JP2733201B2 - Garbage incineration equipment - Google Patents

Garbage incineration equipment

Info

Publication number
JP2733201B2
JP2733201B2 JP6257893A JP25789394A JP2733201B2 JP 2733201 B2 JP2733201 B2 JP 2733201B2 JP 6257893 A JP6257893 A JP 6257893A JP 25789394 A JP25789394 A JP 25789394A JP 2733201 B2 JP2733201 B2 JP 2733201B2
Authority
JP
Japan
Prior art keywords
secondary combustion
combustion gas
gas supply
zone
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.)
Expired - Lifetime
Application number
JP6257893A
Other languages
Japanese (ja)
Other versions
JPH08121724A (en
Inventor
正彦 渡辺
信幸 西口
正道 日野
智 黒石
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.)
Kubota Corp
Original Assignee
Kubota Corp
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 Kubota Corp filed Critical Kubota Corp
Priority to JP6257893A priority Critical patent/JP2733201B2/en
Publication of JPH08121724A publication Critical patent/JPH08121724A/en
Application granted granted Critical
Publication of JP2733201B2 publication Critical patent/JP2733201B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/12Heat utilisation in combustion or incineration of waste

Landscapes

  • Incineration Of Waste (AREA)
  • Engine Equipment That Uses Special Cycles (AREA)

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、ゴミを焼却するストー
カ式の焼却処理帯を備えた一次燃焼領域の上方空間に煙
道を形成して二次燃焼領域とし、前記煙道の下流側に排
ガスから熱回収する廃熱ボイラを備えたゴミ焼却炉と、
前記廃熱ボイラからの発生蒸気を過熱する燃焼式過熱器
と、前記燃焼式過熱器による過熱蒸気で発電する蒸気タ
ービンを備えた発電装置とからなり、前記燃焼式過熱器
からの燃焼排ガスを、酸素濃度を低くした状態で前記二
次燃焼領域に導く二次燃焼ガス供給路を設けてあるゴミ
焼却装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a secondary combustion zone in which a flue is formed in a space above a primary combustion zone having a stoker type incineration zone for incinerating garbage, and is provided downstream of the flue. A waste incinerator equipped with a waste heat boiler that recovers heat from exhaust gas,
Combustion superheater that superheats the steam generated from the waste heat boiler, and a power generation device including a steam turbine that generates power using superheated steam by the combustion superheater, the combustion exhaust gas from the combustion superheater, The present invention relates to a refuse incineration device provided with a secondary combustion gas supply passage that leads the oxygen concentration to the secondary combustion region in a state where the oxygen concentration is low.

【0002】[0002]

【従来の技術】この種のゴミ焼却炉は、図4に示すよう
に、二次燃焼領域におけるガス温度の低下を防止して完
全燃焼を促進し、一酸化炭素や一酸化炭素の発生量と正
の相関があるダイオキシンの発生を抑制すべく、煙道4
の上流側で、且つ、焼却処理帯3の上流側に、二次燃焼
ガスを噴射する二次燃焼ガス供給機構15を設けて、燃
焼式過熱器8からの高温の燃焼排ガスを、酸素濃度を低
くした状態で二次燃焼領域に導くべく、前記二次燃焼ガ
ス供給機構15に供給する前記二次燃焼ガス供給路14
を設けていた。
2. Description of the Related Art As shown in FIG. 4, this type of refuse incinerator prevents a decrease in gas temperature in a secondary combustion zone, promotes complete combustion, and reduces the amount of generated carbon monoxide and carbon monoxide. To suppress the generation of positively correlated dioxins, the flue 4
A secondary combustion gas supply mechanism 15 for injecting secondary combustion gas is provided upstream of the incineration zone 3 and upstream of the incineration zone 3. The high-temperature combustion exhaust gas from the combustion type superheater 8 is used to reduce the oxygen concentration. The secondary combustion gas supply path 14 that supplies the secondary combustion gas supply mechanism 15 to the secondary combustion gas supply mechanism 15 so as to guide the secondary combustion gas to the secondary combustion area in a lowered state.
Was provided.

