JP3366200B2 - Combustion control method in incinerator - Google Patents

Combustion control method in incinerator

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Publication number
JP3366200B2
JP3366200B2 JP33086096A JP33086096A JP3366200B2 JP 3366200 B2 JP3366200 B2 JP 3366200B2 JP 33086096 A JP33086096 A JP 33086096A JP 33086096 A JP33086096 A JP 33086096A JP 3366200 B2 JP3366200 B2 JP 3366200B2
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Japan
Prior art keywords
waste
incinerator
air
combustion
primary
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 - Fee Related
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JP33086096A
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Japanese (ja)
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JPH10169946A (en
Inventor
敬三 挟間
信 大竹
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Mitsui Engineering and Shipbuilding Co Ltd
Mitsui E&S Holdings Co Ltd
Original Assignee
Mitsui Engineering and Shipbuilding Co Ltd
Mitsui E&S Holdings Co Ltd
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Application filed by Mitsui Engineering and Shipbuilding Co Ltd, Mitsui E&S Holdings Co Ltd filed Critical Mitsui Engineering and Shipbuilding Co Ltd
Priority to JP33086096A priority Critical patent/JP3366200B2/en
Publication of JPH10169946A publication Critical patent/JPH10169946A/en
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Publication of JP3366200B2 publication Critical patent/JP3366200B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Fluidized-Bed Combustion And Resonant Combustion (AREA)
  • Incineration Of Waste (AREA)

Description

【発明の詳細な説明】 【0001】 【発明の属する技術分野】本発明は焼却炉における燃焼
制御方法に係り、特に、廃棄物(家庭やオフィスなどか
ら出される都市ごみなどの一般廃棄物、廃プラスチッ
ク、カーシュレッダー・ダスト、廃オフィス機器、電子
機器、化成品等の産業廃棄物など、可燃物を含むもの)
を焼却処理するのに好適な焼却炉における燃焼制御方法
に関する。 【0002】 【従来の技術】都市ごみ等の一般廃棄物や、廃プラスチ
ックなどの産業廃棄物等、可燃物を含むごみなどの廃棄
物の処理装置の一つとして、廃棄物を焼却炉に投入し、
燃焼用空気を送入して焼却し、排ガスとして排出させる
とともに、不燃物を回収する方法が一般に行われてい
る。燃焼用空気としては、廃棄物を燃焼させるための一
次空気と、一次空気によっても不完全燃焼が生じてCO
が発生した場合、これを完全燃焼させるために二次空気
を供給する。また、焼却炉には、例えば、燃焼速度の速
い流動床式焼却炉が使用され、炉床に堆積する流動砂に
空気を吹き込み、躍るように砂を流動させて、不燃物は
砂とともに下方へ落下させ、燃焼物は排ガスとして排出
する。 【0003】 【発明が解決しようとする課題】このような焼却炉の運
転を停止する立下げ時の制御の参考例を、図3を参照し
て説明する。焼却炉の立下げ時には、まず、ごみ等の廃
棄物の供給運転を停止し、焼却炉への廃棄物の投入を停
止する。次に、二次空気および一次空気を、図示するよ
うに、それぞれ2段階に停止する。ごみ投入停止後も炉
内に残っている廃棄物を燃焼させるために、一次空気は
多少遅らせて送風停止する。このような制御で、炉出口
排ガス温度は通常時の約850℃から下降し、O2濃度
が通常時の13%から立下げ時は18%へ上昇してい
る。しかし、CO濃度も通常燃焼時は10ppm以下で
あるのに、立下げ時には一時的にせよ500ppm以上
に上昇しており、不完全燃焼が生じていることがわか
る。これは、例えば流動床式焼却炉のように燃焼速度の
速い焼却炉では、停止時の立下げをわずか数分間で完了
するためと推測されるが、いずれにしても、このCOピ
ークが解消されるように、炉内温度の低下を防ぐため、
灯油等の補助燃料を用いて立下げており、経済的にもメ
ンテナンス上も非効率的であり、また、一時的にせよC
O濃度の上昇は好ましくないという問題があった。 【0004】本発明の目的は、上記課題を解決するため
になされたもので、焼却炉の立下げ時、廃棄物の投入停
止とともに、燃焼用空気量を制御して不完全燃焼を防止
し、CO濃度の上昇しない安定した立下げを可能にする
