JPH03236508A - Waste incinerator - Google Patents

Waste incinerator

Info

Publication number
JPH03236508A
JPH03236508A JP3125590A JP3125590A JPH03236508A JP H03236508 A JPH03236508 A JP H03236508A JP 3125590 A JP3125590 A JP 3125590A JP 3125590 A JP3125590 A JP 3125590A JP H03236508 A JPH03236508 A JP H03236508A
Authority
JP
Japan
Prior art keywords
combustion chamber
primary combustion
secondary combustion
primary
exhaust gas
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP3125590A
Other languages
Japanese (ja)
Inventor
Shigeki Tomobe
友部 茂樹
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.)
KOYO ENG KK
Original Assignee
KOYO ENG KK
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 KOYO ENG KK filed Critical KOYO ENG KK
Priority to JP3125590A priority Critical patent/JPH03236508A/en
Publication of JPH03236508A publication Critical patent/JPH03236508A/en
Pending legal-status Critical Current

Links

Landscapes

  • Incineration Of Waste (AREA)

Abstract

PURPOSE:To burn combustible matters completely and make the exhaust gas smokeless and odorless by constituting the inside of the main body of a primary combustion chamber in which wastes are charged for primary combustion and a secondary combustion chamber into which the generated exhaust gas is sent. CONSTITUTION:In order to incinerate wastes, they are charged into a primary combustion chamber 3 and a primary combustion burner 15 which is positioned in the primary combustion chamber 3 is ignited. The high temperature exhaust gas that is generated from the primary combustion chamber 3 is not sent directly to a stack 6 but stays in the furnace for a long time and sent to a secondary combustion chamber 4 to be completely burned. And in the secondary combustion chamber 4 the exhaust gas is heated by the flame from a secondary combustion burner 16 to further higher temperature. On the other hand in the main body 1 of the incinerator the primary combustion chamber 3 and secondary combustion chamber 4 are both constituted with a heat resistance caster 7 of a large heat accumulation effect and the combustion air is heated through air pipes 18 which are buried in the caster 7 and the heated air is blown out into the primary combustion chamber 3 and secondary combustion chamber 4, and the primary combustion chamber 3 and secondary combustion chamber 4 both have a very good combustion efficiency.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は廃棄物焼却炉に係り、さらに詳細には、排ガス
を無煙、無臭とし、しかも焼却灰中の有害物質をも微量
とすることのできる廃棄物焼却炉に関する。
[Detailed Description of the Invention] [Field of Industrial Application] The present invention relates to a waste incinerator, and more particularly, to a waste incinerator that makes exhaust gas smokeless and odorless, and also reduces the amount of harmful substances in the incinerated ash. Regarding waste incinerators that can be used.

〔従来の技術〕[Conventional technology]

近年、化学技術の発達にともない、ゴムやプラスチック
を用いた製品が数多く市場に出廻っているが、廃棄物と
称されるもののなかにも、これらゴムやプラスチックの
類が混入される機台が多い。
In recent years, with the development of chemical technology, many products using rubber and plastics have appeared on the market, but there are machines that mix these rubbers and plastics into what is called waste. many.

また、医療廃棄物の処理分野においては、使用済みの紙
おむつや注射針9点滴ビン等を焼却処理することがおこ
なわれており、血液が付着し肝炎等に感染する恐れのあ
る医療廃棄物の焼却処理は非常に重要である。
In addition, in the field of medical waste disposal, used disposable diapers, hypodermic needles, 9 drip bottles, etc. are incinerated. Processing is very important.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

しかして、前記したごとき廃棄物のうち、ゴムやプラス
チックの類を従来一般の廃棄物焼却炉、すなわち焼却炉
本体内に廃棄物を投入して燃焼させ、炉内で発生した排
ガスを煙突から大気中に放出させるだけという、炉内設
計の単純な焼却炉で焼却すると、排ガス中に多量の煤煙
や有毒ガスが含まれ、公害防止上好ましくない。すなわ
ち、従来実用に供されている廃棄物焼却炉は、一般に、
排ガスの炉内における滞留時間が短いため、燃焼物質が
不完全燃焼の状態で排ガスとともに炉外に放出される難
点がある。
Among the above-mentioned wastes, rubber and plastics are burned in conventional general waste incinerators, in other words, the waste is put into the incinerator itself, and the exhaust gas generated in the incinerator is released from the chimney into the atmosphere. If incineration is done in an incinerator with a simple internal design that only releases waste into the atmosphere, the exhaust gas will contain a large amount of soot and toxic gases, which is undesirable in terms of pollution prevention. In other words, waste incinerators that have been put into practical use are generally
Since the residence time of the exhaust gas inside the furnace is short, there is a drawback that the combustion material is discharged outside the furnace together with the exhaust gas in a state of incomplete combustion.