【0003】[0003]

【発明が解決しようとする課題】しかし、上述した従来
のゴミ焼却炉では、二次燃焼ガス供給機構15を、煙道
4の上流側で、且つ、焼却処理帯3の上流側に設けてい
たために、そのような位置から噴入された燃焼用のガス
では、焼却処理帯3の上流側を構成する乾燥帯Aにおい
て発生した可燃性ガスを有効に燃焼させ得るものではな
いという欠点があった。
However, in the above-mentioned conventional refuse incinerator, the secondary combustion gas supply mechanism 15 is provided upstream of the flue 4 and upstream of the incineration zone 3. In addition, the combustion gas injected from such a position has a disadvantage that the combustible gas generated in the drying zone A constituting the upstream side of the incineration zone 3 cannot be effectively burned. .

【0004】つまり、水流による流れの可視化実験によ
れば、乾燥帯Aで発生した可燃性ガスはそのまま上昇し
て上方の壁面4bに沿って層をなして煙道4へ流れ、焼
却処理帯3の下流側を構成する燃焼帯Bでの燃焼ガス流
と均一に混合されることなく層をなして煙道4に導かれ
ることが判明したため、従来の二次燃焼ガス供給機構1
5により高速で噴入される燃焼用ガスでは、その様な可
燃性ガス流を突き抜けて燃焼帯Bの上方空間に到ること
となり燃焼に有効に寄与するものではなかったという問
題点があった。
That is, according to the visualization experiment of the flow caused by the water flow, the combustible gas generated in the drying zone A rises as it is, flows in a layer along the upper wall surface 4b to the flue 4, and is incinerated in the incineration zone 3. It has been found that the fuel gas is not uniformly mixed with the combustion gas flow in the combustion zone B constituting the downstream side of the fuel cell and is guided to the flue 4 in a layer.
5, the combustion gas injected at a higher speed penetrates such a flammable gas flow and reaches the space above the combustion zone B, and thus does not contribute to combustion effectively. .

【0005】また、煙道4の入口断面における酸素濃度
分布を求めると、図2(イ)に示すように、乾燥帯A側
では約8%、燃焼帯B側では約15%という大きな濃度
勾配があり、このような濃度勾配を維持したままで煙道
へ流れると、煙道4の乾燥帯A側では酸素不足による不
完全燃焼を起こし、逆に煙道4の燃焼帯B側では窒素酸
化物が発生するおそれがあり、そのような問題を回避す
るためには、高価な排ガス処理装置等をさらに設ける必
要があり、結局、設備費が嵩むという問題点があった。
[0005] Further, when the oxygen concentration distribution at the inlet cross section of the flue 4 is calculated, as shown in Fig. 2 (a), a large concentration gradient of about 8% on the drying zone A side and about 15% on the combustion zone B side. When flowing into the flue while maintaining such a concentration gradient, incomplete combustion occurs due to lack of oxygen in the drying zone A of the flue 4 and, on the contrary, nitrogen oxidation occurs in the combustion zone B of the flue 4. In order to avoid such a problem, it is necessary to further provide an expensive exhaust gas treatment device and the like, and there has been a problem that the equipment cost is eventually increased.

【0006】一方、従来の二次燃焼ガス供給機構15か
らの供給ガス圧を低下すれば、可燃性ガス流を突き抜け
るという不都合は解消されるものの、乾燥帯側を流れる
可燃性ガスの流速に応じた適切な二次空気量が常に供給
できるものではなく、煙道4の燃焼帯B側での窒素酸化
物の発生を低減させるということができない。
On the other hand, if the supply gas pressure from the conventional secondary combustion gas supply mechanism 15 is reduced, the inconvenience of penetrating the combustible gas flow is eliminated, but it is determined according to the flow rate of the combustible gas flowing through the drying zone. Further, an appropriate amount of secondary air cannot always be supplied, and the generation of nitrogen oxides on the combustion zone B side of the flue 4 cannot be reduced.

【0007】本発明の目的は、上述の問題点に鑑みて、
二次燃焼領域において、温度低下を引き起こすことのな
い状態で燃焼ガスを均一拡散して、完全燃焼を促進しな
がら同時に窒素酸化物の発生を低減させることが可能な
ゴミ焼却装置を提供する点にある。
[0007] The object of the present invention, in view of the problems described above,
In the point of providing a refuse incinerator capable of uniformly diffusing a combustion gas without causing a temperature drop in a secondary combustion region to promote complete combustion and simultaneously reduce generation of nitrogen oxides. is there.