焼却炉における燃焼制御方法を提供することである。 【0005】 【課題を解決するための手段】上記課題を以下のように
解決した。発明は、ごみなどの廃棄物を廃棄物供給手
段を介して流動床式焼却炉へ投入し、前記焼却炉内へ
次空気および二次空気を供給して焼却する流動床式焼却
炉の立下げ時に、まず、前記廃棄物の供給を停止し、次
に、前記二次空気および前記一次空気の送風を停止する
前に、前記焼却炉内の温度を保持するようにして、前記
二次空気の供給を徐々に減らす漸減区間A、および、前
記一次空気の供給を徐々に減らす漸減区間Bを設定し
て、それぞれの漸減区間の経過後に、前記二次空気、次
いで前記一次空気の送風を停止するとともに、前記一次
空気の漸減区間Aの漸減勾配を、前記二次空気の漸減区
間Bの漸減勾配より緩やかに制御することを特徴とす
る。このような制御により、炉内に残った廃棄物の不完
全燃焼が防止され、CO濃度の上昇しない焼却炉の立下
げを実現できる。すなわち、二次空気によりCOの発生
を防止するとともに、炉内に残った廃棄物の一次燃焼を
有効に行うことにより、安定した立下げを実現できる。
そのため、短時間のうちに運転を停止できる流動床式焼
却炉において、立下げ時の不完全燃焼が防止され、CO
濃度の上昇を防止することができるので、補助燃料等の
手段が不要であり、省力化に極めて有効である。 【0006】 【発明の実施の形態】以下、本発明の実施の形態を、図
面を参照して説明する。図1は、本発明における燃焼制
御方法の一実施形態を説明するための説明図である。図
1に示すように、焼却炉1は燃焼速度の速い焼却炉とし
て、流動床式焼却炉を用いている。焼却炉1への廃棄物
投入系路には、急傾斜により廃棄物を定量的にパンに載
せて搬送する急傾斜型のパン型コンベア2と、燃焼に不
要な空気の流入や焼却炉内からの逆火を防止するため
に、コンベア2から搬送されてきた廃棄物を、羽根車の
区画された桝で定量的に分取して焼却炉1へ投入するエ
アシール装置3とが配置されている。 【0007】また、焼却炉1には、押込(一次)空気弁
4、押込(一次)送風機5を具備した押込(一次)空気
配管6と、二次空気弁7、二次送風機8を具備した二次
空気配管9とがそれぞれ接続され、さらに、本実施形態
では、焼却炉1内の任意の位置に配設した温度センサ1
0と、押込空気弁4および二次空気弁7とを、制御部1
1を介して接続している。このような構成により、焼却
炉の立下げ時、廃棄物の投入を停止した後、温度センサ
を監視し、炉内温度を一定範囲に維持して不完全燃焼を
防止し、CO濃度の上昇を防ぐために、一次空気および
二次空気の供給を制御するようにした。なお、本実施形
態では、排ガス出口温度検出部12と、コンベア2の運
転モータ、およびエアシール装置3の羽根車を回転させ
るモータとを接続し、排ガス出口温度によって廃棄物の
供給を制御できるようになっている。 【0008】次に、図2を用いて、本発明方法により焼
却炉を立下げる場合の制御例を説明する。図2に示すよ
うに、まず、廃棄物の供給を停止する。次に、二次空気
および一次空気の送風を停止する前に、炉内温度センサ
10による炉内温度を保持するようにして、二次空気の
供給を徐々に減らす漸減区間A、および、一次空気につ
いても同様に漸減区間Bを設定して、それぞれの漸減区
間の経過後に、二次空気、次いで一次空気の送風を停止
するように制御した。炉内に残っている廃棄物を燃焼さ
せるために、一次空気の漸減勾配を二次空気に比べて緩
やかにしている。このような制御を行うことによって、
図3の参考例に比較して、CO濃度の上昇が全くみられ
なかった。また、炉出口排ガス温度も徐々に下降し、O
2も上昇している。 【0009】次に、図4を参照して、本発明における燃
焼制御方法を適用した流動床式廃棄物焼却装置について
説明する。図4は、流動床式廃棄物焼却装置の一例を示
す構成図である。図4に示すように、廃棄物31はピッ
ト32内に一時的に滞留され、適宜、クレーン33で廃
棄物供給機34へ搬送される。廃棄物供給機34にはス
クリューフィーダが用いられ、大きく分けて次の二つの
機能がある。廃棄物の入っている袋を破ったり、あるい
は、廃棄物を解砕したり切り出す機能と、投入不適物を
チェックしたり排出する機能である。前者の機能は、袋
廃棄物等をスクリュー間やスクリューとケーシングとの
間で圧縮ほぐしを繰返し、解砕しながら廃棄物を切り出
す機能である。後者の機能は、一定以上の大きさの不燃
物の投入制限をし、また、スクリューを正逆転させてご
みなどの廃棄物をほぐしたり、大型の廃棄物や破解抵抗
の強い廃棄物は、スクリューを逆転させて後部排出口か
ら排出する機能である。 【0010】廃棄物供給機34を通過して粗破砕された
廃棄物は調量機35へ送給される。調量機35は、焼却
炉内で安定した燃焼を行うために、炉内へ供給する廃棄
物の量を調整し、一定量をコンスタントに供給しようと
するものである。本実施形態では、急傾斜型のパン型コ
ンベアが用いられ、ホッパ内の廃棄物をコンベアのパン
上に載せて搬送する。調量機35から搬送された廃棄物
は、エアシール装置36を介して焼却炉37へ供給され
る。エアシール装置36は、燃焼炉37の廃棄物供給部
に設けられ、焼却炉内の気密性を保持し、廃棄物を焼却
炉へ供給する際、燃焼に不要な空気の流入や、焼却炉内
からの逆火を防止するためのものである。本実施形態で
は、回転する羽根車によって廃棄物を分取し、気密構造
の焼却炉内へ順次供給するようになっている。 【0011】焼却炉37は流動床式の焼却炉で、炉床に
堆積した流動砂(流動媒体)38に、押込空気39を吹
き込んで躍るように流動させることにより、炉内の燃焼
温度を一定に維持したり、廃棄物31の中の不燃物を流
動する砂38とともに下に落したりする。砂38を流動
させるために押し込む空気39は、一次燃焼させるため
の一次空気でもある。一次空気39による不完全燃焼は
二次空気40で完全燃焼させ、クリーンな排ガス41に
して排出する。本実施形態では、図1にも示したよう
に、炉内に温度センサを配設し、炉内温度に応じて一次
空気および二次空気の供給量を制御するようになってい
る。なお、燃焼調節は助熱バーナ42で燃料43を燃焼
させて行う。一般に燃料は重油が用いられる。また、一
次空気39と二次空気40の分配の仕方によっても燃焼
温度をコントロールできる。通常、流動床式焼却炉37
に投入された廃棄物31は、600〜700℃に加熱さ
