JPH0325691B2 - - Google Patents

Info

Publication number
JPH0325691B2
JPH0325691B2 JP21381683A JP21381683A JPH0325691B2 JP H0325691 B2 JPH0325691 B2 JP H0325691B2 JP 21381683 A JP21381683 A JP 21381683A JP 21381683 A JP21381683 A JP 21381683A JP H0325691 B2 JPH0325691 B2 JP H0325691B2
Authority
JP
Japan
Prior art keywords
silo
chamber
residual ash
ash chamber
combustion
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP21381683A
Other languages
Japanese (ja)
Other versions
JPS60105815A (en
Inventor
Saburo Katayose
Kimihiro Katayose
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP21381683A priority Critical patent/JPS60105815A/en
Publication of JPS60105815A publication Critical patent/JPS60105815A/en
Publication of JPH0325691B2 publication Critical patent/JPH0325691B2/ja
Granted legal-status Critical Current

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/027Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/40Portable or mobile incinerators
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/12Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of plastics, e.g. rubber

Description

【発明の詳細な説明】 本発明は小型ゴミ焼却機に関する。[Detailed description of the invention] The present invention relates to a small garbage incinerator.

一般家庭、事業所では日夜ゴミが発生する。そ
のゴミの処理手段として焼却機が汎用されてお
り、その構造には種々のものがあるが、従来では
一日に発生するゴミの排出量が少ない(たとえば
200Kg以下)場合に好適な実用性の高い焼却機が
なかつた。
Garbage is generated day and night in ordinary households and businesses. Incinerators are widely used as a means of disposing of waste, and there are various structures, but conventional incinerators produce only a small amount of waste per day (for example,
(200Kg or less), there was no suitable and highly practical incinerator.

すなわち、排出量が少ない場合、一般に焼却は
容易とも考えられるが、ゴミは排出量に関係な
く、一般雑芥廃プラスチツクなど種類、性質の異
なるものが多く、ことに廃プラスチツクはガス量
が多く、燃焼のため必要な空気量が理論空気量の
3〜4倍を必要とし、この空気(2次空気)を与
えつつ、しかも高温雰囲気内で一定の滞溜時間を
持たせて熱分解しなければならない。そのため、
バーナーなどの機器や灯油、プロパンガスなどの
燃料を不可欠とし、かつ滞溜時間を得るには長い
煙道距離を必要とする。
In other words, if the amount of emissions is small, it is generally considered easy to incinerate, but regardless of the amount of emissions, garbage often has different types and properties such as general garbage plastics, and waste plastics in particular have a large amount of gas. The amount of air required for combustion is three to four times the theoretical amount, and it is necessary to provide this air (secondary air) while allowing a certain residence time in a high-temperature atmosphere for thermal decomposition. No. Therefore,
Equipment such as a burner and fuel such as kerosene or propane gas are essential, and a long flue distance is required to obtain the residence time.

このことから、従来では焼却処理量が少ないに
もかかわらず構造が不必要に大型化し、しかも廃
プラスチツクをうまく無煙、無臭で焼却すること
ができず、装置コストや運転コストが高価になる
という不具合を避けられなかつた。
As a result, the structure of the conventional method is unnecessarily large despite the small amount of incineration, and it is not possible to incinerate waste plastics smokelessly and odorlessly, resulting in high equipment and operating costs. I couldn't avoid it.

本発明は前記のような従来の焼却機の不具合を
解消するために研究を重ねて創案されたもので、
その目的とするところは、一般雑芥や廃プラスチ
ツクを無煙、無臭で効率よく処理できるきわめて
コンパクトなこの種焼却機を提供することにあ
る。
The present invention was created after repeated research to solve the problems of conventional incinerators as described above.
The purpose is to provide an extremely compact incinerator of this type that can efficiently process general garbage and waste plastics in a smokeless and odorless manner.