また、医療廃棄物の処理分野においては、既述のごとく
、使用済みの紙おむつや注射針9点滴ビン等を焼却処理
することがおこなわれているが、従来、これら医療廃棄
物処理分野で使用されている焼却炉も燃焼が不十分であ
り、悪臭が出る等の声があった。
In addition, in the medical waste treatment field, as mentioned above, used disposable diapers, hypodermic needles, and drip bottles are incinerated; There were also complaints that the incinerators used were not producing enough combustion and emitted a foul odor.

本発明の目的は、一般の塵芥廃棄物は勿論のこと、使用
済みのゴムやプラスチック、さらには紙おむつ、注射針
2点滴ビン等の医療廃棄物、その他一般に燃えにくいと
されている産業廃棄物を焼却処理する場合であっても、
燃焼物質を完全燃焼させて排ガスを無煙、無臭とし、し
かも焼却灰中の有害物質をも微量とすることのできる廃
棄物焼却炉を提供ることにある。
The purpose of the present invention is to collect not only general garbage waste, but also used rubber and plastic, medical waste such as paper diapers, syringe needles and drip bottles, and other industrial waste that is generally considered to be difficult to burn. Even when incinerated,
To provide a waste incinerator capable of completely burning combustion materials to make exhaust gas smokeless and odorless, and furthermore, reducing the amount of harmful substances in incineration ash to a trace amount.

〔課題を解決するための手段〕[Means to solve the problem]

前記目的は、焼却炉本体内に投入された廃棄物を燃焼さ
せ、炉内で発生した排ガスを煙突から大気中に放出する
構造の廃棄物焼却炉において、前記焼却炉本体内を、廃
棄物を投入して1次燃焼させる1次燃焼室と、1次燃焼
室内で発生した排ガスを送り込む2次燃焼室とで構成し
、かつ前記1次燃焼室と2次燃焼室とを耐熱キャスタで
構成するとともに、1次燃焼室内に臨む1次燃焼バーナ
以外に、2次燃焼室内にも2次燃焼バーナを臨設せしめ
、さらに前記1次燃焼室と2次燃焼室とを構成する耐熱
キャスタ内に、ブロワからの燃焼用空気を1次燃焼室お
よび2次燃焼室内に送り込む空気路を形成することによ
って遠戚される。
The purpose is to burn the waste put into the incinerator body and to release the waste gas generated in the incinerator into the atmosphere from the chimney. It is composed of a primary combustion chamber that is fed into the combustion chamber for primary combustion, and a secondary combustion chamber that sends the exhaust gas generated in the primary combustion chamber, and the primary combustion chamber and the secondary combustion chamber are constructed of heat-resistant casters. At the same time, in addition to the primary combustion burner facing into the primary combustion chamber, a secondary combustion burner is also installed in the secondary combustion chamber, and a blower is installed in the heat-resistant casters that constitute the primary combustion chamber and the secondary combustion chamber. This is done by forming an air passage that sends combustion air from the combustion chamber into the primary combustion chamber and the secondary combustion chamber.

〔作用〕[Effect]

以上の構成において、廃棄物を焼却処理するには、前記
廃棄物を1次燃焼室内に投入し、1次燃焼室内に臨む1
次燃焼バーナに着火する。
In the above configuration, in order to incinerate the waste, the waste is put into the primary combustion chamber, and the
The next combustion burner is ignited.

