Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP3619940B2 - Fluidized bed incinerator and its combustion method - Google Patents
[go: Go Back, main page]

JP3619940B2 - Fluidized bed incinerator and its combustion method - Google Patents

Fluidized bed incinerator and its combustion method Download PDF

Info

Publication number
JP3619940B2
JP3619940B2 JP30066694A JP30066694A JP3619940B2 JP 3619940 B2 JP3619940 B2 JP 3619940B2 JP 30066694 A JP30066694 A JP 30066694A JP 30066694 A JP30066694 A JP 30066694A JP 3619940 B2 JP3619940 B2 JP 3619940B2
Authority
JP
Japan
Prior art keywords
combustion
air
fluidized
fluidized bed
incinerator
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
Application number
JP30066694A
Other languages
Japanese (ja)
Other versions
JPH08159414A (en
Inventor
賢 深井
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.)
Mitsubishi Power Ltd
Original Assignee
Babcock Hitachi 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 Babcock Hitachi KK filed Critical Babcock Hitachi KK
Priority to JP30066694A priority Critical patent/JP3619940B2/en
Publication of JPH08159414A publication Critical patent/JPH08159414A/en
Application granted granted Critical
Publication of JP3619940B2 publication Critical patent/JP3619940B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Landscapes

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

Description

【0001】
【産業上の利用分野】
本発明は、性状が著しく変化する都市ごみ等の燃焼において無作為に発生する有害ガスを低減するのに好適な焼却炉及び焼却方法に関する。
【0002】
【従来の技術】
従来の流動床焼却炉は、流動層燃焼のみの燃焼形態で、都市ごみのように高カロリー物(ビニール、プラスチック製品、紙ごみ等)が偏って混入しており、しかも何時炉内に投入されるか予測ができない位に性状が著しく変化する焼却物では、無作為に発生する有害ガスの抑制が困難であり、例えばビニール、プラスチック製品等の高温で燃焼するごみが投入されると、これらの燃焼には過剰すぎる流動化空気によって、一時的に高温な燃焼となり、NOXが多量に発生する。
【0003】
また、同じく燃焼初期の空気量としては過剰すぎる流動化空気により、これらが早い燃焼速度で一気に燃え上がるため、多量に発生したCOが早い空塔速度により炉外へ排出される。
【0004】
【発明が解決しようとする課題】
上記従来技術は、流動床燃焼という一形態の燃焼方法しか行うことができないため、性状が著しく変化するような焼却物の燃焼においては、無作為に投入される高カロリーで揮発分の多い合成樹脂、油脂類の焼却に対して、それらが燃焼するための空気としては多すぎる流動化空気により早い燃焼速度で瞬時に燃焼し、一時的に高濃度のNOX,COといった有害ガスが発生する。
【0005】
本発明の目的は、燃焼状態、焼却物の投入量の変動に起因する有害ガスの発生を抑制することにある。
【0006】
【課題を解決するための手段】
上記の目的は、流動層には流動化空気を供給し、流動層の上方には燃焼用二次空気を供給し、燃焼状態を示す状態量と炉内に投入される焼却物の投入量とを検出して、その検出結果に基づいて流動化空気と燃焼用二次空気の供給を制御して前記焼却物を燃焼する流動床式焼却炉の燃焼方法において、焼却物の投入量の増加率と増加量との双方が予め設定された値よりも大きいとき、流動化空気の供給を制御して流動層の流動を停止させ、流動層燃焼からおき燃焼に切り替えることにより、達成される。
【0007】
上記の目的はまた、燃焼状態、焼却物の投入状態を、火炎の輝度・ガス量・ガス濃度・炉内圧力・炉内温度・焼却物の投入量・落下速度・大きさ等の状態量として検知する投入量検出手段、状態量検出手段と、これら投入量検出手段、状態量検出手段の出力に基づいて、ごみの投入量が一時的に増加した場合、先行して、あるいは追従して炉内への流動化空気をダンパー等にて、おき燃焼用の多段燃焼用空気ノズルへ切り替え、流動を数秒乃至数分停止し、流動層燃焼からおき燃焼に一時的に切り替える制御手段とを設けた流動床式焼却炉により達成される。
【0008】
流動化空気の供給量を零として、多段燃焼用空気ノズルから燃焼用空気を供給することにより、燃焼形態は燃焼速度の比較的早い流動層燃焼から、おき燃焼、つまり多段燃焼に切り替わる。この切り替えにより、揮発分の多い合成樹脂はゆっくりした燃焼速度により燃焼され、温度上昇が抑制され瞬間的なCO,NOの発生が低減される。また、紙ごみ等も、流動層燃焼の場合に比べて燃焼速度が遅くなり、瞬間的に高温が発生するのが避けられる。
【0009】
【実施例】
本発明の実施例を図面により説明する。図1は、本発明が適用された都市ごみ焼却炉を示し、図示の焼却炉は、都市ごみを焼却する流動床焼却炉本体18と、この焼却炉本体18に投入シュート17を介して接続され該投入シュート17を通して焼却炉本体18に焼却物、つまり都市ごみを供給する給じん機16と、流動床焼却炉本体18に流動化空気及び多段燃焼用空気を供給する空気供給系と、この空気供給系を制御する制御装置と、を含んで構成されている。
【0010】
流動床焼却炉本体18は、その下部に流動化空気を取り入れる複数の流動化空気ノズル24を備え、流動層部分の上方におき燃焼のための複数の多段燃焼空気ノズル14を備えている。
【0011】
空気供給系は、送風機19と、この送風機19の空気吐出口に接続され下流側が二つに分岐した送風機吐出ダクト20と、送風機吐出ダクト20の二つの下流端それぞれに接続された切り替えダンパ15A,15Bと、切り替えダンパ15Bの出側と焼却炉本体18の流動化空気ノズル24を流動化空気制御ダンパ12を介して接続する流動化空気供給ダクト21と、切り替えダンパ15Aの出側と焼却炉本体18の多段空気燃焼ノズル14を多段燃焼空気制御ダンパ13を介して接続する多段燃焼空気供給ダクト22と、を含んで構成されている。
【0012】
また、制御装置は、投入量検出手段と、状態量検出手段と、制御手段とを含んで構成されている。投入量検出手段は、投入シュート17に装着されて投入シュート17を通過する焼却物の影(大きさ)と通過速度を検出して出力する給じんセンサ1と、給じんセンサ1の出力を入力としてごみの投入量を算出、出力する演算装置2と、を含んで構成されている。
【0013】
