JPH08178237A - Combustion method for waste incinerator - Google Patents

Combustion method for waste incinerator

Info

Publication number
JPH08178237A
JPH08178237A JP31477394A JP31477394A JPH08178237A JP H08178237 A JPH08178237 A JP H08178237A JP 31477394 A JP31477394 A JP 31477394A JP 31477394 A JP31477394 A JP 31477394A JP H08178237 A JPH08178237 A JP H08178237A
Authority
JP
Japan
Prior art keywords
combustion
chamber
burner
gasified
waste
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
JP31477394A
Other languages
Japanese (ja)
Inventor
Ichiro Nakamachi
一郎 仲町
Yukio Tomita
由起夫 富田
Masamichi Yamamoto
雅通 山本
Hiroshi Kosuge
浩 小菅
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.)
HIRAKAWA GUIDOM KK
Tokyo Gas Co Ltd
Original Assignee
HIRAKAWA GUIDOM KK
Tokyo Gas Co Ltd
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 HIRAKAWA GUIDOM KK, Tokyo Gas Co Ltd filed Critical HIRAKAWA GUIDOM KK
Priority to JP31477394A priority Critical patent/JPH08178237A/en
Publication of JPH08178237A publication Critical patent/JPH08178237A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE: To perform control of a gasifying speed by means of a combustion amount of a burner by a method wherein combustion by a burner is effected so that oxygen concentration in a combustion product in a gasifying chamber is adjusted to a specified value to effect an endothermic gasifying reaction of waste in the gasifying chamber, and gasified combustible gas is introduced to a secondary combustion chamber having a specified temperature and combustion is completed. CONSTITUTION: In a gasifying chamber 1, combustion of a primary burner 2 is controlled so that oxygen concentration in a combustion product due to combustion by a primary burner 2 is reduced to 15% or less. Waste 8 is gasified by heat generated by the primary burner 2, gasified combustion gas is introduced to a wide secondary combustion chamber 3 of 800 deg.C or higher through a communication part 4, and a sufficient combustion aid is fed to complete combustion. Secondary air for combustion is introduced as combustion aid in a secondary combustion chamber 3 through an air injection part 5 as it is or completion combustion may be effected by O2 in combustion gas in such a way that high surplus air combustion through which oxygen concentration in a combustion product is at least 18% in a secondary burner 6 is executed.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は廃棄物焼却炉の燃焼方法
に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a combustion method for a waste incinerator.

【0002】[0002]

【従来の技術】[Prior art]

【0003】従来の焼却炉の燃焼方法には次の二つの方
法がある。図1に示す炉は、最も一般的な燃焼方法を
用いるもので、廃棄物の燃焼に必要な全空気を底部から
供給して燃焼させる方法である。図2及び図3で示す
炉は、乾留燃焼、ガス化燃焼、段階燃焼等と呼ばれる燃
焼法を使用するものであり、着火バーナで廃棄物に着火
後、理論空気量以下の空気を供給して部分燃焼させ、そ
の発生熱で可燃分をガス化し、ガス化した可燃分に二次
空気を混入して二次燃焼室で完全燃焼させる。
There are the following two combustion methods in the conventional incinerator. The furnace shown in FIG. 1 uses the most general combustion method, and is a method in which all the air required for combustion of waste is supplied from the bottom and burned. The furnace shown in FIGS. 2 and 3 uses a combustion method called dry distillation combustion, gasification combustion, stepwise combustion, etc. After igniting the waste with an ignition burner, air below the theoretical air amount is supplied. Partial combustion is performed, the combustible components are gasified by the generated heat, secondary air is mixed with the gasified combustible components, and complete combustion is performed in the secondary combustion chamber.

【0004】[0004]