そして、前記のようにして発生した1次燃焼室からの高
温排ガスは、短時間のうちに直接煙突に送られることな
く、炉内に長時間滞留して完全燃焼されるべく、2次燃
焼室内に送られ、この2次燃焼室内において、2次燃焼
バーナからの火焔によってさらに高温に加熱される。一
方、焼却炉本体は、前記1次燃焼室および2次燃焼室共
、蓄熱効果の大きな耐熱キャスタにより構成されており
、この蓄熱効果の大きな耐熱キャスタ内に形成されてい
る空気路を介しブロワからの燃焼用空気が加熱されて1
次燃焼室および2次燃焼室内に噴き出すため、1次燃焼
室内および2次燃焼室内共、その燃焼効率は非常に良好
であり、前記各効果が相剰的に作用する本発明焼却炉を
試作して紙おむつを焼却処理した場合の焼却灰溶出試験
結果および、煙突から大気中に放出れる気流の分析結果
はそれぞれ後記する表(および2のとおり良好であった
The high-temperature exhaust gas from the primary combustion chamber generated as described above is not sent directly to the chimney in a short time, but stays in the furnace for a long time and is completely combusted in the secondary combustion chamber. In this secondary combustion chamber, it is further heated to a high temperature by the flame from the secondary combustion burner. On the other hand, in the incinerator main body, both the primary combustion chamber and the secondary combustion chamber are constructed of heat-resistant casters that have a large heat storage effect, and the blower is connected to the incinerator through an air path formed in the heat-resistant casters that have a large heat storage effect. of combustion air is heated to 1
Since the air is ejected into the secondary combustion chamber and the primary combustion chamber, the combustion efficiency in both the primary combustion chamber and the secondary combustion chamber is very good.The incinerator of the present invention, in which the above-mentioned effects act mutually, was manufactured as a prototype. The results of the incineration ash elution test when the paper diapers were incinerated and the analysis results of the airflow released into the atmosphere from the chimney were good as shown in the tables (and 2) below.

〔実施例〕〔Example〕

以下5本発明を、図面の一実施例にもとづいて説明する
と、第1図は本発明焼却炉の炉内構造を示す一部縦断正
面図、第2図は第1図に符号6で示す煙突の全体構成を
示す一部切欠正面図、第3図は第1図のA−A断面図、
第4図は第3図のB−B断面図である。
The present invention will be explained below based on one embodiment of the drawings. Fig. 1 is a partially longitudinal front view showing the internal structure of the incinerator of the present invention, and Fig. 2 is a chimney shown by the reference numeral 6 in Fig. 1. FIG. 3 is a partially cutaway front view showing the overall configuration of FIG. 1, and FIG.
FIG. 4 is a sectional view taken along line BB in FIG. 3.

本発明焼却炉の炉内構造を示す第1図、第3図および第
4図において、1は焼却炉本体、2は焼却炉本体lのベ
ース、3は廃棄物を投入して1次燃焼させる1次燃焼室
、4は1次燃焼室3内で発生した排ガスを送り込む2次
燃焼室、5は2次燃焼室4に続く煙道、6は煙道5の上
部に延設された煙突を示し、1次燃焼室3と2次燃焼室
4とは、蓄熱効果の大きな耐熱キャスタ7によって構成
されている。8は鋼板製の焼却炉本体ケーシングである
In Figs. 1, 3, and 4 showing the internal structure of the incinerator of the present invention, 1 is the incinerator main body, 2 is the base of the incinerator main body l, and 3 is the waste that is charged for primary combustion. A primary combustion chamber, 4 is a secondary combustion chamber into which the exhaust gas generated in the primary combustion chamber 3 is sent, 5 is a flue that continues to the secondary combustion chamber 4, and 6 is a chimney extending above the flue 5. The primary combustion chamber 3 and the secondary combustion chamber 4 are constructed of heat-resistant casters 7 that have a large heat storage effect. 8 is an incinerator main body casing made of steel plate.