状態量検出手段は、流動層内温度を検出、出力する層内温度計3と、炉内圧力を検出、出力する炉内圧力計4と、炉内温度を検出、出力する炉内温度計5と、炉出口酸素濃度を計測、出力する酸素濃度計6と、NOXの発生量を検出、出力する窒素酸化物濃度計7と、SOXの発生量を検出、出力する硫黄酸化物濃度計8と、COの発生量を検出、出力する一酸化炭素濃度計9と、火炎の輝度を検出するフレームディテクタ10と、を含んで構成されている。層内温度計3,炉内圧力計4,炉内温度計5及びフレームディテクタ10は焼却炉本体18に装着されているが、酸素濃度計6,窒素酸化物濃度計7,硫黄酸化物濃度計8,一酸化炭素濃度計9は、焼却炉本体18から燃焼排ガスを抜き出す排気ダクト23に装着されている。
【0014】
制御手段は、前記演算装置2,層内温度計3,炉内圧力計4,炉内温度計5,酸素濃度計6,窒素酸化物濃度計7,硫黄酸化物濃度計8,一酸化炭素濃度計9,フレームディテクタ10の出力を入力として、流動化空気制御ダンパ12,多段燃焼空気制御ダンパ13,切り替えダンパ15A,15Bの動作を制御する判別装置11と、を含んで構成されている。
【0015】
以下上記構成の設備の動作を説明する。給じん機16から送り出されたごみは、投入シュート17を通り、焼却炉本体18へ投入される。このとき投入シュート17の壁面に設置された給じんセンサ1によりごみの影(大きさ)と通過速度を検出し、そのデータを演算装置2に入力する。演算装置2は、入力された前記データに基づいてごみの投入量を算出し、得られた投入量を判別装置11に出力する。
【0016】
同様に、層内温度計3にて流動層内温度を、炉内圧力計4にて焼却炉炉内圧力を、炉内温度計5にて焼却炉炉内温度を、酸素濃度計6により焼却炉出口酸素濃度を、窒素酸化物濃度計7にて焼却炉におけるNOXの発生量を、硫黄酸化物濃度計8にて焼却炉におけるSOXの発生量を、一酸化炭素濃度計9により焼却炉におけるCOの発生量を、フレームディテクタ10により火炎の輝度を、それぞれ検出して判別装置11に取り込む。判別装置11は、予めプログラミングされたそれらのデータできまる条件に基づいて流動層燃焼またはおき燃焼を選択し、切り替えダンパ15A,15Bを制御して流動化空気供給ダクト21または、おき燃焼用の多段燃焼空気供給ダクト22のどちらかに空気を送りこむ。さらに、おき燃焼または流動層燃焼開始後も各センサからの検出信号を判別装置11に取り込み、判別装置11にてそのときの最適な燃焼空気量の調節と空気配分をそれぞれ流動化空気制御ダンパ12または多段燃焼空気制御ダンパ13をコントロールすることにより行う。
【0017】
前記演算装置2や各センサの出力が予め設定された複数の領域のどの領域に属するかが判別装置によって判定され、それによって流動層燃焼かおき燃焼かが選択されて空気供給系が制御される。通常の状態では流動層燃焼が選択されるが、流動層燃焼が選択された場合、当然切り替えダンパ15Bが開かれ、さらに流動化空気制御ダンパ12が開かれて流動化空気が焼却炉本体18に供給されるが、層内温度計3,炉内圧力計4,炉内温度計5,酸素濃度計6,窒素酸化物濃度計7,硫黄酸化物濃度計8,一酸化炭素濃度計9,フレームディテクタ10の各出力値が、予め設定された複数の領域のどの領域に属するかによって、流動化空気制御ダンパ12の開度や、切り替えダンパ15Aの開度、多段燃焼空気制御ダンパ13の開度が判別装置によって設定される。
【0018】
また、流動層燃焼中に、ごみの投入量が予め設定された増加率と増加量をともに超えて増加した場合はおき燃焼が選択される。おき燃焼が選択された場合、切り替えダンパ15Aが開かれ、さらに多段燃焼空気制御ダンパ13が開かれて多段燃焼空気ノズル14に空気が供給され、切り替えダンパ15Bが閉じられる。これによって流動媒体の流動が停止し、ごみは多段燃焼空気ノズル14を経て供給される空気により、静止した流動媒体上でおき燃焼状態(流動しない状態)で焼却される。おき燃焼が選択されるのは、例えばごみ供給量が、予め設定された増加率と増加量を超えて一時的に増加した場合などであり、このような場合にごみにおき燃焼を行わせることにより急激に燃焼が進行したり、有害ガスが発生したりするのが防がれる。おき燃焼は、ごみの投入量が急に増加した場合やごみがかたまって一時にどさっと投入されたような場合に対処するもので、長時間に亘って継続されることはない。ごみの供給量が予め設定された値よりも多い状態が継続する場合、給じん機が供給量を減らすか、もしくは流動化空気及びまたは二次燃焼空気(多段燃焼空気ノズルから供給される空気)を増加するように制御されるから、おき燃焼の選択が長時間継続する必要はなく、おき燃焼が継続する時間は、数秒乃至数分、長くても10分以下程度でよい。この時間の長さは、判別装置11に内装されたタイマー(図示せず)により設定される。
【0019】
図2に流動層燃焼とおき燃焼が切り替えられる場合の制御手順の例を示す。
【0020】
図1に示す実施例では、流動化空気供給ダクト21には、環状の流動化空気ヘッダ25が設けられており、個々の流動化空気ノズル24は流動化空気ヘッダ25に流動化空気ヘッダ配管26を介して接続されている。各流動化空気ヘッダ配管26に止め弁を設け、この止め弁の開度を判別装置11の出力に基づいて調節するようにすれば、焼却物の一部は流動床燃焼させ、他の部分ではおき燃焼をさせるようにすることができる。この方法は、投入されるごみの性状に差があり、特定の性状のごみが常に炉の特定の場所に堆積するような場合に効果的である。
【0021】
【発明の効果】
本発明によれば、ごみの投入量、燃焼状態に適した燃焼形態(流動層燃焼とおき燃焼のいずれか、もしくは両者を複合した燃焼)を選択でき、給じん量、発熱量の変動が大きい都市ごみ等の焼却処理時に発生するCO,NOX,SOX等の有害ガスの発生が低減される。
【図面の簡単な説明】
【図1】本発明の実施例を示す焼却設備の概念図である。
【図2】本発明に係る焼却炉の制御方法の実施例を示す手順図である。
【符号の説明】
1 給じんセンサ 2 演算装置
3 層内温度計 4 炉内圧力計
5 炉内温度計 6 酸素濃度計
7 窒素酸化物濃度計 8 硫黄酸化物濃度計
9 一酸化炭素濃度計 10 フレームディテクタ
11 判別装置 12 流動化空気制御ダンパ
13 多段燃焼空気制御ダンパ 14 多段燃焼空気ノズル
15A,15B 切り替えダンパ 16 給じん機
17 投入シュート 18 焼却炉本体
19 送風機 20 送風機吐出ダクト
21 流動化空気供給ダクト 22 多段燃焼空気供給ダクト
23 排気ダクト 24 流動化空気ノズル
25 流動化空気ヘッダ 26 流動化空気ヘッダ配管
[0001]
[Industrial application fields]
The present invention relates to an incinerator and an incineration method suitable for reducing harmful gases randomly generated in combustion of municipal waste or the like whose properties change significantly.
[0002]
[Prior art]
A conventional fluidized bed incinerator is a combustion type that uses only fluidized bed combustion, and high-calorie substances (vinyl, plastic products, paper waste, etc.) are mixed in an unbalanced manner like municipal waste. It is difficult to control harmful gases generated at random for incinerators whose properties change to such an extent that they cannot be predicted. For example, if garbage that burns at high temperatures, such as vinyl and plastic products, is introduced, Fluidized air that is excessive for combustion temporarily becomes high-temperature combustion, and a large amount of NOx is generated.