【0008】[0008]

【課題を解決するための手段】この目的を達成するため
本発明によるゴミ焼却炉の特徴構成は、煙道の上流側
で、且つ、焼却処理帯の下流側に、前記焼却処理帯の下
流側から上流側に向けて二次燃焼ガスを噴射する二次燃
焼ガス供給機構を設けて、二次燃焼ガス供給路を前記二
次燃焼ガス供給機構に接続してある点にある。
In order to achieve this object, a refuse incinerator according to the present invention is characterized in that the refuse incinerator is arranged upstream of the flue and downstream of the incineration zone, downstream of the incineration zone. And a secondary combustion gas supply mechanism for injecting secondary combustion gas from upstream to upstream is provided, and a secondary combustion gas supply path is connected to the secondary combustion gas supply mechanism.

【0009】上述の構成において、ゴミ焼却炉の排ガス
中に含まれる酸素濃度を検出するガスセンサを設けて、
前記ガスセンサによる検出酸素濃度が所定の目標値に維
持されるように、前記二次燃焼ガス供給機構からの二次
燃焼ガスの噴射量を調節する二次燃焼ガス供給量調節機
構を設けてあることが好ましい。
In the above configuration, a gas sensor for detecting the concentration of oxygen contained in the exhaust gas from the refuse incinerator is provided.
A secondary combustion gas supply amount adjusting mechanism for adjusting an injection amount of the secondary combustion gas from the secondary combustion gas supply mechanism is provided so that the oxygen concentration detected by the gas sensor is maintained at a predetermined target value. Is preferred.

【0010】上述の構成において、ゴミ焼却炉の排ガス
温度を検出する温度センサを設けて、前記温度センサに
よる検出排ガス温度が所定の目標値に維持されるよう
に、前記二次燃焼ガス供給機構からの二次燃焼ガスの噴
射量を調節する二次燃焼ガス供給量調節機構を設けてあ
ることが好ましい。
In the above configuration, a temperature sensor for detecting the temperature of the exhaust gas from the refuse incinerator is provided, and the temperature of the exhaust gas detected by the temperature sensor is maintained at a predetermined target value from the secondary combustion gas supply mechanism. It is preferable to provide a secondary combustion gas supply amount adjustment mechanism for adjusting the secondary combustion gas injection amount.

【0011】[0011]

【作用】二次燃焼ガス供給機構を、煙道の上流側で、且
つ、焼却処理帯の下流側に、前記焼却処理帯の下流側か
ら上流側に向けて二次燃焼ガスを噴射するように設けて
あるので、そのような二次燃焼ガス供給機構から噴射さ
れた二次燃焼ガスは、煙道の燃焼帯側(焼却処理帯の下
流側)に流入する酸素濃度の高い燃焼ガスを巻き込みな
がら、煙道の乾燥帯側(焼却処理帯の上流側)に流入す
る酸素濃度の低い未燃ガスに向かって流れる結果、煙道
での燃焼ガスの均一拡散が促進されるのである。このと
き、一次燃焼領域で生じた燃焼ガスには二次燃焼に必要
とされる量の酸素が既に含まれており、二次燃焼領域で
二次燃焼ガスとして通常の空気を供給する場合には、酸
素過多となり却って窒素酸化物の発生量が上昇するおそ
れがあるので、燃焼式過熱器からの高温の燃焼排ガスを
酸素濃度を低くした状態で供給することで過剰酸素供給
による窒素酸化物の発生を防止するとともに、二次燃焼
領域での燃焼温度を高温に維持して二次燃焼を促進する
のである。
The secondary combustion gas supply mechanism is configured to inject secondary combustion gas upstream of the flue and downstream of the incineration zone from downstream to upstream of the incineration zone. Since the secondary combustion gas is injected from the secondary combustion gas supply mechanism, the combustion gas with a high oxygen concentration flowing into the combustion zone side of the flue (downstream of the incineration treatment zone) is entrained. As a result, the uniform diffusion of the combustion gas in the flue is promoted as a result of the flow toward the unburned gas having a low oxygen concentration flowing into the drying zone of the flue (upstream of the incineration zone). At this time, the combustion gas generated in the primary combustion region already contains an amount of oxygen required for the secondary combustion, and when supplying normal air as the secondary combustion gas in the secondary combustion region, Since there is a possibility that the amount of nitrogen oxides may increase due to excessive oxygen, the high-temperature combustion exhaust gas from the combustion type superheater is supplied at a low oxygen concentration to generate nitrogen oxides due to excess oxygen supply. And promotes secondary combustion by maintaining the combustion temperature in the secondary combustion region at a high temperature.