れた流動砂38によって、短時間のうちに乾燥、完全焼
却される。また、流動床式焼却炉37の出口排ガス温度
は800〜900℃に保持されている。 【0012】焼却炉内で燃焼できない不燃物は、流動砂
と混在して流動媒体排出機44により炉外へ排出され、
流動媒体分級機45で流動砂と振るい分けされ、磁選機
46により鉄分47とその他の不燃物(非鉄不燃物4
8)とに選り分けられ、それぞれ鉄分バンカ49および
不燃物バンカ50から回収される。流動媒体分級機45
で振るい分けされた流動砂は、流動媒体搬送機51によ
り燃焼炉37内へ戻される。なお、ピット32に溜まる
廃棄物汚水52は、濾過噴霧ポンプ53を介して焼却炉
37内へ噴霧し高温酸化処理する。また、ピット32な
どからの廃棄物31の臭気は、燃焼用空気として、二次
空気40、一次空気(押込空気)39などに吸引し、炉
内へ供給して高温酸化分解して脱臭される。ピット32
には廃棄物投入扉54が設けられている。さらに、焼却
炉37には、汚泥55なども投入して焼却処理すること
が可能である。 【0013】このような流動床式廃棄物処理装置におい
て、焼却炉立下げ時に、図1にも示したように、炉内温
度を保持しながら、二次および一次空気の供給量を漸減
させる制御を行うことによって、短時間のうちに運転を
停止できる流動床式焼却炉において、不完全燃焼が防止
され、CO濃度の上昇を防止することができるので、補
助燃料等の手段が不要であり、省力化に極めて有効であ
る。以上、本発明を図示の実施形態について詳述した
が、本発明はそれらの実施形態のみに限定されるもので
はなく、本発明の精神を逸脱せずして種々改変を加え、
多種多様の変形をなし得ることは云うまでもない。 【0014】 【発明の効果】以上説明したように本発明における燃焼
制御方法によれば、焼却炉の立下げ時、廃棄物の投入停
止とともに、燃焼用空気の供給量を制御することによ
り、不完全燃焼を防止し、CO濃度の上昇しない安定し
た立下げを実施することができ、そのため、従来行って
いた補助燃料による燃焼も不要になるという優れた効果
がある。
Description: BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for controlling combustion in an incinerator, and more particularly, to waste (general waste such as municipal waste from homes and offices, waste Including combustible materials such as plastic, car shredder dust, waste office equipment, electronic equipment, industrial waste such as chemical products)
The present invention relates to a method for controlling combustion in an incinerator suitable for incineration of incinerators. 2. Description of the Related Art Waste is introduced into an incinerator as one of the treatment apparatuses for waste such as municipal solid waste such as general waste, industrial waste such as waste plastic, and the like, including combustible waste. And
In general, a method is employed in which combustion air is sent in and incinerated, exhausted as exhaust gas, and incombustibles are collected. As combustion air, primary air for burning waste and incomplete combustion also occur due to the primary air to reduce CO2
Is generated, secondary air is supplied to completely combust this. The incinerator is, for example, a fluidized bed incinerator with a fast burning rate, in which air is blown into the fluidized sand that accumulates on the hearth, causing the sand to flow so that the incombustibles move downward with the sand. It is dropped and the combustion products are discharged as exhaust gas. A reference example of control at the time of shutdown for stopping the operation of the incinerator will be described with reference to FIG. When shutting down the incinerator, first, the operation of supplying waste such as refuse is stopped, and the input of waste to the incinerator is stopped. Next, the secondary air and the primary air are stopped in two stages as shown in the figure. In order to burn the waste remaining in the furnace even after