[0003]
Similarly, fluidized air that is too excessive as the amount of air at the early stage of combustion burns at a high rate at a high combustion speed, so that a large amount of CO is discharged outside the furnace at a high superficial velocity.
[0004]
[Problems to be solved by the invention]
The above prior art can only perform one form of combustion method called fluidized bed combustion, so in the combustion of incinerated products whose properties change significantly, a high-calorie, high-volatility synthetic resin that is randomly introduced In contrast to the incineration of fats and oils, the fluidized air that is too much as the air for burning them instantaneously burns at a fast combustion rate, and temporarily generates harmful gases such as high concentrations of NOx and CO.
[0005]
An object of the present invention is to suppress the generation of harmful gases due to fluctuations in the combustion state and the amount of incinerated materials to be charged.
[0006]
[Means for Solving the Problems]
The purpose of the above is to supply fluidized air to the fluidized bed and supply secondary air for combustion above the fluidized bed. The amount of state indicating the combustion state and the amount of incinerated material charged into the furnace In the combustion method of the fluidized bed incinerator for controlling the supply of fluidized air and secondary air for combustion based on the detection result and burning the incinerated product, the rate of increase in the amount of incinerated product input This is achieved by controlling the supply of fluidized air to stop the flow of the fluidized bed and switching from fluidized bed combustion to combustion when both of the increase amount and the increase amount are larger than preset values .
[0007]
The above purpose is also to set the combustion state and the incinerated state as the state quantity such as flame brightness, gas amount, gas concentration, furnace pressure, furnace temperature, amount of incinerated material input, drop speed, size, etc. Based on the output of the input amount detecting means, the state amount detecting means, and the outputs of these input amount detecting means and the state amount detecting means, if the waste input amount temporarily increases, the furnace is preceded or followed up. There is provided control means for switching the fluidized air into the multi-stage combustion air nozzle for combustion by a damper or the like, stopping the flow for several seconds to several minutes, and temporarily switching from fluidized bed combustion to combustion. Achieved by fluidized bed incinerator.
[0008]
By setting the supply amount of fluidized air to zero and supplying combustion air from the multistage combustion air nozzle, the combustion mode is switched from fluidized bed combustion having a relatively fast combustion speed to vertical combustion, that is, multistage combustion. By this switching, the synthetic resin with a large amount of volatile matter is burned at a slow burning rate, the temperature rise is suppressed, and the instantaneous generation of CO and NO x is reduced. In addition, paper dust or the like has a burning rate that is slower than that in the case of fluidized bed combustion, and an instantaneously high temperature can be avoided.
[0009]
【Example】