【発明が解決しようとする課題】 図1で示す焼却炉で採用する燃焼法は、種々の廃棄物
がガス化室に投入されると、例えば、プラスチック、廃
油などの高発熱量のものが投入されると、急激な燃焼が
起り、ガス化室が極めて高温になり、炉本体を傷めるだ
けでなく、大量の黒煙を発生する。また、例えば、低発
熱量のものが投入されると、自己の発生熱だけでは燃焼
が維持できなくなったり、紙おむつ等の断熱層からなる
ものが投入されると、未燃部分への伝熱が不充分となっ
たりして燃え残りが発生したりする課題がある。図2
及び図3で示す炉の燃焼方法に於いても、の場合と同
様の問題が発生する。即ち、廃棄物自体の部分燃焼によ
り発生した熱でガス化を行うため、廃油とかプラスチッ
クのように燃焼しやすい高発熱物質が投入されると、急
激な部分燃焼により、大量の可燃ガスが発生し、二次燃
焼室では燃焼しきれずに、黒煙を発生する。また、低発
熱量物質が投入された場合には、自己の部分燃焼熱では
ガス化のための充分な熱が得られず、いわゆる燃え残り
が出てしまう課題がある。総じて、前記した従来技術
等々は、燃焼の状態およびガス化速度が廃棄物自体の反
応のしやすさに大きく影響され、その結果種々の問題が
生じてしまう課題がある。
The combustion method adopted in the incinerator shown in FIG. 1 is such that when various wastes are put into the gasification chamber, for example, plastics, waste oil, etc. having a high heating value are put in. Then, a rapid combustion occurs, the gasification chamber becomes extremely hot, which not only damages the furnace body but also produces a large amount of black smoke. Also, for example, if a low calorific value is input, combustion cannot be maintained only by the heat generated by itself, or if a heat insulating layer such as a paper diaper is input, heat transfer to the unburned part There is a problem that it becomes insufficient and unburned residue occurs. Figure 2
Also, in the combustion method of the furnace shown in FIG. 3, the same problem as in the case of occurs. That is, since the heat generated by partial combustion of the waste itself is used for gasification, when a highly exothermic substance such as waste oil or plastic that is easy to burn is added, a large amount of combustible gas is generated due to rapid partial combustion. However, in the secondary combustion chamber, black smoke is generated because the combustion cannot be completed. Further, when a low calorific value substance is added, sufficient heat for gasification cannot be obtained by its own partial combustion heat, and there is a problem that so-called unburned residue is generated. In general, the above-mentioned conventional techniques and the like have a problem that the state of combustion and the gasification rate are greatly influenced by the easiness of reaction of the waste itself, resulting in various problems.

【0005】[0005]

【課題を解決するための手段】前記課題を解決するため
に、本発明は、ガス化室において燃焼生成物中の酸素濃
度が15%以下となるように、バーナを燃焼させなが
ら、前記ガス化室中の廃棄物を吸熱ガス化反応させ、ガ
ス化された可燃ガスは800℃以上の二次燃焼室に導き
燃焼を完結させることを特徴とする廃棄物焼却炉の燃焼
方法を提供するものである。
In order to solve the above-mentioned problems, the present invention relates to the gasification while burning the burner so that the oxygen concentration in the combustion products is 15% or less in the gasification chamber. An endothermic gasification reaction of waste in a room is conducted, and the gasified combustible gas is guided to a secondary combustion chamber at 800 ° C or higher to complete combustion, thereby providing a combustion method for a waste incinerator. is there.

【0006】また、本発明は、前記課題を解決するため
に、二次燃焼室において燃焼生成物中の酸素濃度が18
%以上となるような高過剰空気燃焼を二次バーナにより
実行させて、その燃焼ガス中のO2 でガス化された可燃
ガスを燃焼させることを特徴とする廃棄物焼却炉の燃焼
方法を提供するものである。
Further, according to the present invention, in order to solve the above-mentioned problems, the oxygen concentration in the combustion products in the secondary combustion chamber is 18
% Excess of excess air is performed by a secondary burner to burn combustible gas gasified with O 2 in the combustion gas, and a combustion method for a waste incinerator is provided. To do.

【0007】また、本発明は、前記課題を解決するため
に、二次燃焼室に空気のみを導入して、ガス化された可
燃ガスを燃焼させることを特徴とする廃棄物焼却炉の燃
焼方法を提供するものである。
In order to solve the above-mentioned problems, the present invention also introduces only air into the secondary combustion chamber to burn the gasified combustible gas and burns the waste incinerator. Is provided.

【0008】また、本発明は、前記課題を解決するため
に、二次燃焼室において、ガス化された可燃ガスを2秒
以上滞留させて燃焼させることを特徴とする廃棄物焼却
炉の燃焼方法を提供するものである。
Further, in order to solve the above-mentioned problems, the present invention is characterized in that a gasified combustible gas is retained for 2 seconds or more and burned in a secondary combustion chamber, and burned. Is provided.