9は1次燃焼室3内に設置されたロスドル、10は同じ
く1次燃焼室3内に設けられた廃棄物投入口、1工はロ
スドル9の上方に位置して1次燃焼室3の側壁に設けた
焼却灰取出口、12はロスドル9の下方に位置して1次
燃焼室3の側壁に設けた焼却灰取出口、13は2次燃焼
室4の下方寄り側壁に設けた焼却灰取出口、14は煙道
5の下方寄り側壁に設けた焼却灰取出口で、煙突6の途
中には、排気流量調整用のダンパ(図示せず)が設けら
れている。
Reference numeral 9 denotes a rosdol installed in the primary combustion chamber 3, 10 a waste inlet also provided in the primary combustion chamber 3, and 1 a side wall of the primary combustion chamber 3 located above the rosdol 9. 12 is an incinerated ash outlet located below the rosdol 9 and provided on the side wall of the primary combustion chamber 3; 13 is an incinerated ash outlet provided on the lower side wall of the secondary combustion chamber 4. The outlet 14 is an incinerated ash outlet provided on the lower side wall of the flue 5, and a damper (not shown) for adjusting the exhaust flow rate is provided in the middle of the chimney 6.

15は1次燃焼室3内に臨む1次燃焼バーナを示し、本
発明においては、1次燃焼室3内に臨む前記1次燃焼バ
ーナ15以外に、2次燃焼室4内にも2次燃焼バーナ1
6が臨設されている。
Reference numeral 15 indicates a primary combustion burner facing into the primary combustion chamber 3. In the present invention, in addition to the primary combustion burner 15 facing into the primary combustion chamber 3, there is also a secondary combustion burner inside the secondary combustion chamber 4. Burner 1
6 has been temporarily installed.

17は1次燃焼室3および2次燃焼室4内に燃焼用空気
を送り込むブロワで、ブロワ17からの燃焼用空気は、
耐熱用キャスタ7内に埋設された空気管18を介して前
記1次燃焼室3および2次燃焼室4内に送り込まれるも
ので、図示実施例に示すように、ブロワ17を1次燃焼
室3および2次燃焼室4に共用とすることにより、1次
燃焼室3および2次燃焼室4用として個々にブロワを設
置する場合に比べて設備費の低減化をはかることができ
る。
17 is a blower that sends combustion air into the primary combustion chamber 3 and the secondary combustion chamber 4, and the combustion air from the blower 17 is
The air is fed into the primary combustion chamber 3 and the secondary combustion chamber 4 through an air pipe 18 embedded in the heat-resistant caster 7, and as shown in the illustrated embodiment, the blower 17 is connected to the primary combustion chamber 3. By sharing the blower with the secondary combustion chamber 4, equipment costs can be reduced compared to the case where blowers are installed individually for the primary combustion chamber 3 and the secondary combustion chamber 4.

煙突6の全体構成を示す第2図において、当該煙突6の
上端開口部に対向してその上方、および煙突上端寄りの
外周は、ハウジング部材工9によって包囲されている。
In FIG. 2 showing the overall structure of the chimney 6, the upper part of the chimney 6 opposite to and above the opening, and the outer periphery near the upper end of the chimney 6 are surrounded by a housing member 9.

また、前記ハウジング部材工9の底部を閉塞するハウジ
ング底壁19aは傾斜しており、その傾斜下底に灰出管
2oが接続されている。さらに、ハウジング部材19の
側壁19bには、排気口21が設けられており、この排
気口21にメツシュ部材22が張設されている。一方、
前記ハウジング部材19の傾斜底壁19aの上方に位置
して、当該ハウジング部材19の側壁19b内に給水管
23が臨設されている。24はハウジング側壁19bに
形成した前記排気口21の外周に間隔を存して付設され
たカバ一部材を示している。
Further, the housing bottom wall 19a that closes the bottom of the housing member 9 is inclined, and the ash extraction pipe 2o is connected to the inclined lower bottom thereof. Further, an exhaust port 21 is provided in the side wall 19b of the housing member 19, and a mesh member 22 is stretched over the exhaust port 21. on the other hand,
A water supply pipe 23 is provided within the side wall 19b of the housing member 19, located above the inclined bottom wall 19a of the housing member 19. Reference numeral 24 indicates a cover member attached at a distance from the outer periphery of the exhaust port 21 formed in the housing side wall 19b.

以上の構成において、廃棄物を焼却処理するには、前記
廃棄物を1次燃焼室3内に投入し、1次燃焼室3内に臨
む1次燃焼バーナ15に着火する。
In the above configuration, in order to incinerate the waste, the waste is put into the primary combustion chamber 3 and the primary combustion burner 15 facing the inside of the primary combustion chamber 3 is ignited.