Embodiments of the present invention will be described with reference to the drawings. FIG. 1 shows a municipal waste incinerator to which the present invention is applied. The incinerator shown in the figure is connected to a fluidized bed incinerator body 18 for incinerating municipal waste, and this incinerator body 18 is connected via an input chute 17. baked却物the incinerator body 18 through the chute 17, i.e. a paper precipitator 16 for supplying the municipal waste, and air supply system for supplying fluidizing air and the multi-stage combustion air to the fluidized bed incinerator body 18, the And a control device that controls the air supply system.
[0010]
The fluidized bed incinerator main body 18 includes a plurality of fluidized air nozzles 24 for taking fluidized air into the lower portion thereof, and a plurality of multistage combustion air nozzles 14 for combustion that are placed above the fluidized bed portion.
[0011]
The air supply system includes a blower 19, a blower discharge duct 20 that is connected to the air discharge port of the blower 19 and has a downstream branching into two, and a switching damper 15 </ b> A connected to each of the two downstream ends of the blower discharge duct 20. 15B, the fluidized air supply duct 21 connecting the outlet side of the switching damper 15B and the fluidizing air nozzle 24 of the incinerator body 18 via the fluidizing air control damper 12, the outlet side of the switching damper 15A, and the incinerator body A multi-stage combustion air supply duct 22 for connecting 18 multi-stage air combustion nozzles 14 via a multi-stage combustion air control damper 13.
[0012]
The control device includes an input amount detection unit, a state amount detection unit, and a control unit. Input amount detecting means includes a sheet dust sensor 1 for shadow baked却物you pass the input chute 17 are attached to the chute 17 (size) and detect and passing speed output, the output of Kyujin sensor 1 And an arithmetic unit 2 that calculates and outputs the amount of waste input.
[0013]
The state quantity detection means includes an in-bed thermometer 3 for detecting and outputting the fluidized bed temperature, an in-furnace pressure gauge 4 for detecting and outputting the in-furnace pressure, and an in-furnace thermometer 5 for detecting and outputting the in-furnace temperature. An oxygen concentration meter 6 that measures and outputs the furnace outlet oxygen concentration, a nitrogen oxide concentration meter 7 that detects and outputs the amount of NOX generated, and a sulfur oxide concentration meter 8 that detects and outputs the amount of SOX generated , A carbon monoxide concentration meter 9 that detects and outputs the amount of CO generated, and a frame detector 10 that detects the luminance of the flame. The in-layer thermometer 3, the in-furnace pressure gauge 4, the in-furnace thermometer 5 and the frame detector 10 are mounted on the incinerator body 18, but the oxygen concentration meter 6, the nitrogen oxide concentration meter 7, the sulfur oxide concentration meter. 8. The carbon monoxide concentration meter 9 is attached to an exhaust duct 23 that extracts combustion exhaust gas from the incinerator body 18.
[0014]
The control means includes the arithmetic device 2, the in-layer thermometer 3, the in-furnace pressure gauge 4, the in-furnace thermometer 5, the oxygen concentration meter 6, the nitrogen oxide concentration meter 7, the sulfur oxide concentration meter 8, the carbon monoxide concentration. A discriminating device 11 that controls the operation of the fluidizing air control damper 12, the multistage combustion air control damper 13, and the switching dampers 15A and 15B using the output of the total 9 and the frame detector 10 as an input.