the refuse is stopped, the primary air is blown off with a slight delay. Under such control, the temperature of the exhaust gas from the furnace is lowered from about 850 ° C. in the normal state, and the O 2 concentration is increased from 13% in the normal state to 18% in the fall. However, the CO concentration was 10 ppm or less during normal combustion, but rose temporarily to 500 ppm or more at the time of shutdown, indicating that incomplete combustion has occurred. This is presumed to be because in an incinerator with a fast burning rate such as a fluidized bed incinerator, the shutdown during shutdown is completed in only a few minutes, but in any case, this CO peak is eliminated. To prevent the furnace temperature from dropping,
Shutdown is performed using auxiliary fuel such as kerosene, which is inefficient in terms of economics and maintenance.
There was a problem that an increase in the O concentration was not preferable. An object of the present invention is to solve the above-mentioned problems. When the incinerator is shut down, the supply of waste is stopped, and the amount of combustion air is controlled to prevent incomplete combustion. An object of the present invention is to provide a combustion control method in an incinerator that enables stable shutdown without increasing the CO concentration. [0005] The above-mentioned problems have been solved as follows. The present invention, waste such as dust through the waste supply means was charged into the fluidized bed incinerator, one into said incinerator
Fluidized bed incineration in which secondary air and secondary air are supplied for incineration
When shutting down the furnace , first stop the supply of the waste ,
Then, the blowing of the secondary air and the primary air is stopped.
Before, so as to hold the temperature inside the incinerator, the
A gradually decreasing section A gradually decreasing the supply of the secondary air and before
Set the gradually decreasing section B to gradually reduce the primary air supply.
After the elapse of each gradual section, the secondary air
Then, while stopping the blowing of the primary air,
The gradually decreasing gradient of the gradually decreasing section A of the air is determined by the decreasing section of the secondary air.
It is characterized in that the control is performed more gently than the gradually decreasing gradient of the interval B. By such control, incomplete combustion of the waste remaining in the furnace is prevented, and the shutdown of the incinerator without increasing the CO concentration can be realized. That is, by preventing the generation of CO by the secondary air and effectively performing the primary combustion of the waste remaining in the furnace, a stable shutdown can be realized.