そして、前記のようにして発生した1次燃焼室3からの
高温排ガスは、短時間のうちに直接煙突6に送られるこ
となく、炉内に長時間滞留して完全燃焼されるべく、2
次燃焼室4内に送られ、この2次燃焼室4内において、
2次燃焼バーナ16からの火焔によってさらに高温に加
熱される。
The high-temperature exhaust gas from the primary combustion chamber 3 generated as described above is not directly sent to the chimney 6 in a short period of time, but remains in the furnace for a long time and is completely combusted.
It is sent into the secondary combustion chamber 4, and within this secondary combustion chamber 4,
The flame from the secondary combustion burner 16 further heats it to a high temperature.

方、焼却炉本体1は、前記1次燃焼室3および2次燃焼
室4共、蓄熱効果の大きな耐熱キャスタ7により構成さ
れており、この蓄熱効果の大きな耐熱キャスタ7内に埋
設されている空気管18を介しブロワ17からの燃焼用
空気が加熱されて1次燃焼室3の周壁から旋回流となっ
て噴き出し、また2次燃焼室4内にも加熱された燃焼用
空気が噴き出すため、1次燃焼室3内および2次燃焼室
4内共、その燃焼効率は非常に良好であり、前記各効果
が相剰的に作用する焼却炉を試作して紙おむつ焼却処理
した場合の焼却灰溶出試験結果および、煙突6から大気
中に放出される気流の分析結果は、それぞれ下記する表
1および2のとおり良好であった。
On the other hand, in the incinerator main body 1, both the primary combustion chamber 3 and the secondary combustion chamber 4 are constructed of heat-resistant casters 7 that have a large heat storage effect, and the air buried in the heat-resistant casters 7 that have a large heat storage effect Combustion air from the blower 17 is heated through the pipe 18 and blows out from the peripheral wall of the primary combustion chamber 3 in the form of a swirling flow, and the heated combustion air also blows into the secondary combustion chamber 4. The combustion efficiency in both the secondary combustion chamber 3 and the secondary combustion chamber 4 is very good, and an incineration ash elution test was performed when a paper diaper incineration process was carried out using a prototype incinerator in which each of the above-mentioned effects acts mutually. The results and the analysis results of the airflow released into the atmosphere from the chimney 6 were good as shown in Tables 1 and 2 below, respectively.

表  1 表  2 また、前記実施例において、煙突6内を上昇してきた排
ガスは、単純に雨よけを設けた程度の煙突上端開口部か
ら大気中に放出されることなく、第2図に示すように、
煙突6の上端開口部に対向してその上方、および煙突上
端寄りの外周を包囲しているハウジング部材19の天板
19cに衝突し、流れ方向を変えて、ハウジング側壁1
9bに設けた排気口21からメツシュ部材22を通過し
て大気中に放出される。
Table 1 Table 2 In addition, in the above embodiment, the exhaust gas rising inside the chimney 6 is not released into the atmosphere through the opening at the top of the chimney, which is simply provided with a rain screen, but instead is released into the atmosphere as shown in Fig. 2. ,
It collides with the top plate 19c of the housing member 19 that faces and surrounds the upper opening of the chimney 6 and the outer periphery near the upper end of the chimney, changing the flow direction and causing the housing side wall 1
It passes through the mesh member 22 from the exhaust port 21 provided at 9b and is discharged into the atmosphere.