[0015]
The operation of the equipment having the above configuration will be described below. Garbage delivered from the dust feeder 16 passes through the input chute 17 and is input to the incinerator main body 18. At this time, the dust supply sensor 1 installed on the wall surface of the charging chute 17 detects the dust shadow (size) and the passing speed, and inputs the data to the arithmetic unit 2. The arithmetic device 2 calculates the input amount of garbage based on the input data, and outputs the obtained input amount to the determination device 11.
[0016]
Similarly, the fluidized bed temperature is measured with the in-bed thermometer 3, the pressure inside the incinerator with the pressure gauge 4 in the furnace, the temperature inside the incinerator with the temperature gauge 5, and incinerated with the oxygen concentration meter 6. Oxygen concentration at the furnace outlet, NOx generation amount in the incinerator with the nitrogen oxide concentration meter 7, SOX generation amount in the incinerator with the sulfur oxide concentration meter 8, and in the incinerator with the carbon monoxide concentration meter 9 The amount of CO generated is detected by the flame detector 10 and the brightness of the flame is detected and taken into the discriminator 11. The discriminating device 11 selects fluidized bed combustion or extra combustion based on preprogrammed conditions based on those data, and controls the switching dampers 15A and 15B to control the fluidized air supply duct 21 or multistage for extra combustion. Air is fed into one of the combustion air supply ducts 22. Further, the detection signals from the respective sensors are taken into the discriminating device 11 even after the start of the vertical combustion or the fluidized bed combustion, and the discriminating device 11 adjusts the optimal combustion air amount and the air distribution at that time respectively by the fluidizing air control damper 12. Alternatively, the control is performed by controlling the multistage combustion air control damper 13.
[0017]
A determination device determines which region of the plurality of predetermined regions the outputs of the arithmetic unit 2 and each sensor belong to, and thereby selects fluidized bed combustion or superficial combustion to control the air supply system. . In a normal state, fluidized-bed combustion is selected. However, when fluidized-bed combustion is selected, the switching damper 15B is naturally opened, and the fluidized air control damper 12 is opened, so that fluidized air enters the incinerator body 18. In-bed thermometer 3, furnace pressure gauge 4, furnace thermometer 5, oxygen concentration meter 6, nitrogen oxide concentration meter 7, sulfur oxide concentration meter 8, carbon monoxide concentration meter 9, frame The opening of the fluidized air control damper 12, the opening of the switching damper 15 </ b> A, and the opening of the multistage combustion air control damper 13 depend on which of the plurality of preset areas each output value of the detector 10 belongs to. Is set by the discrimination device.
[0018]