また本発明の目的は、上記に加え、ストーブに
類する室内暖房器としてあるいは給湯用の熱回収
機器として利用でき、屋内、屋外へ移動も容易に
行えるこの種小型焼却機を提供することにある。
In addition to the above, an object of the present invention is to provide a small incinerator of this type that can be used as an indoor heater similar to a stove or as a heat recovery device for hot water supply, and can be easily moved indoors or outdoors.

上記目的を達成するため本発明は、本体に、雑
芥を収蔵して内熱乾留を行うサイロと、このサイ
ロとロストルで仕切られた残灰室と、残灰室をめ
くら板で仕切られ、残灰室からの輻射熱で廃プラ
スチツクを外熱乾留する下室を順次段設すると共
に、下室からサイロを貫いて筒状の燃焼タワーを
挿設し、この燃焼タワーには、サイロに対応する
位置に雑芥乾留ガス導入孔を、残灰室を対応する
位置に2次エア導入孔を、下室に対応する位置に
高分子乾留ガス導入孔を夫々設けたものである。
In order to achieve the above object, the present invention has a main body including a silo for storing garbage and performing internal heat carbonization, a residual ash chamber separated from the silo by a rostol, and a residual ash chamber partitioned by a blind board. Lower chambers are successively installed to use radiant heat from the residual ash chamber to externally carbonize waste plastics, and a cylindrical combustion tower is inserted from the lower chamber through the silo. A garbage carbonization gas introduction hole is provided at a position corresponding to the residual ash chamber, a secondary air introduction hole is provided at a position corresponding to the residual ash chamber, and a polymer carbonization gas introduction hole is provided at a position corresponding to the lower chamber.

以下本発明の実施例を添付図面に基いて説明す
る。
Embodiments of the present invention will be described below with reference to the accompanying drawings.

第1図ないし第4図は本発明に係る小型ゴミ焼
却機の一実施例を示すもので、1はSS材などを
亜鉛メツキしてなる筒状の本体で、底部には耐火
材からなる床板11が設けられている。
Figures 1 to 4 show an embodiment of a small garbage incinerator according to the present invention. 1 is a cylindrical main body made of galvanized SS material, and the bottom is a floor plate made of fireproof material. 11 are provided.

2は前記本体1の頂部から下方に設けられたサ
イロで、主として雑芥類Aを収蔵して内熱乾留を
行うゾーンである。このサイロ2は蓋体21によ
り閉止され、蓋体21には開閉自在な投入口22
と一次エア取入口23が設けられている。そし
て、サイロ2の下部はロストル24で仕切られ、
側部にはのぞき穴25が設けられている。
Reference numeral 2 denotes a silo provided below from the top of the main body 1, and is a zone where miscellaneous garbage A is mainly stored and internal heat carbonization is performed. This silo 2 is closed by a lid 21, and the lid 21 has an input port 22 that can be opened and closed freely.
and a primary air intake port 23 are provided. The lower part of silo 2 is partitioned with rostle 24,
A peephole 25 is provided on the side.

3は前記サイロ2の底をなすロストル24の下
方に形成された残灰室で、残灰室3の下部には亜
鉛メツキ処理を施した耐熱鋼又は耐火材などから
なるめくら板5が張設されている。残灰室3の側
部には灰出し口を兼ねた二次エア取入口31が設
けられている。
3 is a residual ash chamber formed below the rostol 24 forming the bottom of the silo 2, and a blind plate 5 made of zinc-plated heat-resistant steel or fire-resistant material is stretched at the bottom of the residual ash chamber 3. has been done. A secondary air intake port 31 that also serves as an ash outlet is provided on the side of the residual ash chamber 3.

4はめくら板5から本体1の床板11にわたる
ゾーンに形成された下室であり、主として高分子
系ゴミBを処理するための空間である。この下室
4の側部には投入口41が設けられている。
A lower chamber 4 is formed in a zone extending from the blind plate 5 to the floor plate 11 of the main body 1, and is a space mainly for processing polymeric waste B. An input port 41 is provided on the side of the lower chamber 4.