一方、前記ハウジング天板19cに衝突した比較的大き
な浮遊塵、たとえば紙片が燃えてすす状となった黒色の
軽い浮遊塵は、最終的には、ハウジング部材19の底部
を閉塞する傾斜状のハウジング底壁19a上に落下し、
ハウジング側壁19b内に臨設された給水管23、さら
に詳しくは、傾斜状ハウジング底壁19aの上方に位置
して、ハウジング側壁19b内に臨設された給水管23
から適宜給水される水によって、ハウジング底壁19a
の傾斜下底に接続されている販出管20側に強制的に送
り込まれるものであって、販出管20の出口部から取り
出された前記浮遊塵の集りは、地上部において適宜処理
すればよく、このように、本実施例によれば、焼却炉本
体1内で焼却処理した排ガス中の浮遊塵を大気中に放出
して周囲環境を汚すことなく、しかもハウジング部材1
9内に捕集された前記浮遊塵は、当該ハウジング部材1
9内に臨む給水管23からの水によって、販出管20を
経て強制的に地上部に送られるため、前記ハウジング部
材19内を定期的にメンテナンスする煩雑さもない。
On the other hand, relatively large floating dust that collides with the housing top plate 19c, for example, light black floating dust that has become soot-like after burning paper pieces, will eventually form an inclined housing that closes the bottom of the housing member 19. Falling onto the bottom wall 19a,
A water supply pipe 23 installed inside the housing side wall 19b, more specifically, a water supply pipe 23 installed inside the housing side wall 19b above the inclined housing bottom wall 19a.
The housing bottom wall 19a is
The floating dust collected from the outlet of the outlet pipe 20 can be disposed of appropriately in the above ground area. As described above, according to the present embodiment, floating dust in the exhaust gas incinerated in the incinerator body 1 is not released into the atmosphere and pollutes the surrounding environment, and the housing member 1
The floating dust collected in the housing member 1
Since the water from the water supply pipe 23 facing inside the housing member 9 is forcibly sent to the above ground area via the sales pipe 20, there is no need for regular maintenance of the inside of the housing member 19.

なお、図示実施例に示すように、ハウジング側壁19b
に形成した排気口21の外周に間隔を存してカバ一部材
24を付設するようにすれば、排気口21からハウジン
グ部材19外に放出された排ガス流は、前記カバ一部材
24に衝突した後周囲に分散して当該カバ一部材24の
上・下端から大気中に放出されるものであって、このと
き、排気口21からの排ガス流がカバ一部材24に衝突
したときの衝撃による戻り風圧は、排気口21に張設さ
れているメツシュ部材22にも影響して、当該メツシュ
部材22に付着している粉塵を強制的に落下させるよう
に作用し、メツシュ部材22の目詰りを効果的に防止す
ることができる。
Note that, as shown in the illustrated embodiment, the housing side wall 19b
If the cover member 24 is attached to the outer periphery of the exhaust port 21 formed at a distance, the exhaust gas flow released from the exhaust port 21 to the outside of the housing member 19 collides with the cover member 24. It is dispersed around the rear and released into the atmosphere from the upper and lower ends of the cover member 24, and at this time, the exhaust gas flow from the exhaust port 21 collides with the cover member 24 and returns due to the impact. The wind pressure also affects the mesh member 22 stretched over the exhaust port 21 and acts to forcibly drop dust adhering to the mesh member 22, thereby effectively preventing clogging of the mesh member 22. can be prevented.

〔発明の効果〕〔Effect of the invention〕

本発明は以上のごときであり、図示実施例の説明からも
明らかなように、本発明によれば、一般の塵芥廃棄物は
勿論のこと、使用済みのゴムやプラスチック、さらには
紙おむつ、注射針9点滴ビン等の医療廃棄物、その他一
般に燃えにくいとされている産業廃棄物を焼却処理する
場合であっても、燃焼物質を完全燃焼させて排ガスを無
煙、無臭とし、しかも焼却灰中の有害物質をも微量とす
ることのできる廃棄物焼却炉を提供することができる。
The present invention is as described above, and as is clear from the explanation of the illustrated embodiments, according to the present invention, not only general garbage waste but also used rubber and plastic, disposable diapers, syringe needles, etc. 9 Even when incinerating medical waste such as drip bottles and other industrial waste that is generally considered to be difficult to burn, the combustion materials are completely combusted, the exhaust gas is smokeless and odorless, and no harmful substances are contained in the incinerated ash. It is possible to provide a waste incinerator that can reduce even trace amounts of substances.

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

図面は本発明の一実施例を示し、第1図は本発明焼却炉
の炉内構造を示す一部縦断正面図、第2図は第1図に符
号6で示す煙突の全体構成を示す一部切欠正面図、第3
図は第1図のA−A断面図、第4図は第3図のB−B断
面図である。
The drawings show one embodiment of the present invention; FIG. 1 is a partially longitudinal front view showing the internal structure of the incinerator of the present invention, and FIG. Part cutaway front view, 3rd
The figure is a sectional view taken along the line AA in FIG. 1, and FIG. 4 is a sectional view taken along the line BB in FIG. 3.