【0009】[0009]

【作用】ガス化室において、燃焼生成物中の酸素濃度が
15%以下となるようにバーナを燃焼させながら廃棄物
の吸熱ガス化反応を実行し、ガス化された可燃ガスは、
800℃以上の二次燃焼室に導いて2秒以上滞留させつ
つ燃焼を完結させる。
In the gasification chamber, the endothermic gasification reaction of the waste is carried out while burning the burner so that the oxygen concentration in the combustion product becomes 15% or less, and the gasified combustible gas is
Combustion is completed while being guided to the secondary combustion chamber at 800 ° C or higher and staying for 2 seconds or more.

【0010】[0010]

【実施例】符号1はガス化室であって、2はガス化室1
の下部に設置した一次バーナである。3は二次燃焼室で
あって、4は連通部であり、5は二次空気噴出部であ
る。6は二次バーナを示し、7は排ガス洗浄塔への出口
部である。8は投入された廃棄物を示す。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Reference numeral 1 is a gasification chamber, and 2 is a gasification chamber 1.
It is a primary burner installed at the bottom of the. 3 is a secondary combustion chamber, 4 is a communication part, and 5 is a secondary air ejection part. 6 is a secondary burner, and 7 is an outlet part to the exhaust gas cleaning tower. 8 indicates the waste that has been thrown in.

【0011】ガス化室1に於いて、一次バーナ2が燃焼
を開始するが、その燃焼による燃焼生成物中の酸素濃度
が15%以下となるように、一次バーナ2の燃焼を制御
する。この低酸素濃度に制御することによって廃棄物8
自体は燃焼することはなくなる。しかして、一次バーナ
2で発生した熱で廃棄物8はガス化する。ガス化反応は
吸熱反応であるため、熱が与えられた分だけガス化する
ので、ガス化速度の制御が容易となる。ガス化された可
燃ガスは、連通部4を介して800℃以上の広い二次燃
焼室3(滞留時間2秒以上)に導き、充分な支燃剤の供
給をうけて燃焼を完結する。支燃剤としては、燃焼用二
次空気を空気噴出部5からそのまま二次燃焼室3に導入
してもよいし、又は、二次バーナ6において、燃焼生成
物中の酸素濃度が18%以上となるような高過剰空気燃
焼を実行させて、燃焼ガス中のO2 で完全燃焼させても
よい。二次燃焼室3の800℃以上の温度は二次バーナ
6によって制御維持される。
In the gasification chamber 1, the primary burner 2 starts combustion, but the combustion of the primary burner 2 is controlled so that the oxygen concentration in the combustion product due to the combustion becomes 15% or less. Waste 8 by controlling to this low oxygen concentration
It will not burn itself. Then, the waste 8 is gasified by the heat generated in the primary burner 2. Since the gasification reaction is an endothermic reaction, it is gasified by the amount of heat applied, so that the gasification rate can be easily controlled. The gasified combustible gas is guided to a wide secondary combustion chamber 3 (holding time of 2 seconds or more) at 800 ° C. or higher through the communication part 4, and completes combustion by receiving sufficient supply of the combustion-supporting agent. As the combustion-supporting agent, secondary air for combustion may be introduced into the secondary combustion chamber 3 as it is from the air ejection portion 5, or in the secondary burner 6, the oxygen concentration in the combustion product may be 18% or more. Such high excess air combustion may be performed to complete combustion with O 2 in the combustion gas. The temperature of 800 ° C. or higher in the secondary combustion chamber 3 is controlled and maintained by the secondary burner 6.

【0012】[0012]

【発明の効果】本発明は以上の通りであるので、次の諸
効果がある。ガス化室内の廃棄物は、O2%の低い雰
囲気中でバーナにおいて発生する熱で加熱されガス化す
る。従って、自らは燃焼し得ず、与えられた熱に見合う
だけガス化が実行される。このことにより、ガス化速度
はバーナの燃焼量によって制御でき、一定に保持するこ
とも容易である。廃棄物が低発熱量物質であっても、
バーナによってガス化に必要な熱量は充分に与えること
ができる。このように、ガス化速度は廃棄物によら
ず、バーナの燃焼量のみで完全にコントロールできるの
みならず、ガス化室の温度も同様に完全に制御できる。
ガス化された一定量の可燃分は、広く(滞留時間2秒
以上)、且つ800℃以上の二次燃焼室に於いて支燃剤
と混合され燃焼を完結し、黒煙の発生は完全に防止でき
る。
As described above, the present invention has the following effects. The waste in the gasification chamber is heated and gasified by the heat generated in the burner in an atmosphere of low O 2 %. Therefore, it cannot burn itself, and the gasification is performed as much as the heat given. As a result, the gasification rate can be controlled by the combustion amount of the burner, and it is easy to keep it constant. Even if the waste is a low calorific substance,
The burner can provide a sufficient amount of heat for gasification. In this way, the gasification rate does not depend on the waste but can be completely controlled only by the combustion amount of the burner, and the temperature in the gasification chamber can be completely controlled as well.
A certain amount of combustible gasified is wide (residence time is 2 seconds or more) and is mixed with the combustion-supporting agent in the secondary combustion chamber at 800 ° C or higher to complete combustion, and black smoke is completely prevented. it can.

