28 communicate with the gas storage chamber 22. Yes. According to the above configuration, it is possible to selectively introduce air and odor gas into the secondary combustion chamber 2, and when the air is introduced, the combustion gas and air can be agitated and completely burned at a high temperature. When the odor gas is introduced into the secondary combustion chamber, the combustion gas and the odor gas are agitated, and the odor gas can be burned at a high temperature.
In addition, the odor gas introduced into the combustion apparatus according to the present embodiment is ammonia gas generated in composting facilities and human waste processing facilities that compost organic waste such as livestock manure and garbage, so that ammonia gas is It can be pyrolyzed into nitrogen and water to make it odorless and non-toxic. Further, since NOx generated by burning waste oil or the like can be decomposed, pollution components in the exhaust gas can be drastically reduced.
In the above description, ammonia has been described as an example of the odor gas, but odor gas such as hydrogen sulfide can be made non-brominated and non-toxic in the same manner.

本発明による燃焼装置は、アンモニアガスを排出する家畜の糞尿や生ゴミ等の有機廃棄物の堆肥化装置、し尿処理装置のアンモニアガス処理装置、硫化水素などの硫黄化合物を排出する廃物、廃水、下水、汚泥処理の処理槽、乾燥機、焼却炉などの排気ガス処理装置などに適用することができる。   Combustion apparatus according to the present invention is a composting apparatus for organic waste such as livestock manure and garbage that discharges ammonia gas, an ammonia gas processing apparatus for human waste processing apparatus, waste that discharges sulfur compounds such as hydrogen sulfide, waste water, The present invention can be applied to exhaust gas treatment devices such as sewage and sludge treatment tanks, dryers, and incinerators.

本発明の一実施例による燃焼装置の一部破断側面図The partially broken side view of the combustion apparatus by one Example of this invention 本実施例による燃焼装置の一部破断平面図Partially broken plan view of the combustion apparatus according to the present embodiment 本実施例による燃焼装置の空気噴出管の要部斜視図The principal part perspective view of the air jet pipe of the combustion apparatus by a present Example 本実施例による燃焼装置の二次燃焼室における燃焼室部分の入り口側壁面の正面図The front view of the entrance side wall surface of the combustion chamber part in the secondary combustion chamber of the combustion apparatus by a present Example

1 一次燃焼室
2 二次燃焼室
3 排気室
4 排気ダクト
5 排気ファン
11 燃焼壁
12 底部
13 蓋部
14 点検口
15 燃料供給口
16 空気供給管
17 一次燃焼室出口部
18 垂直空気噴出管
18A、19A 空気噴出孔
20 空気噴出管
21 燃焼室
22 ガス収納室
23 支持具
24 二次燃焼室入口部
25 燃焼流規制板
26 二次燃焼室出口部
27 燃焼室の壁面
28 臭気ガスダクト
29、32、33 バルブ
30、31 空気供給ダクト
36 排気筒
221 ガス収納室の壁面
271 孔
272 開口
DESCRIPTION OF SYMBOLS 1 Primary combustion chamber 2 Secondary combustion chamber 3 Exhaust chamber 4 Exhaust duct 5 Exhaust fan 11 Combustion wall 12 Bottom part 13 Cover part 14 Inspection port 15 Fuel supply port 16 Air supply pipe 17 Primary combustion chamber outlet part 18 Vertical air ejection pipe 18A, 19A Air ejection hole 20 Air ejection pipe 21 Combustion chamber 22 Gas storage chamber 23 Support 24 Secondary combustion chamber inlet 25 Combustion flow regulating plate 26 Secondary combustion chamber outlet 27 Combustion chamber wall 28 Odor gas ducts 29, 32, 33 Valve 30, 31 Air supply duct 36 Exhaust tube 221 Wall surface of gas storage chamber 271 Hole 272 Open

Claims (4)