Therefore, in a fluidized bed incinerator that can be shut down in a short time, incomplete combustion during shutdown is prevented, and CO
Since the increase in the concentration can be prevented, no means such as auxiliary fuel is required, which is extremely effective for labor saving. Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is an explanatory diagram illustrating an embodiment of the combustion control method according to the present invention. As shown in FIG. 1, the incinerator 1 uses a fluidized bed incinerator as an incinerator with a high burning rate. A steeply inclined pan-type conveyer 2 for quantitatively placing waste on a pan and transporting the waste by steeply inclined, and a flow of air unnecessary for combustion and from the inside of the incinerator to a waste introduction path to the incinerator 1. In order to prevent flashback, an air sealing device 3 for quantitatively collecting wastes conveyed from the conveyor 2 in a compartment defined by an impeller and feeding the waste into the incinerator 1 is provided. . The incinerator 1 also includes a push (primary) air valve 4, a push (primary) air pipe 6 having a push (primary) blower 5, a secondary air valve 7, and a secondary blower 8. The secondary air piping 9 is connected to each other. In the present embodiment, the temperature sensor 1 is disposed at an arbitrary position in the incinerator 1.
0, the pushing air valve 4 and the secondary air valve 7
1 are connected. With this configuration, when shutting down the incinerator, after the introduction of waste is stopped, the temperature sensor is monitored, the temperature in the furnace is maintained within a certain range, incomplete combustion is prevented, and a rise in the CO concentration is prevented. To prevent this, the supply of primary and secondary air was controlled. In the present embodiment, the exhaust gas outlet temperature detecting unit 12 is connected to the operation motor of the conveyor 2 and the motor for rotating the impeller of the air seal device 3 so that the supply of waste can be controlled by the exhaust gas outlet temperature. Has become. Next, an example of control when the incinerator is shut down by the method of the present invention will be described with reference to FIG. As shown in FIG. 2, the supply of the waste is first stopped. Next, before stopping the blowing of the secondary air and the primary air, the furnace temperature is maintained by the furnace temperature sensor 10, so that the supply of the secondary air is gradually reduced, and the primary air is gradually reduced. Similarly, a gradually decreasing section B was set, and after the elapse of each gradually decreasing section, control was performed such that the blowing of the secondary air and then the primary air was stopped. In order to burn the waste remaining in the furnace, the gradual gradient of the primary air is made gentler than that of the secondary air. By performing such control,
Compared with the reference example of FIG. 3, no increase in the CO concentration was observed. Also, the temperature of the exhaust gas from the furnace gradually decreases, and
2 is also rising. Next, a fluidized bed waste incinerator to which the combustion control method of the present invention is applied will be described with reference to FIG. FIG. 4 is a configuration diagram illustrating an example of a fluidized bed waste incineration apparatus. As shown in FIG. 4, the waste 31 temporarily stays in the pit 32, and is appropriately conveyed to the waste feeder 34 by the crane 33. A screw feeder is used for the waste feeder 34, and has the following two main functions. It has a function to break bags containing waste, or to crush or cut out waste, and a function to check and discharge unsuitable materials. The former function is a function of repeatedly compressing and loosening bag waste or the like between screws or between a screw and a casing, and cutting out waste while crushing. The latter function restricts the injection of non-combustible materials of a certain size or more, and also turns the screw forward and reverse to loosen waste such as garbage, and removes large-sized waste and waste with strong crushing resistance. Is a function of reversing and discharging from the rear outlet. [0010] The waste which has been roughly crushed after passing through the waste feeder 34 is sent to a metering machine 35. The metering machine 35 adjusts the amount of waste to be supplied to the incinerator and constantly supplies a constant amount thereof in order to perform stable combustion in the incinerator. In the present embodiment, a steeply inclined pan-type conveyor is used, and the waste in the hopper is transported on a pan of the conveyor. The waste conveyed from the metering machine 35 is supplied to the incinerator 37 via the air seal device 36. The air seal device 36 is provided in the waste supply part of the combustion furnace 37, maintains airtightness in the incinerator, and supplies air unnecessary for combustion when injecting waste into the incinerator. This is to prevent flashback. In the present embodiment, waste is collected by a rotating impeller and is sequentially supplied into an incinerator having an airtight structure. The incinerator 37 is a fluidized bed type incinerator, in which a forced sand 39 is blown into a fluidized sand (fluid medium) 38 deposited on the hearth to make the fluid flow so as to make the combustion temperature in the furnace constant. Or the incombustibles in the waste 31 are dropped together with the flowing sand 38. The air 39 pushed in to flow the sand 38 is also primary air for primary combustion. The incomplete combustion by the primary air 39 is completely burned by the secondary air 40 to be discharged as clean exhaust gas 41. In the present embodiment, as shown in FIG. 1, a temperature sensor is provided in the furnace, and the supply amounts of the primary air and the secondary air are controlled according to the furnace temperature. The combustion is adjusted by burning the fuel 43 with the auxiliary heat burner 42. Generally, heavy oil is used as the fuel. Also, the combustion temperature can be controlled by the manner of distribution of the primary air 39 and the secondary air 40. Usually, fluidized bed incinerator 37
The waste 31 put into the furnace is dried and completely incinerated in a short time by the fluidized sand 38 heated to 600 to 700 ° C. The temperature of the exhaust gas at the outlet of the fluidized bed incinerator 37 is maintained at 800 to 900 ° C. The incombustibles that cannot be burned in the incinerator are discharged out of the incinerator by the fluidized medium discharger 44 together with the fluidized sand.