【0012】一般に一酸化炭素の完全燃焼化のために
は、十分な酸素量、燃焼時間、燃焼温度が必要とされる
が、この中で酸素量に着目すると、焼却炉においては、
最終的に排ガス中の残留酸素濃度が約8%確保されてお
れば十分であることが知られている。そこで、ゴミ焼却
炉の排ガス中に含まれる酸素濃度を検出するガスセンサ
を設けて、二次燃焼ガス供給量調節機構により、前記ガ
スセンサによる検出酸素濃度が所定の目標値、例えば8
%に維持されるように、前記二次燃焼ガス供給機構から
の二次燃焼ガスの噴射量を調節することにより、二次燃
焼領域での燃焼条件を良好に保つのである。
In general, for complete combustion of carbon monoxide, a sufficient amount of oxygen, a burning time and a burning temperature are required.
It is known that it is sufficient if the residual oxygen concentration in the exhaust gas is about 8%. Therefore, a gas sensor for detecting the concentration of oxygen contained in the exhaust gas of the refuse incinerator is provided, and the oxygen concentration detected by the gas sensor is adjusted to a predetermined target value, for example, 8 by the secondary combustion gas supply amount adjusting mechanism.
% By adjusting the injection amount of the secondary combustion gas from the secondary combustion gas supply mechanism so as to maintain the combustion condition in the secondary combustion region.

【0013】さらに、燃焼温度に着目すると、二次燃焼
領域で一酸化炭素の完全燃焼化を促進するためには、該
領域を少なくとも一酸化炭素の燃焼温度である約650
℃よりも高温に維持する必要がある。そこで、ゴミ焼却
炉の排ガス温度を検出する温度センサを設けて、二次燃
焼ガス供給量調節機構により、前記温度センサによる検
出排ガス温度が所定の目標値、例えば850℃以上に維
持されるように、前記二次燃焼ガス供給機構からの二次
燃焼ガスの噴射量を調節することにより二次燃焼領域で
の燃焼条件を良好に保つのである。
Further, focusing on the combustion temperature, in order to promote complete combustion of carbon monoxide in the secondary combustion region, the region must be heated to at least about 650 which is the combustion temperature of carbon monoxide.
It must be maintained above ℃. Therefore, a temperature sensor for detecting the exhaust gas temperature of the refuse incinerator is provided, and the secondary combustion gas supply amount adjusting mechanism is configured to maintain the exhaust gas temperature detected by the temperature sensor at a predetermined target value, for example, 850 ° C. or higher. By adjusting the injection amount of the secondary combustion gas from the secondary combustion gas supply mechanism, the combustion conditions in the secondary combustion region can be kept good.

【0014】[0014]

【発明の効果】本発明によれば、二次燃焼領域におい
て、温度低下を引き起こすことのない状態で燃焼ガスを
均一拡散して、完全燃焼を促進しながら同時に窒素酸化
物の発生を低減させることが可能なゴミ焼却装置を提供
することができるようになった。
According to the present invention, in the secondary combustion region, the combustion gas is uniformly diffused without causing a temperature decrease, thereby promoting complete combustion and simultaneously reducing the generation of nitrogen oxides. It has become possible to provide a garbage incinerator capable of performing the above.