6は燃焼タワーであり、筒状ないし管状をな
し、前記下室4からめくら板5、ロストル24を
貫いて蓋体21に到るように縦設されている。本
実施例ではこの燃焼タワー6の上端に煙突10を
同心状に嵌合している。
A combustion tower 6 has a cylindrical or tubular shape and is installed vertically from the lower chamber 4 through the blind plate 5 and the roaster 24 to reach the lid body 21. In this embodiment, a chimney 10 is fitted concentrically to the upper end of the combustion tower 6.

前記燃焼タワー6には、サイロ2に対応する部
位に雑芥類乾留ガスの導入孔7が形成され、残灰
室3に対応する部位には二次燃焼用エアの導入孔
8が形成され、下室4に対応する部位には高分子
乾留ガスの導入孔9が形成されている。前記各導
入孔7,8,9は本実施例では全周に等間隔で形
成している。各導入孔7,8,9の大きさや数は
各部位で変化していてもよく、また接続方向の気
流や乱流を生ずるように形状等を調整してもよ
い。
In the combustion tower 6, an introduction hole 7 for garbage carbonization gas is formed in a part corresponding to the silo 2, and an introduction hole 8 for secondary combustion air is formed in a part corresponding to the residual ash chamber 3. An introduction hole 9 for polymer carbonization gas is formed in a portion corresponding to the lower chamber 4 . In this embodiment, the introduction holes 7, 8, and 9 are formed at equal intervals around the entire circumference. The size and number of the introduction holes 7, 8, and 9 may be changed in each part, and the shape etc. may be adjusted so as to generate airflow or turbulence in the connection direction.

前記サイロ2は、残灰室3や下室4よりも大き
な容積に構成されており、下室4の底部すなわち
本体1の底側部にはコロ部材12が取付けられて
いる。
The silo 2 has a larger volume than the residual ash chamber 3 and the lower chamber 4, and a roller member 12 is attached to the bottom of the lower chamber 4, that is, to the bottom side of the main body 1.

第5図は本発明の別の実施例を示すもので、本
体1の外周に耐熱鋼板131などにより水壁13
を囲繞形成し、水壁13の適所に導水配管14と
給湯配管15を接続したものである。
FIG. 5 shows another embodiment of the present invention, in which a water wall 13 is formed around the outer periphery of the main body 1 by a heat-resistant steel plate 131 or the like.
A water supply pipe 14 and a hot water supply pipe 15 are connected to appropriate places on the water wall 13.

本発明は上記のような構成からなるので、ゴミ
の焼却にあたつては、雑芥類Aを投入口22から
サイロ2に装入し、高分子系ゴミBを投入口41
から下室4に装入する。そして、まず雑芥類Aを
適宜の手段により着火する。
Since the present invention has the above-described configuration, when incinerating garbage, garbage A is charged into the silo 2 through the input port 22, and polymeric garbage B is charged into the silo 2 through the input port 41.
From there, it is charged into the lower chamber 4. First, garbage A is ignited by appropriate means.

これにより、第6図で示すように、雑芥類Aは
サイロ2のロストル24に堆積した状態で内燃乾
留が開始され、ガス化したものはチヤーとなつて
ロストル付近にてオキ燃焼し、このオキ燃焼によ
りサイロ2中に挿設されている燃焼タワー6が高
温850〜900℃に加熱され、高温熱雰囲気帯とな
る。それと共に、一次エア取入口23から導入さ
れたエアが雑芥類Aを抜けて下降し、雑芥類より
発生した黒煙、臭気を含む有機性ガスは、前記オ
キ燃焼熱により燃焼タワー6の周辺で高温に加熱
されながら乾留ガスの導入孔7から燃焼タワー6
に連続して導入される。
As a result, as shown in Fig. 6, internal combustion carbonization starts with garbage A being deposited in the rostol 24 of silo 2, and the gasified material becomes a char and is ignited near the rostol. The combustion tower 6 inserted in the silo 2 is heated to a high temperature of 850 to 900°C by the oyster combustion, creating a high-temperature thermal atmosphere zone. At the same time, the air introduced from the primary air intake port 23 passes through the garbage A and descends, and the black smoke and odor-containing organic gas generated from the garbage are transferred to the combustion tower 6 due to the heat of combustion of the gas. The combustion tower 6 is heated from the carbonization gas introduction hole 7 to the combustion tower 6 while being heated to a high temperature in the surrounding area.
will be introduced successively.