燃料を燃焼させて下部から上部に向かって渦状に回転する燃焼流を発生させる一次燃焼室と、前記一次燃焼室に連設された二次燃焼室とを有する燃焼装置であって、前記二次燃焼室に空気を導入する開閉自在の空気導入口と、前記二次燃焼室に臭気ガスを導入する開閉自在のガス導入口とを設け、前記二次燃焼室は、燃焼室と、前記燃焼室の外部を覆うガス収納室とを有しており、前記燃焼室は前記一次燃焼室で燃焼した燃焼ガスを取り入れる入口部と、前記燃焼室の内部に設けられた燃焼流規制板と、燃焼した前記燃焼ガスを取り出す出口部とで構成され、前記燃焼室の前記入口部の周辺部には前記ガス収納室に連通する開口が設けられており、前記空気導入口と前記ガス導入口は前記ガス収納室に連通していることを特徴とする燃焼装置。 A combustion apparatus having a primary combustion chamber for burning a fuel and generating a combustion flow rotating in a spiral shape from the lower part to the upper part, and a secondary combustion chamber connected to the primary combustion chamber, An openable / closable air inlet for introducing air into the combustion chamber and an openable / closable gas inlet for introducing odor gas into the secondary combustion chamber are provided , the secondary combustion chamber comprising: a combustion chamber; and the combustion chamber A gas storage chamber covering the outside of the combustion chamber, and the combustion chamber burns with an inlet portion for taking in combustion gas burned in the primary combustion chamber, a combustion flow regulating plate provided inside the combustion chamber, and An outlet portion for taking out the combustion gas, and an opening communicating with the gas storage chamber is provided in a peripheral portion of the inlet portion of the combustion chamber, and the air inlet and the gas inlet are the gas combustion apparatus, characterized in that in communication with the storage chamber 前記臭気ガスがアンモニアガスであることを特徴とする請求項1に記載の燃焼装置。 The combustion apparatus according to claim 1, wherein the odor gas is ammonia gas. 燃料を燃焼させる一次燃焼室と、前記一次燃焼室に連設された二次燃焼室とを有し、前記二次燃焼室に空気を導入する開閉自在の空気導入口と、前記二次燃焼室に臭気ガスを導入する開閉自在のガス導入口とを設け、前記二次燃焼室は、燃焼室と、前記燃焼室の外部を覆うガス収納室とを有しており、前記燃焼室は前記一次燃焼室で燃焼した燃焼ガスを取り入れる入口部と、燃焼した前記燃焼ガスを取り出す出口部とで構成され、前記燃焼室の前記入口部の周辺部には前記ガス収納室に連通する開口が設けられており、前記空気導入口と前記ガス導入口は前記ガス収納室に連通している燃焼装置を用いた臭気ガス処理方法であって、前記一次燃焼室で燃料を燃焼させて下部から上部に向かって渦状に回転する燃焼流を発生させる第1の工程と、前記一次燃焼室に連設された前記二次燃焼室で前記燃焼流を高温化させる第2の工程と、前記二次燃焼室に前記臭気ガスを導入して燃焼させる第3の工程を有し、前記第3の工程に先立って、前記空気導入口から前記ガス収納室に導入された前記空気を前記開口から前記燃焼室内に導入して燃焼を行い、燃焼が高温で安定した状態になったときに前記ガス導入口を開いて前記第3の工程による前記臭気ガスの燃焼を行うことを特徴とする臭気ガス処理方法。 A primary combustion chamber for burning fuel; a secondary combustion chamber connected to the primary combustion chamber; an openable / closable air inlet for introducing air into the secondary combustion chamber; and the secondary combustion chamber The secondary combustion chamber has a combustion chamber and a gas storage chamber that covers the outside of the combustion chamber, and the combustion chamber is the primary chamber. An inlet portion for taking in combustion gas burned in the combustion chamber and an outlet portion for taking out the burned combustion gas are provided, and an opening communicating with the gas storage chamber is provided in the peripheral portion of the inlet portion of the combustion chamber. The air inlet and the gas inlet are odor gas treatment methods using a combustion device communicating with the gas storage chamber, and the fuel is combusted in the primary combustion chamber from the lower part to the upper part. A first step of generating a swirling combustion flow Possess a second step of high temperature of the combustion stream by the secondary combustion chamber provided continuously to the primary combustion chamber, a third step of burning by introducing the odorous gases in the secondary combustion chamber Prior to the third step, the air introduced into the gas storage chamber from the air introduction port was introduced into the combustion chamber from the opening, and combustion was performed, and the combustion became stable at a high temperature. An odor gas treatment method characterized in that the odor gas is combusted by the third step by opening the gas inlet occasionally . 前記第3の工程において前記空気の導入を停止することを特徴とする請求項3に記載の臭気ガス処理方法。 Odor gas treatment method according to claim 3, characterized in that stopping the introduction of the air in the third step.
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