【0015】[0015]

【実施例】以下に実施例を説明する。図1に示すよう
に、ゴミ焼却装置は、ゴミを焼却するストーカ式の焼却
処理帯3を備えた一次燃焼領域R1の上方空間に煙道4
を形成して二次燃焼領域R2とし、前記煙道4の下流側
に排ガスから熱回収する廃熱ボイラ7を備えたゴミ焼却
炉1と、前記廃熱ボイラ7からの発生蒸気を過熱する燃
焼式過熱器8と、前記燃焼式過熱器8による過熱蒸気で
発電する蒸気タービン9aを備えた発電装置9とからな
る。
Embodiments will be described below. As shown in FIG. 1, the refuse incineration apparatus includes a flue 4 in a space above a primary combustion region R1 provided with a stoker-type incineration treatment zone 3 for incinerating refuse.
To form a secondary combustion region R2, a refuse incinerator 1 provided with a waste heat boiler 7 for recovering heat from exhaust gas on the downstream side of the flue 4 and a combustion for heating steam generated from the waste heat boiler 7 It comprises a superheater 8 and a power generation device 9 having a steam turbine 9a that generates power using superheated steam generated by the combustion superheater 8.

【0016】前記ゴミ焼却炉1について詳述すると、ホ
ッパ2に投入されたゴミが油圧駆動式のプッシャ2aに
より炉内に投入され、前記焼却処理帯3で一次燃焼され
る。前記焼却処理帯3は、火格子3aの往復運動により
ゴミを搬送処理するストーカ機構を備え、上流側から順
にゴミを乾燥処理する乾燥帯Aと、乾燥されたゴミを燃
焼する燃焼帯Bと、燃焼したゴミを完全に灰化する後燃
焼帯Cを階段状に縦続設置して構成してあり、各処理帯
の下方に風箱6c,6d,6eを設けて、送風機6a、
送風路6bを介して一次燃焼用の空気を供給する一次燃
焼空気供給機構6を設けてある。前記煙道4は、前記乾
燥帯Aから燃焼帯Bの上方空間に断面が方形に形成して
あり、乾燥帯Aで生じる可燃性ガス(還元性ガス)と燃
焼帯Bで生じるNOxを含む燃焼ガスを混合してNOx
を還元するとともに、一酸化炭素を完全燃焼させる二次
燃焼領域R2となる。
The refuse incinerator 1 will be described in detail. The refuse introduced into the hopper 2 is introduced into the furnace by a hydraulically driven pusher 2a, and is primarily burned in the incineration treatment zone 3. The incineration zone 3 is provided with a stoker mechanism for transporting dust by reciprocating motion of the grate 3a, and a drying zone A for drying the dust in order from the upstream side, and a combustion zone B for burning the dried dust. After the burned refuse is completely incinerated, the combustion zone C is cascade-installed in a step-like manner, and wind boxes 6c, 6d, 6e are provided below each processing zone to provide a blower 6a,
A primary combustion air supply mechanism 6 for supplying air for primary combustion via an air passage 6b is provided. The flue 4 has a rectangular cross section in the space above the drying zone A and above the combustion zone B, and a combustion containing a combustible gas (reducing gas) generated in the drying zone A and NOx generated in the combustion zone B. NOx by mixing gas
And a secondary combustion region R2 in which carbon monoxide is completely burned.

【0017】廃熱ボイラ7で熱交換された排ガスは、バ
グフィルターや洗煙装置等の排ガス処理装置10により
有害物質やばいじんが除去された後に煙突11から排気
される。
Exhaust gas heat-exchanged in the waste heat boiler 7 is exhausted from a chimney 11 after harmful substances and soot and dust are removed by an exhaust gas treatment device 10 such as a bag filter or a smoke washer.

【0018】前記発電装置9は、蒸気タービン9aとこ
れによって駆動される発電機9bとでなり、前記廃熱ボ
イラ7で発生した約310℃の蒸気を、蒸気供給路12
を介して前記燃焼式過熱器8に供給し、過熱用バーナー
8aによる燃焼熱で約500℃に昇温した後に、蒸気供
給路13を介して前記蒸気タービン9aに供給する。つ
まり、前記焼却炉1での排ガスには塩化水素等の腐食性
ガスが発生するために、高温腐食防止の観点から約31
0℃以上に過熱できないために、外部に過熱器を設けて
過熱し、発電効率を高めるものである。
The power generator 9 comprises a steam turbine 9a and a generator 9b driven by the steam turbine 9a. The steam at about 310.degree.
The heat is supplied to the combustion type superheater 8 through the heater, the temperature is increased to about 500 ° C. by the heat of combustion by the superheating burner 8a, and then supplied to the steam turbine 9a through the steam supply path 13. That is, since corrosive gas such as hydrogen chloride is generated in the exhaust gas from the incinerator 1, about 31%
Since it is not possible to overheat to 0 ° C. or more, an external superheater is provided to overheat and enhance the power generation efficiency.