そして、一方では二次エア取入口31から燃焼
に必要な二次エアが残灰室3に供給される。残灰
室3は、オキ燃焼が完了しあるいは若干の燃焼分
の残つたチヤーがロストル6から落下堆積してい
るため、500〜600℃の高温状態となつている。し
たがつて、二次エア取入口31から供給された二
次エアは、この残灰室3を通過する間に加熱され
てガス燃焼に適する高温エアとなり、残灰室3に
位置する燃焼タワー6の二次燃焼用エア導入孔8
から燃焼タワー内に供給される。これがさきのサ
イロ2からの雑芥乾留ガスと混合されるため、燃
焼タワー中にてきわめて安定した熱分解が行わ
れ、無煙、無臭の状態で煙突10から大気中に放
散される。
On the other hand, secondary air necessary for combustion is supplied to the residual ash chamber 3 from the secondary air intake port 31. The residual ash chamber 3 is in a high temperature state of 500 to 600° C. because the ash combustion has been completed or some char remaining from the combustion has fallen and accumulated from the roaster 6. Therefore, the secondary air supplied from the secondary air intake port 31 is heated while passing through the residual ash chamber 3 and becomes high-temperature air suitable for gas combustion. Secondary combustion air introduction hole 8
is supplied into the combustion tower. Since this is mixed with the waste carbonization gas from the previous silo 2, extremely stable thermal decomposition takes place in the combustion tower, and it is released into the atmosphere from the chimney 10 in a smokeless and odorless state.

そして、上記のようなサイロ2での処理が行わ
れた場合、オキ燃焼熱は本体1を伝導して下室4
の外周に伝われると共に、高温の残灰室3の底で
あるめくら板5および内挿状態の燃焼タワー6を
介して内部から下室4に伝達され、これらの輻射
熱により下室内は高温化し、ここに装入されてい
る高分子系ゴミBは外熱乾留を受ける。
When the above-mentioned treatment is performed in the silo 2, the oki combustion heat is conducted through the main body 1 and flows into the lower chamber 4.
The radiant heat is transmitted to the outer periphery of the ash chamber 3, and is also transmitted from the inside to the lower chamber 4 via the blind plate 5, which is the bottom of the high-temperature residual ash chamber 3, and the inserted combustion tower 6, and due to these radiant heat, the temperature inside the lower chamber becomes high. The polymer waste B charged here undergoes external heat carbonization.

高分子系ゴミBはその焼却に多量の燃焼用エア
を必要とし、しかもこの空気量のほかに高温雰囲
気内での一定の滞溜時間が必要とされており、そ
のため小型ゴミ焼却機では無煙、無臭での焼却が
不可能とされていた。しかし本発明においては、
さきのように下室4において輻射熱で外熱乾留を
行い、発生した高分子乾留ガスは導入孔9から燃
焼タワー6に導入され、その燃焼タワー6が上部
でオキ燃焼熱と雑芥乾留ガスの分解熱により高温
雰囲気化しており、しかも残灰室3に供給した二
次エアが高温化して燃焼タワー中に連続供給され
る。そのため、高分子乾留ガスは燃焼タワー6に
おいて、きわめて確実かつ安定的に熱分解し、無
煙、無臭の排気となつて煙突10から放散され
る。
Polymer waste B requires a large amount of combustion air to incinerate, and in addition to this amount of air, a certain residence time in a high-temperature atmosphere is also required. Incineration without odor was considered impossible. However, in the present invention,
As before, external heat carbonization is performed in the lower chamber 4 using radiant heat, and the generated carbonized polymer gas is introduced into the combustion tower 6 through the inlet hole 9, and the combustion tower 6 combines the ocher combustion heat and the waste carbonized gas at the top. The decomposition heat creates a high-temperature atmosphere, and the secondary air supplied to the residual ash chamber 3 is heated to a high temperature and is continuously supplied into the combustion tower. Therefore, the carbonized polymer gas is thermally decomposed extremely reliably and stably in the combustion tower 6, and is emitted from the chimney 10 as smokeless and odorless exhaust gas.