In addition, during the fluidized bed combustion, if the input amount of waste increases exceeding both the preset increase rate and the increase amount, the extra combustion is selected. When the vertical combustion is selected, the switching damper 15A is opened, the multistage combustion air control damper 13 is opened, air is supplied to the multistage combustion air nozzle 14, and the switching damper 15B is closed. As a result, the flow of the fluidized medium is stopped, and the dust is placed on the stationary fluidized medium by the air supplied through the multistage combustion air nozzle 14 and incinerated in a combustion state (a state where it does not flow). For example, when the waste supply amount temporarily increases beyond the preset rate of increase and the increase amount, the waste combustion is performed in such cases. As a result, the rapid progress of combustion and the generation of harmful gases can be prevented. Occurrence combustion deals with a case where the amount of waste input suddenly increases or a case where dust is gathered up and put in at once, and does not continue for a long time. If the amount of waste supply continues to exceed the preset value, the duster will reduce the supply amount, or fluidized air and / or secondary combustion air (air supplied from the multi-stage combustion air nozzle) Therefore, it is not necessary to select the long combustion for a long time, and the continuous combustion time may be several seconds to several minutes, at most about 10 minutes or less. The length of this time is set by a timer (not shown) built in the discrimination device 11.
[0019]
FIG. 2 shows an example of a control procedure when fluidized bed combustion and vertical combustion are switched.
[0020]
In the embodiment shown in FIG. 1, the fluidizing air supply duct 21 is provided with an annular fluidizing air header 25, and each fluidizing air nozzle 24 is connected to the fluidizing air header 25 with a fluidizing air header pipe 26. Connected through. Each fluidized valve in the air header pipe 26 is provided, if so adjusted based the opening of the stop valve on the output of the discriminating device 11, a portion of the baked却物causes the fluidized bed combustion, the other part Then, you can make it burn. This method is effective in the case where there is a difference in the properties of the waste to be charged, and the waste having a specific property is always deposited at a specific location in the furnace.
[0021]
【The invention's effect】
According to the present invention, it is possible to select a combustion mode suitable for the input amount of dust and the combustion state (combustion of either fluidized bed combustion, vertical combustion, or a combination of both), and the fluctuations in the amount of supplied dust and the amount of generated heat are large. Generation of harmful gases such as CO, NOX, and SOX generated during incineration of municipal waste is reduced.
[Brief description of the drawings]
FIG. 1 is a conceptual diagram of an incineration facility showing an embodiment of the present invention.
FIG. 2 is a procedure diagram showing an embodiment of a method for controlling an incinerator according to the present invention.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Dust supply sensor 2 Arithmetic unit 3 In-layer thermometer 4 In-furnace pressure gauge 5 In-furnace thermometer 6 Oxygen concentration meter 7 Nitrogen oxide concentration meter 8 Sulfur oxide concentration meter 9 Carbon monoxide concentration meter 10 Frame detector 11 Discriminator 12 Fluidized Air Control Damper 13 Multistage Combustion Air Control Damper 14 Multistage Combustion Air Nozzle 15A, 15B Switching Damper 16 Dust Feeder 17 Input Chute 18 Incinerator Body 19 Blower 20 Blower Discharge Duct 21 Fluidized Air Supply Duct 22 Multistage Combustion Air Supply Duct 23 Exhaust duct 24 Fluidized air nozzle 25 Fluidized air header 26 Fluidized air header piping