【0019】前記過熱用バーナー8aへの供給空気量を
必要空気量より増した状態で燃焼し、含有酸素濃度が約
3.5%、約400℃の高温の燃焼排ガスを、二次燃焼
ガス供給路14を介して前記二次燃焼領域R2に導くよ
うに構成してある。
The combustion is performed in a state where the amount of air supplied to the superheating burner 8a is increased from the required amount of air, and high-temperature combustion exhaust gas having an oxygen content of about 3.5% and about 400 ° C. is supplied to the secondary combustion gas supply. It is configured to be guided to the secondary combustion region R2 via the path 14.

【0020】詳述すると、前記煙道4の上流側で、且
つ、前記焼却処理帯3の下流側の壁面4aに、前記焼却
処理帯3の下流側(燃焼帯B側)から上流側(乾燥帯A
側)に向けて、さらに詳しくは、乾燥帯Aと燃焼帯Bと
のなす段差部に向けて、二次燃焼ガスを噴射する複数の
ノズル15aでなる二次燃焼ガス供給機構15を設け
て、前記二次燃焼ガス供給路14を前記二次燃焼ガス供
給機構15にダンパ機構16aを介して接続してある。
More specifically, on the wall 4a on the upstream side of the flue 4 and on the downstream side of the incineration zone 3, the downstream side (combustion zone B side) of the incineration zone 3 upstream (drying). Obi A
Side), more specifically, a secondary combustion gas supply mechanism 15 including a plurality of nozzles 15a for injecting secondary combustion gas is provided toward a step formed by the drying zone A and the combustion zone B, The secondary combustion gas supply path 14 is connected to the secondary combustion gas supply mechanism 15 via a damper mechanism 16a.

【0021】前記排ガス処理装置10の下流側には、前
記ゴミ焼却炉1の排ガス中に含まれる酸素濃度を検出す
るガスセンサS1を設けて、前記ガスセンサS1による
検出酸素濃度が目標値である約8%以上に維持されるよ
うに、前記二次燃焼ガス供給機構15からの二次燃焼ガ
スの噴射量を調節する二次燃焼ガス供給量調節機構16
を設けてある。
A gas sensor S1 for detecting the concentration of oxygen contained in the exhaust gas from the refuse incinerator 1 is provided on the downstream side of the exhaust gas treatment device 10, and the oxygen concentration detected by the gas sensor S1 is about 8 which is a target value. % Of the secondary combustion gas supplied from the secondary combustion gas supply mechanism 15 so as to be maintained at or above the secondary combustion gas supply amount adjustment mechanism 16.
Is provided.

【0022】即ち、前記二次燃焼ガス供給量調節機構1
6は、前記ダンパ機構16aと、前記ガスセンサS1か
らの信号を入力し、前記ダンパ機構16aの開度を調節
する制御装置16bとで構成される。
That is, the secondary combustion gas supply amount adjusting mechanism 1
Reference numeral 6 includes the damper mechanism 16a and a control device 16b which receives a signal from the gas sensor S1 and adjusts the opening of the damper mechanism 16a.