そして、この高分子乾留ガスの熱分解により燃
焼タワー6は高温熱雰囲気が持続的に形成される
ため、サイロ2に収容されている雑芥類Aの乾燥
−ガス化が促進され、これによりオキ燃焼が安定
化し、このオキ燃焼熱により残灰室3を通る二次
エアの加熱および下室4に収容されている高分子
系ゴミBの外熱乾留も安定する。
Since a high-temperature thermal atmosphere is continuously formed in the combustion tower 6 due to the thermal decomposition of this polymer carbonization gas, the drying and gasification of the garbage A stored in the silo 2 is promoted, and as a result, the Combustion is stabilized, and the heating of the secondary air passing through the residual ash chamber 3 and the external heat carbonization of the polymeric waste B accommodated in the lower chamber 4 are also stabilized by this oxygen combustion heat.

高温熱雰囲気帯である燃焼タワー6はタテ型で
抵抗が少ないため炉内を不必要に負圧にすること
がなく、前記のように熱効率が合理化しているた
め煙道に必要な所要面積も小さくて済む。
The combustion tower 6, which is a high-temperature thermal atmosphere zone, is vertical and has low resistance, so there is no unnecessary negative pressure inside the furnace, and as mentioned above, the thermal efficiency is streamlined, so the area required for the flue is also reduced. It's small enough.

なお、本体1の底部にコロ部材12を有してい
るため移動が簡単に行え、寒冬期においては室内
に移設することにより焼却機兼ストーブのような
室内暖戻器として熱利用することができ、夏期に
おいては屋外へ移置することにより焼却機として
使用できる。
In addition, since the body 1 has a roller member 12 at the bottom, it can be easily moved, and in cold winter months, by moving it indoors, the heat can be used as an indoor warmer like an incinerator and stove. During the summer, it can be moved outdoors and used as an incinerator.

また、第5図のように本体1の外側に水壁13
を囲繞した場合には、ゴミ焼却により生じた熱量
が水壁13で熱回収されるため、配管14,15
により給湯、暖房等を同時に行うことができ、ゴ
ミを灯油やプロパンガスと同様の高カロリーの燃
料として有効に利用することができるものであ
る。
In addition, as shown in FIG.
When surrounding the pipes 14 and 15, the heat generated by waste incineration is recovered by the water wall 13.
With this system, hot water supply, space heating, etc. can be performed at the same time, and garbage can be effectively used as a high-calorie fuel similar to kerosene or propane gas.