Claims (1)

【特許請求の範囲】 1、焼却炉本体内に投入された廃棄物を燃焼させ、炉内
で発生した排ガスを煙突から大気中に放出する構造の廃
棄物焼却炉において、 前記焼却炉本体内を、廃棄物を投入して1次燃焼させる
1次燃焼室と、1次燃焼室内で発生した排ガスを送り込
む2次燃焼室とで構成し、かつ前記1次燃焼室と2次燃
焼室とを耐熱キャスタで構成するとともに、1次燃焼室
内に臨む1次燃焼バーナ以外に、2次燃焼室内にも2次
燃焼バーナを臨設せしめ、さらに前記1次燃焼室と2次
燃焼室とを構成する耐熱キャスタ内に、ブロワからの燃
焼用空気を1次燃焼室および2次燃焼室内に送り込む空
気路を形成したことを特徴とする廃棄物焼却炉。
[Scope of Claims] 1. In a waste incinerator having a structure in which waste put into the incinerator body is burned and exhaust gas generated in the incinerator is released into the atmosphere from a chimney, inside the incinerator body: , consists of a primary combustion chamber in which waste is input and undergoes primary combustion, and a secondary combustion chamber into which exhaust gas generated within the primary combustion chamber is sent, and the primary combustion chamber and the secondary combustion chamber are heat-resistant. In addition to the primary combustion burner facing into the primary combustion chamber, the heat-resistant casters are constructed of casters and have a secondary combustion burner installed in the secondary combustion chamber, and further constitute the primary combustion chamber and the secondary combustion chamber. A waste incinerator characterized in that an air passage is formed in the interior for sending combustion air from a blower into a primary combustion chamber and a secondary combustion chamber.
JP3125590A 1990-02-10 1990-02-10 Waste incinerator Pending JPH03236508A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3125590A JPH03236508A (en) 1990-02-10 1990-02-10 Waste incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3125590A JPH03236508A (en) 1990-02-10 1990-02-10 Waste incinerator

Publications (1)

Publication Number Publication Date
JPH03236508A true JPH03236508A (en) 1991-10-22

Family

ID=12326249

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3125590A Pending JPH03236508A (en) 1990-02-10 1990-02-10 Waste incinerator

Country Status (1)

Country Link
JP (1) JPH03236508A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05332522A (en) * 1992-05-29 1993-12-14 Toshimitsu Ukai Method of igniting waste food containing salt

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05332522A (en) * 1992-05-29 1993-12-14 Toshimitsu Ukai Method of igniting waste food containing salt

Similar Documents

Publication Publication Date Title
US6324999B1 (en) Incinerator for removing noxious substances
KR101928762B1 (en) Hit cyclone combustor
KR101916128B1 (en) Hit cyclone combustor
JPH03236508A (en) Waste incinerator
CN2512994Y (en) Interlinked comprehensive garbage incinerator
KR200371234Y1 (en) The spread of a fire device again waste gas a trash boiler
JP2952160B2 (en) Waste incineration method, grate, incinerator and incinerator
KR200352792Y1 (en) A trash boiler waste gas purifier
KR100249104B1 (en) Method and apparatus for burning out industrial wastes
CN100491830C (en) Self-heat-supply energy-saving environmental protection incinerator
JPH03125808A (en) Fluidized-bed type refuse incinerator
JPH0531386Y2 (en)
TWM631143U (en) Refuse incinerating equipment
KR101967117B1 (en) Waste Incineration System with Cyclone Combustion Structure
JPH1163440A (en) Waste incinerator
JPH07332632A (en) Combustible dust incinerating device
JP3579774B2 (en) Burner heating type polymer incinerator
KR200249665Y1 (en) The trash burner
JPS5741515A (en) Incinerator
JP3100572B2 (en) Incinerator
KR0136768Y1 (en) Trash burner
KR100245118B1 (en) Burner recombustion apparatus
JPH0587313A (en) Incinerator
KR0165921B1 (en) Spontaneous ventilation type trash burner
JP2782599B2 (en) Incineration method and incinerator for wet incineration