【0023】以下に別実施例を説明する。図3に示すよ
うに、前記二次燃焼領域R2に、排ガス温度を検出する
温度センサS2を設けて前記温度センサS2による検出
排ガス温度が所定の目標値、例えば800℃から950
℃に維持されるように、前記二次燃焼ガス供給機構15
からの二次燃焼ガスの噴射量お調節する二次燃焼ガス供
給量調節機構16を設けてもよい。即ち、前記二次燃焼
ガス供給量調節機構16は前記ダンパ機構16aと、前
記温度センサS2からの信号を入力し、前記ダンパ機構
16aの開度を調節する制御装置16cとで構成され、
検出排ガス温度が目標値より低い場合には前記ダンパ機
構16aの開度を小に調節して過剰供給による冷却で温
度が低下することを防止し、目標値より高い場合には、
前記ダンパ機構16aの開度を大に調節して二次燃焼を
促進するのである。尚、目標値は例示であり、この値に
限定するものではない。
Another embodiment will be described below. As shown in FIG. 3, a temperature sensor S2 for detecting exhaust gas temperature is provided in the secondary combustion region R2 so that the exhaust gas temperature detected by the temperature sensor S2 is set to a predetermined target value, for example, 800 to 950.
℃, the secondary combustion gas supply mechanism 15
A secondary combustion gas supply amount adjusting mechanism 16 for adjusting the injection amount of the secondary combustion gas from the engine may be provided. That is, the secondary combustion gas supply amount adjustment mechanism 16 includes the damper mechanism 16a and a control device 16c that receives a signal from the temperature sensor S2 and adjusts the opening of the damper mechanism 16a.
When the detected exhaust gas temperature is lower than the target value, the opening degree of the damper mechanism 16a is adjusted to a small value to prevent the temperature from being lowered by cooling due to excessive supply, and when the detected exhaust gas temperature is higher than the target value,
The degree of opening of the damper mechanism 16a is largely adjusted to promote secondary combustion. Note that the target value is an example, and is not limited to this value.

【0024】さらに、二次燃焼ガス供給量調節機構16
としては、上述のガスセンサS1と温度センサS2を備
え、双方のセンサによる検出入力により前記ダンパ機構
16aの開度を調節するものであってもよい。
Further, the secondary combustion gas supply amount adjusting mechanism 16
May be provided with the above-mentioned gas sensor S1 and temperature sensor S2, and the opening degree of the damper mechanism 16a is adjusted by the detection input of both sensors.

【0025】尚、特許請求の範囲の項に図面との対照を
便利にするために符号を記すが、該記入により本発明は
添付図面の構成に限定されるものではない。
In the claims, reference numerals are provided for convenience of comparison with the drawings, but the present invention is not limited to the configuration shown in the attached drawings.

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

【図1】本発明による都市ゴミ焼却装置の実施例を示す
説明図
FIG. 1 is an explanatory view showing an embodiment of a municipal garbage incinerator according to the present invention.

【図2】実験結果の説明図FIG. 2 is an explanatory diagram of an experimental result.

【図3】別実施例を示す都市ゴミ焼却装置の説明図FIG. 3 is an explanatory view of an urban refuse incineration apparatus showing another embodiment.

【図4】従来例を示す都市ゴミ焼却装置の説明図FIG. 4 is an explanatory view of a municipal garbage incinerator showing a conventional example.

【符号の説明】[Explanation of symbols]

1 焼却炉 3 焼却処理帯 4 煙道 7 廃熱ボイラ 8 燃焼式過熱器 9 発電装置 9a 蒸気タービン 14 二次燃焼ガス供給路 15 二次燃焼ガス供給機構 Reference Signs List 1 incinerator 3 incineration zone 4 flue 7 waste heat boiler 8 combustion superheater 9 power generation device 9a steam turbine 14 secondary combustion gas supply path 15 secondary combustion gas supply mechanism

───────────────────────────────────────────────────── フロントページの続き (72)発明者 黒石 智 兵庫県尼崎市浜1丁目1番1号 株式会 社クボタ 技術開発研究所内 ──────────────────────────────────────────────────の Continuing from the front page (72) Inventor Satoshi Kuroishi 1-1-1 Hama, Amagasaki-shi, Hyogo Pref.