Claims (5)

流動層には流動化空気を供給し、前記流動層の上方には燃焼用二次空気を供給し、燃焼状態を示す状態量と炉内に投入される焼却物の投入量とを検出して、その検出結果に基づいて前記流動化空気と前記燃焼用二次空気の供給を制御して前記焼却物を燃焼する流動床式焼却炉の燃焼方法において、前記焼却物の投入量の増加率と増加量との双方が予め設定された値よりも大きいとき、前記流動化空気の供給を制御して前記流動層の流動を停止させ、前記流動層燃焼からおき燃焼に切り替えることを特徴とする流動床式焼却炉の燃焼方法。 Fluidized air is supplied to the fluidized bed, and secondary air for combustion is supplied to the upper part of the fluidized bed to detect the state quantity indicating the combustion state and the amount of incinerated material to be charged into the furnace. In the combustion method of the fluidized bed incinerator for controlling the supply of the fluidized air and the secondary air for combustion based on the detection result to burn the incinerator, the rate of increase in the input amount of the incinerator When both the increase amount and the preset value are larger than a preset value, the flow of the fluidized bed is stopped by controlling the supply of the fluidized air, and the flow is switched from the fluidized bed combustion to the combustion. Combustion method for floor type incinerator. 前記流動層の流動を停止させる期間が10分を超えないことを特徴とする請求項に記載の流動床式焼却炉の燃焼方法。The combustion method for a fluidized bed incinerator according to claim 1 , wherein a period for stopping the flow of the fluidized bed does not exceed 10 minutes. 流動層には流動化空気ダクトから流動化空気ヘッダを介して流動化空気を供給し、前記流動層の上方には燃焼用二次空気を供給し、燃焼状態を示す状態量と炉内に投入される焼却物の投入量とを検出して、その検出結果に基づいて前記流動化空気と前記燃焼用二次空気の供給を制御して前記焼却物を燃焼する流動床式焼却炉の燃焼方法において、前記流動層に前記流動化空気を供給する複数の流動化空気ノズルは、前記流動化空気ヘッダに接続される複数の流動化空気配管に設けられ、前記検出結果に基づいて、前記流動化空気配管に設けられる止め弁の開度を調節して、前記焼却物の一部は流動床燃焼させ、他の部分はおき燃焼させることを特徴とする流動床式焼却炉の燃焼方法 Fluidized air is supplied to the fluidized bed from the fluidized air duct through the fluidized air header, and the secondary air for combustion is supplied above the fluidized bed, and the state quantity indicating the combustion state and the state is introduced into the furnace. Of a fluidized-bed incinerator that detects the amount of incinerated material to be burned and controls the supply of the fluidized air and the secondary air for combustion based on the detection result to burn the incinerated material. A plurality of fluidized air nozzles for supplying the fluidized air to the fluidized bed are provided in a plurality of fluidized air pipes connected to the fluidized air header, and based on the detection result, the fluidized air A combustion method of a fluidized bed incinerator characterized by adjusting a degree of opening of a stop valve provided in an air pipe so that a part of the incinerated product is subjected to fluidized bed combustion and the other part is placed and combusted . 流動層に流動媒体を流動化させる空気を供給する流動化空気供給ダクトと、流動層に燃焼用二次空気を供給する燃焼用二次空気ダクトと、焼却炉に投入シュートを介して焼却物を投入する給じん機と、前記投入シュートに設置されて焼却物の投入量を検出する投入量検出手段と、前記焼却物の燃焼状態を示す複数の状態量を検出する状態量検出手段と、前記投入量検出手段の出力及び前記状態量検出手段の出力を入力して前記流動化空気供給ダクト及び前記燃焼用二次空気ダクトに供給する空気量を制御する制御手段と、を有してなる流動床式焼却炉において、前記制御手段は、前記投入量検出手段の出力の変化率及び変化量の双方が、予め設定された値よりも大きいとき、前記流動化空気供給ダクトに設けたダンパを閉とすることを特徴とする流動床式焼却炉。Through a fluidizing air supply duct for supplying air to fluidize the fluidized medium in the fluidized bed, and the secondary air duct for combustion to supply the combustion secondary air above side of the fluidized bed, the chute into the incinerator state quantity detecting multiple state quantity indicating a paper dust machine for introducing material to be incinerated, and input amount detecting means for detecting an input amount before Symbol incinerated is placed in chute, the combustion state of the incinerated Te a detection means, and control means for controlling the output and the amount of air supplied to the fluidizing air supply duct and secondary air duct for the combustion output and input of the state quantity detecting means of the input amount detecting means, In the fluidized bed incinerator, the control means has the fluidized air supply duct when both the rate of change and the amount of change of the output of the input amount detecting means are larger than preset values. Close the damper provided on Fluidized bed incinerator, characterized. 前記状態量検出手段は、少なくとも、流動層内温度、炉内圧力、炉内温度、炉出口酸素濃度、NOの発生量、SOの発生量、COの発生量、及び火炎の輝度検出手段であることを特徴とする請求項4に記載の流動床式焼却炉。 The state quantity detection means detects at least the fluidized bed temperature, furnace pressure, furnace temperature, furnace outlet oxygen concentration, NO x generation quantity, SO x generation quantity, CO generation quantity, and flame brightness . The fluidized bed incinerator according to claim 4, wherein the fluidized bed incinerator is a means .
JP30066694A 1994-12-05 1994-12-05 Fluidized bed incinerator and its combustion method Expired - Fee Related JP3619940B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP30066694A JP3619940B2 (en) 1994-12-05 1994-12-05 Fluidized bed incinerator and its combustion method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP30066694A JP3619940B2 (en) 1994-12-05 1994-12-05 Fluidized bed incinerator and its combustion method