以上説明した本発明によるときには、本体1
に、主として雑芥類を収蔵しこれを内熱乾留する
サイロ2と、このサイロ2とロストルで仕切られ
た残灰室3と、該残灰室3とめくら板5で仕切ら
れ、残灰室の輻射熱等により主として高分子系ゴ
ミを外熱乾留する下室4を順次形成すると共に、
下室4からサイロ2を貫いて筒状の燃焼タワー6
を縦設し、この燃焼タワー6には、サイロ2に対
応する位置に雑芥乾留ガスの導入孔7を、残灰室
3に対応する位置に二次燃焼用エア導入孔8を、
下室4に対応する位置に高分子乾留ガス導入孔9
を夫々設け、サイロ2で雑芥類を内熱乾留し、チ
ヤーのオキ燃焼熱により有機性ガスの加熱と内挿
燃焼タワー6の高温下を行わしめ、雑芥焼却後の
チヤーを利用して残灰室3により導入二次エアの
高温下を行わしめ、かつ残灰室3、本体1及び燃
焼タワー6の輻射熱により下室4で高分子系ゴミ
の外熱乾留を行わしめ、発生した雑芥乾留ガスと
高分子系乾留ガスを導入孔7,9から高温雰囲気
帯の燃焼タワー6に導入して、ここでさきの燃焼
用高温二次エアと混合して熱分解するようにした
ので、きわめて小型、コンパクトかつ簡単な構造
により、雑芥類や高分子系ゴミを無煙無臭の状態
で処理することができ、バーナーや重油なども使
用せず、構造も簡単なため安価な焼却機とするこ
とができるというすぐれた効果が得られる。
According to the present invention explained above, the main body 1
There is a silo 2 that mainly stores miscellaneous garbage and for internally carbonizing it, a residual ash chamber 3 separated from the silo 2 by a rostol, and a residual ash chamber 3 separated from the residual ash chamber 3 by a blind plate 5. A lower chamber 4 is sequentially formed in which polymer waste is mainly carbonized by external heat using radiant heat, etc.
A cylindrical combustion tower 6 extends from the lower chamber 4 through the silo 2.
is installed vertically, and this combustion tower 6 has an inlet hole 7 for waste carbonization gas at a position corresponding to the silo 2, and an air inlet hole 8 for secondary combustion at a position corresponding to the residual ash chamber 3.
A polymer carbonization gas introduction hole 9 is located at a position corresponding to the lower chamber 4.
The waste is internally carbonized in the silo 2, and the organic gas is heated by the combustion heat of the oki in the chir, and the interpolation combustion tower 6 is heated to a high temperature. The secondary air introduced into the residual ash chamber 3 is heated to a high temperature, and the radiant heat of the residual ash chamber 3, the main body 1, and the combustion tower 6 performs external heat carbonization of polymeric waste in the lower chamber 4, and the generated miscellaneous substances are removed. The waste carbonization gas and polymer carbonization gas are introduced into the combustion tower 6 in the high temperature atmosphere zone through the introduction holes 7 and 9, where they are mixed with the high temperature secondary air for combustion and thermally decomposed. The extremely small, compact, and simple structure allows garbage and polymeric waste to be processed in a smokeless and odorless manner. It does not require a burner or heavy oil, and its simple structure makes it an inexpensive incinerator. You can get excellent results by being able to do this.

本発明は一日のゴミの排出量の少ない各種事業
所、旅館、スキー場、一般家庭などに好適であ
り、ストーブ類を兼ねた焼却機あるいは給湯手段
を兼ねた焼却機として利用することができる。
The present invention is suitable for various businesses, inns, ski resorts, general households, etc. where the amount of waste generated per day is small, and can be used as an incinerator that also functions as a stove or as a hot water supply means. .

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

第1図は本発明に係る小型ゴミ焼却機の一実施
例を示す断面図、第2図は第1図−線にそう
断面図、第3図は第1図−線にそう断面図、
第4図は第1図−線にそう断面図、第5図は
本発明の別の実施例を示す一部切欠側面図、第6
図は本発明の作動原理を示す概略図である。 1……本体、2……サイロ、3……残灰室、4
……下室、5……めくら板、6……燃焼タワー、
7……雑芥乾留ガス導入孔、8……二次燃焼用エ
ア導入孔、9……高分子乾留ガス導入孔。
FIG. 1 is a cross-sectional view showing an embodiment of a small garbage incinerator according to the present invention, FIG. 2 is a cross-sectional view along the line shown in FIG. 1, and FIG. 3 is a cross-sectional view taken along the line shown in FIG.
FIG. 4 is a sectional view along the line of FIG. 1, FIG. 5 is a partially cutaway side view showing another embodiment of the present invention, and FIG.
The figure is a schematic diagram illustrating the operating principle of the invention. 1... Main body, 2... Silo, 3... Ash chamber, 4
... Lower chamber, 5 ... Blind board, 6 ... Combustion tower,
7...Miscellaneous carbonized gas introduction hole, 8...Secondary combustion air introduction hole, 9...Polymer carbonized gas introduction hole.