It is separated from the fluidized sand by the fluidized media classifier 45 and the iron 47 and other noncombustibles (non-ferrous incombustibles 4) by the magnetic separator 46.
8) and are collected from the iron bunker 49 and the noncombustible bunker 50, respectively. Fluid medium classifier 45
The fluidized sand sieved in is returned to the combustion furnace 37 by the fluidized-medium transporter 51. The waste sewage 52 accumulated in the pits 32 is sprayed into the incinerator 37 via a filtration spray pump 53 and subjected to high-temperature oxidation treatment. Further, the odor of the waste 31 from the pit 32 or the like is sucked into the secondary air 40, the primary air (push air) 39 or the like as combustion air, supplied to the furnace, decomposed by high-temperature oxidative decomposition, and deodorized. . Pit 32
Is provided with a waste input door 54. Further, sludge 55 and the like can be put into the incinerator 37 for incineration. In such a fluidized bed type waste treatment apparatus, when the incinerator is shut down, as shown in FIG. 1, the control for gradually decreasing the supply amounts of the secondary and primary air while maintaining the furnace temperature is performed. In the fluidized bed incinerator, the operation of which can be stopped within a short period of time, incomplete combustion is prevented, and a rise in the CO concentration can be prevented. This is extremely effective for labor saving. As described above, the present invention has been described in detail with reference to the illustrated embodiments. However, the present invention is not limited to only those embodiments, and various modifications can be made without departing from the spirit of the present invention.
It goes without saying that a wide variety of modifications can be made. As described above, according to the combustion control method of the present invention, when the incinerator is shut down, the supply of waste air and the supply of combustion air are controlled at the same time as the supply of waste air is controlled. It is possible to prevent complete combustion and perform a stable shutdown without increasing the CO concentration. Therefore, there is an excellent effect that the conventional combustion with the auxiliary fuel is not required.