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

【図1】従来の廃棄物焼却炉の説明的断面図である。FIG. 1 is an explanatory sectional view of a conventional waste incinerator.

【図2】従来の廃棄物焼却炉の説明的断面図である。FIG. 2 is an explanatory sectional view of a conventional waste incinerator.

【図3】従来の廃棄物焼却炉の説明的断面図である。FIG. 3 is an explanatory sectional view of a conventional waste incinerator.

【図4】本発明の断面的節説明的断面図である。FIG. 4 is a cross-sectional explanatory cross-sectional view of the present invention.

【符号の説明】[Explanation of symbols]

1 ガス化室 2 一次バーナ 3 二次燃焼室 4 連通部 5 二次空気噴出部 6 二次バーナ 7 排気部 8 廃棄物 1 Gasification chamber 2 Primary burner 3 Secondary combustion chamber 4 Communication section 5 Secondary air jet section 6 Secondary burner 7 Exhaust section 8 Waste

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 F23G 5/50 N (72)発明者 小菅 浩 京都府宇治市伊勢田町名木2−1−67─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location F23G 5/50 N (72) Inventor Hiroshi Kosuge 2-1-6 Nagi, Iseta Town, Uji City, Kyoto Prefecture

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 ガス化室において燃焼生成物中の酸素濃
度が15%以下となるように、バーナを燃焼させなが
ら、前記ガス化室中の廃棄物を吸熱ガス化反応させ、ガ
ス化された可燃ガスは800℃以上の二次燃焼室に導き
燃焼を完結させることを特徴とする廃棄物焼却炉の燃焼
方法。
1. The endothermic gasification reaction of the waste in the gasification chamber is gasified while burning the burner so that the oxygen concentration in the combustion product is 15% or less in the gasification chamber. Combustion gas is introduced into a secondary combustion chamber of 800 ° C or higher to complete combustion, and a combustion method for a waste incinerator.
【請求項2】 二次燃焼室において、燃焼生成物中の酸
素濃度が18%以上となるような高過剰空気燃焼を二次
バーナにより実行させて、その燃焼ガス中のO2でガス
化された可燃ガスを燃焼させることを特徴とする請求項
1記載の廃棄物焼却炉の燃焼方法。
2. In the secondary combustion chamber, high excess air combustion is carried out by a secondary burner so that the oxygen concentration in the combustion products becomes 18% or more, and is gasified with O 2 in the combustion gas. The method for burning a waste incinerator according to claim 1, wherein the combustible gas is burned.
【請求項3】 二次燃焼室に空気のみを導入して、ガス
化された可燃ガスを燃焼させることを特徴とする請求項
1記載の廃棄物焼却炉の燃焼方法。
3. The combustion method for a waste incinerator according to claim 1, wherein only the air is introduced into the secondary combustion chamber to burn the gasified combustible gas.
【請求項4】 二次燃焼室において、ガス化された可燃
ガスを2秒以上滞留させて燃焼させることを特徴とする
請求項1記載の廃棄物焼却炉の燃焼方法。
4. The combustion method for a waste incinerator according to claim 1, wherein the combustible gas that has been gasified is retained for 2 seconds or more and burned in the secondary combustion chamber.
JP31477394A 1994-12-19 1994-12-19 Combustion method for waste incinerator Pending JPH08178237A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP31477394A JPH08178237A (en) 1994-12-19 1994-12-19 Combustion method for waste incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP31477394A JPH08178237A (en) 1994-12-19 1994-12-19 Combustion method for waste incinerator

Publications (1)

Publication Number Publication Date
JPH08178237A true JPH08178237A (en) 1996-07-12

Family

ID=18057421

Family Applications (1)

Application Number Title Priority Date Filing Date
JP31477394A Pending JPH08178237A (en) 1994-12-19 1994-12-19 Combustion method for waste incinerator

Country Status (1)

Country Link
JP (1) JPH08178237A (en)

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