Claims (1)

【特許請求の範囲】 1 本体1に、主として雑芥類を収蔵しこれを内
熱乾留するサイロ2と、このサイロ2とロストル
で仕切られた残灰室3と、該残灰室3とめくら板
5で仕切られ、残灰室等からの輻射熱により主と
して高分子系ゴミを外熱乾留する下室4を順次形
成すると共に、下室4からサイロ2を貫いて筒状
の燃焼タワー6を縦設し、この燃焼タワー6に
は、サイロ2に対応する位置に雑芥乾留ガスの導
入孔7を、残灰室3に対応する位置に二次燃焼用
エアの導入孔8を、下室4に対応する位置に高分
子乾留ガスの導入孔9を夫々設けたことを特徴と
する小型ゴミ焼却機。 2 サイロ2が残灰室3および下室4より容積を
大きく構成されている特許請求の範囲第1項記載
の小型ゴミ焼却機。 3 本体1が、外周に水壁13を有しているもの
を含む特許請求の範囲第1項記載の小型ゴミ焼却
機。 4 本体1が下部にコロ部材12を有しているも
のを含む特許請求の範囲第1項記載の小型ゴミ焼
却機。
[Scope of Claims] 1 The main body 1 includes a silo 2 that mainly stores miscellaneous garbage and for internally carbonizing it, a residual ash chamber 3 separated from the silo 2 by a rostol, and a blind between the residual ash chamber 3 and the silo 2. A lower chamber 4 is partitioned by a plate 5, and a cylindrical combustion tower 6 is vertically installed through the silo 2 from the lower chamber 4, and a lower chamber 4 is successively formed in which polymeric waste is externally carbonized using radiant heat from a residual ash chamber, etc. The combustion tower 6 has an inlet hole 7 for miscellaneous waste carbonization gas at a position corresponding to the silo 2, an inlet hole 8 for secondary combustion air at a position corresponding to the residual ash chamber 3, and an inlet hole 8 for secondary combustion air at a position corresponding to the ash chamber 3. A small garbage incinerator characterized in that introduction holes 9 for polymer carbonization gas are provided at positions corresponding to the respective positions. 2. The small-sized garbage incinerator according to claim 1, wherein the silo 2 has a larger volume than the residual ash chamber 3 and the lower chamber 4. 3. The small-sized garbage incinerator according to claim 1, wherein the main body 1 has a water wall 13 on the outer periphery. 4. The small-sized garbage incinerator according to claim 1, wherein the main body 1 includes a roller member 12 at the lower part.
JP21381683A 1983-11-14 1983-11-14 Small-sized dust incinerator Granted JPS60105815A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP21381683A JPS60105815A (en) 1983-11-14 1983-11-14 Small-sized dust incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP21381683A JPS60105815A (en) 1983-11-14 1983-11-14 Small-sized dust incinerator

Publications (2)

Publication Number Publication Date
JPS60105815A JPS60105815A (en) 1985-06-11
JPH0325691B2 true JPH0325691B2 (en) 1991-04-08

Family

ID=16645501

Family Applications (1)

Application Number Title Priority Date Filing Date
JP21381683A Granted JPS60105815A (en) 1983-11-14 1983-11-14 Small-sized dust incinerator

Country Status (1)

Country Link
JP (1) JPS60105815A (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2728366B2 (en) * 1994-07-29 1998-03-18 栄一郎 佐藤 Combustion equipment for polymer materials
FR2886377B1 (en) * 2005-05-31 2007-11-23 Jean Guillot COMBUSTION DEVICE WITH PREHEATING OF THE COMBUSTION AIR BY THE POSTCOMBUSTION GAS THEY ARE OVERHEATED BY THEIR PASSAGE AT THE HEART OF THE COMBUSTION
GB0604907D0 (en) 2006-03-10 2006-04-19 Morgan Everett Ltd Pyrolysis apparatus and method
JP4755158B2 (en) * 2007-09-27 2011-08-24 株式会社ステラ環境科学 Solid biomass waste plastic small incinerator to suppress dioxin formation
CN106338071A (en) * 2015-07-14 2017-01-18 广西龙昌环保科技有限公司 Environment-friendly garbage incinerator

Also Published As

Publication number Publication date
JPS60105815A (en) 1985-06-11

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