【図面の簡単な説明】 【図1】本発明における燃焼制御方法の一実施形態を説
明するための構成図である。 【図2】本発明の一制御例を説明するための図である。 【図3】本発明の制御の一参考例を説明するための図で
ある。 【図4】本発明を適用した流動床式廃棄物焼却装置の一
実施形態を示す構成図である。 【符号の説明】 1 焼却炉 2 パン型コンベア 3 エアシール装置 4 押込(一次)空気弁 5 押込(一次)送風機 6 押込(一次)空気配管 7 二次空気弁 8 二次送風機 9 二次空気配管 10 炉内温度センサ 11 制御部 12 排ガス出口温度検出部 31 廃棄物 32 ピット 33 クレーン 34 廃棄物供給機 35 調量機(急傾斜型コンベア) 36 エアシール装置 37 焼却炉 38 流動砂(流動媒体) 39 押込空気(一次空気) 40 二次空気 41 排ガス 42 助熱バーナ 43 燃料 44 流動媒体排出機 45 流動媒体分級機 46 磁選機 47 鉄分 48 非鉄不燃物 49 鉄分バンカ 50 不燃物バンカ 51 流動媒体搬送機 52 廃棄物汚水 53 濾過噴霧ポンプ 54 廃棄物投入扉 55 汚泥 A、B 漸減区間
BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a configuration diagram for explaining an embodiment of a combustion control method according to the present invention. FIG. 2 is a diagram for explaining one control example of the present invention. FIG. 3 is a diagram illustrating a reference example of control according to the present invention. FIG. 4 is a configuration diagram showing an embodiment of a fluidized bed waste incinerator to which the present invention is applied. [Description of Signs] 1 Incinerator 2 Bread conveyor 3 Air seal device 4 Push-in (primary) air valve 5 Push-in (primary) blower 6 Push-in (primary) air pipe 7 Secondary air valve 8 Secondary blower 9 Secondary air pipe 10 Furnace temperature sensor 11 Controller 12 Exhaust gas outlet temperature detector 31 Waste 32 Pit 33 Crane 34 Waste feeder 35 Metering machine (steeply inclined conveyor) 36 Air seal device 37 Incinerator 38 Fluid sand (fluid medium) 39 Pushing Air (primary air) 40 Secondary air 41 Exhaust gas 42 Heating burner 43 Fuel 44 Fluid medium discharger 45 Fluid medium classifier 46 Magnetic separator 47 Iron 48 Non-ferrous non-combustible material 49 Iron bunker 50 Non-combustible material bunker 51 Fluid media carrier 52 Waste Waste water 53 Filtration spray pump 54 Waste input door 55 Sludge A, B Gradual reduction section

フロントページの続き (56)参考文献 特開 平5−296430(JP,A) 特開 昭60−105808(JP,A) 特開 昭55−20359(JP,A) 特開 昭59−197716(JP,A) 特開 平8−145339(JP,A) 特開 昭61−38312(JP,A) (58)調査した分野(Int.Cl.7,DB名) F23G 5/50 F23G 5/30 F23C 10/28 Continuation of front page (56) References JP-A-5-296430 (JP, A) JP-A-60-105808 (JP, A) JP-A-55-20359 (JP, A) JP-A-59-197716 (JP) , A) JP-A-8-145339 (JP, A) JP-A-61-38312 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) F23G 5/50 F23G 5/30 F23C 10/28

Claims (1)

(57)【特許請求の範囲】 【請求項1】 ごみなどの廃棄物を廃棄物供給手段を介
して流動床式焼却炉へ投入し、前記焼却炉内へ一次空気
および二次空気を供給して焼却する流動床式焼却炉の
下げ時に、まず、前記廃棄物の供給を停止し、次に、前
記二次空気および前記一次空気の送風を停止する前に、
前記焼却炉内の温度を保持するようにして、前記二次空
気の供給を徐々に減らす漸減区間A、および、前記一次
空気の供給を徐々に減らす漸減区間Bを設定して、それ
ぞれの漸減区間の経過後に、前記二次空気、次いで前記
一次空気の送風を停止するとともに、前記一次空気の漸
減区間Aの漸減勾配を、前記二次空気の漸減区間Bの漸
減勾配より緩やかに制御することを特徴とする焼却炉に
おける燃焼制御方法。
(57) [Claims] [Claim 1] Waste such as garbage is put into a fluidized bed incinerator through a waste supply means, and primary air is introduced into the incinerator.
And when the fluidized bed incinerator for incineration by supplying secondary air is shut down, first, supply of the waste is stopped, and then
Before stopping the blowing of the secondary air and the primary air,
The secondary space is maintained by maintaining the temperature in the incinerator.
A gradually decreasing section A for gradually reducing the supply of air and the primary
Set the gradual decrease section B to gradually reduce the air supply.
After the elapse of each decreasing section, the secondary air and then the
While stopping the primary air blow, the primary air
The gradually decreasing gradient of the decreasing section A is set to the gradually decreasing section B of the secondary air.
A method for controlling combustion in an incinerator , wherein the control is performed more gently than the gradient .
JP33086096A 1996-12-11 1996-12-11 Combustion control method in incinerator Expired - Fee Related JP3366200B2 (en)

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Application Number Priority Date Filing Date Title
JP33086096A JP3366200B2 (en) 1996-12-11 1996-12-11 Combustion control method in incinerator

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JP3366200B2 true JP3366200B2 (en) 2003-01-14

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