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 ゴミを焼却するストーカ式の焼却処理帯
(3)を備えた一次燃焼領域の上方空間に煙道(4)を
形成して二次燃焼領域とし、前記煙道(4)の下流側に
排ガスから熱回収する廃熱ボイラ(7)を備えたゴミ焼
却炉(1)と、前記廃熱ボイラ(7)からの発生蒸気を
過熱する燃焼式過熱器(8)と、前記燃焼式過熱器
(8)による過熱蒸気で発電する蒸気タービン(9a)
を備えた発電装置(9)とからなり、 前記燃焼式過熱器(8)からの燃焼排ガスを、酸素濃度
を低くした状態で前記二次燃焼領域に導く二次燃焼ガス
供給路(14)を設けてあるゴミ焼却装置であって、 前記煙道(4)の上流側で、且つ、前記焼却処理帯
(3)の下流側に、前記焼却処理帯(3)の下流側から
上流側に向けて二次燃焼ガスを噴射する二次燃焼ガス供
給機構(15)を設けて、前記二次燃焼ガス供給路(1
4)を前記二次燃焼ガス供給機構(15)に接続してあ
るゴミ焼却装置。
A flue (4) is formed in a space above a primary combustion area provided with a stoker-type incineration treatment zone (3) for incinerating garbage to form a secondary combustion area. A refuse incinerator (1) provided with a waste heat boiler (7) for recovering heat from exhaust gas on the downstream side; a combustion type superheater (8) for heating steam generated from the waste heat boiler (7); Steam turbine (9a) that generates power using superheated steam by a superheater (8)
A secondary combustion gas supply passage (14) for guiding the combustion exhaust gas from the combustion type superheater (8) to the secondary combustion region in a state where the oxygen concentration is low. A refuse incineration apparatus provided, wherein the refuse incineration device is provided on the upstream side of the flue (4) and on the downstream side of the incineration zone (3) from the downstream side of the incineration zone (3) to the upstream side. A secondary combustion gas supply mechanism (15) for injecting secondary combustion gas through the secondary combustion gas supply path (1).
4) A garbage incinerator connected to the secondary combustion gas supply mechanism (15).
【請求項2】 前記ゴミ焼却炉(1)の排ガス中に含ま
れる酸素濃度を検出するガスセンサ(S1)を設けて、
前記ガスセンサ(S1)による検出酸素濃度が所定の目
標値に維持されるように、前記二次燃焼ガス供給機構
(15)からの二次燃焼ガスの噴射量を調節する二次燃
焼ガス供給量調節機構(16)を設けてある請求項1記
載のゴミ焼却装置。
2. A gas sensor (S1) for detecting the concentration of oxygen contained in exhaust gas of the refuse incinerator (1),
Secondary combustion gas supply adjustment for adjusting the injection amount of secondary combustion gas from the secondary combustion gas supply mechanism (15) such that the oxygen concentration detected by the gas sensor (S1) is maintained at a predetermined target value. The refuse incinerator according to claim 1, further comprising a mechanism (16).
【請求項3】 前記ゴミ焼却炉(1)の排ガス温度を検
出する温度センサ(S2)を設けて、前記温度センサ
(S2)による検出排ガス温度が所定の目標値に維持さ
れるように、前記二次燃焼ガス供給機構(15)からの
二次燃焼ガスの噴射量を調節する二次燃焼ガス供給量調
節機構(16)を設けてある請求項1又は2記載のゴミ
焼却装置。
3. A temperature sensor (S2) for detecting an exhaust gas temperature of the refuse incinerator (1), wherein the exhaust gas temperature detected by the temperature sensor (S2) is maintained at a predetermined target value. The refuse incinerator according to claim 1 or 2, further comprising a secondary combustion gas supply amount adjusting mechanism (16) for adjusting an injection amount of the secondary combustion gas from the secondary combustion gas supply mechanism (15).
JP6257893A 1994-10-24 1994-10-24 Garbage incineration equipment Expired - Lifetime JP2733201B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6257893A JP2733201B2 (en) 1994-10-24 1994-10-24 Garbage incineration equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6257893A JP2733201B2 (en) 1994-10-24 1994-10-24 Garbage incineration equipment

Publications (2)

Publication Number Publication Date
JPH08121724A JPH08121724A (en) 1996-05-17
JP2733201B2 true JP2733201B2 (en) 1998-03-30

Family

ID=17312657

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6257893A Expired - Lifetime JP2733201B2 (en) 1994-10-24 1994-10-24 Garbage incineration equipment

Country Status (1)

Country Link
JP (1) JP2733201B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
ES2151793B1 (en) * 1997-11-12 2001-07-01 Holter Heinz Professor Dr Sc D PROCEDURE FOR BURNING FOSSIL FUEL AND GARBAGE.
JP6616945B2 (en) * 2014-12-24 2019-12-04 川崎重工業株式会社 Incineration plant

Also Published As

Publication number Publication date
JPH08121724A (en) 1996-05-17

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