Publications (2)

Publication Number Publication Date
JPH08159414A JPH08159414A (en) 1996-06-21
JP3619940B2 true JP3619940B2 (en) 2005-02-16

Family

ID=17887615

Family Applications (1)

Application Number Title Priority Date Filing Date
JP30066694A Expired - Fee Related JP3619940B2 (en) 1994-12-05 1994-12-05 Fluidized bed incinerator and its combustion method

Country Status (1)

Country Link
JP (1) JP3619940B2 (en)

Family Cites Families (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS597815A (en) * 1982-07-07 1984-01-17 Hitachi Ltd Controlling device to reduce sox
JPH01291010A (en) * 1988-05-16 1989-11-22 Ishikawajima Harima Heavy Ind Co Ltd Combustion control method for fluidized bed incinerator
JPH0694929B2 (en) * 1989-11-06 1994-11-24 川崎重工業株式会社 Combustion control method for fluidized bed furnace
JPH03168516A (en) * 1989-11-28 1991-07-22 Nkk Corp Combustion control method for fluidized bed incinerator
JPH0490409A (en) * 1990-07-31 1992-03-24 Kobe Steel Ltd Method and device for controlling combustion in fluidized bed type incinerator
JP3021062B2 (en) * 1991-02-27 2000-03-15 三井造船株式会社 Combustion control method for waste incinerator
JP2972454B2 (en) * 1992-08-27 1999-11-08 川崎重工業株式会社 Fluid bed furnace combustion control method and apparatus
JP2656879B2 (en) * 1992-10-05 1997-09-24 株式会社神戸製鋼所 Automatic combustion control method for incinerator
JPH06332501A (en) * 1993-05-24 1994-12-02 Ishikawajima Harima Heavy Ind Co Ltd Feedback control device and incinerator using the control device

Also Published As

Publication number Publication date
JPH08159414A (en) 1996-06-21

Similar Documents

Publication Publication Date Title
US4838183A (en) Apparatus and method for incinerating heterogeneous materials
CA1302168C (en) Automatic combustion control for a rotary combustor
WO1988008504A1 (en) Combustion control method for fluidized bed incinerator
JPS59180212A (en) Combustion controller in refuse incinerator
JP2955431B2 (en) Incinerator combustion control device
GB2272752A (en) Incinerator
JP3619940B2 (en) Fluidized bed incinerator and its combustion method
JP2008064361A (en) Stoker-type incinerator and combustion control method therefor
JPH03244912A (en) Controlling method for combustion in fluidized bed type incinerator
WO1991014915A1 (en) Method of controlling combustion in fluidized bed incinerator
JP3819458B2 (en) Waste supply measuring device and combustion control method using the same
JPS59129316A (en) Dust feeding control device in refuse incinerater
JP3856589B2 (en) Combustion equipment
JPH1061917A (en) Fluidized bed type incinerator and combustion control method for the same
JPS5986814A (en) Control method for automatic combustion of refuse incinerator
JP3356946B2 (en) Garbage quality determination method and apparatus, and combustion control device for garbage incinerator
JP3843382B2 (en) Combustion control method and apparatus for waste incinerator
JPS58195707A (en) Combustion control method for refuse incinerator
JP3888870B2 (en) Garbage incinerator
JPH01302018A (en) Automatic combustion control method of rotary type incinerator
JP2001227731A (en) Control method of fluidized bed furnace and its device
JPH03168516A (en) Combustion control method for fluidized bed incinerator
JPH03230007A (en) Interruption detecting method of supply of items to be incinerated in fluidized-bed incinerator
JP2002195534A (en) Method and system for controlling combustion of refuse incinerator
JPS6136611A (en) Combustion control of refuse incinerator

Legal Events

Date Code Title Description
TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20041012

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20041102

R150 Certificate of patent or registration of utility model

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20081126

Year of fee payment: 4

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20091126

Year of fee payment: 5

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20101126

Year of fee payment: 6

LAPS Cancellation because of no payment of annual fees