JP2002228130A - Combustion furnace or incinerator, and method for reducing discharge of regulated gas content of the furnaces - Google Patents
Combustion furnace or incinerator, and method for reducing discharge of regulated gas content of the furnacesInfo
- Publication number
- JP2002228130A JP2002228130A JP2001025894A JP2001025894A JP2002228130A JP 2002228130 A JP2002228130 A JP 2002228130A JP 2001025894 A JP2001025894 A JP 2001025894A JP 2001025894 A JP2001025894 A JP 2001025894A JP 2002228130 A JP2002228130 A JP 2002228130A
- Authority
- JP
- Japan
- Prior art keywords
- combustion
- furnace
- exhaust gas
- incinerator
- temperature
- 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.)
- Withdrawn
Links
- 238000002485 combustion reaction Methods 0.000 title claims abstract description 56
- 238000000034 method Methods 0.000 title claims description 8
- 230000001105 regulatory effect Effects 0.000 title 1
- 239000007789 gas Substances 0.000 claims abstract description 35
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 25
- 239000001301 oxygen Substances 0.000 claims abstract description 25
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 25
- 239000000446 fuel Substances 0.000 claims abstract description 12
- 238000005192 partition Methods 0.000 claims description 3
- 238000010521 absorption reaction Methods 0.000 claims description 2
- 230000033228 biological regulation Effects 0.000 claims description 2
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 abstract 1
- 238000009434 installation Methods 0.000 description 11
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 description 6
- 230000015572 biosynthetic process Effects 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- 101710112287 DNA-directed RNA polymerases I and III subunit RPAC2 Proteins 0.000 description 2
- 101710183183 Probable DNA-directed RNA polymerases I and III subunit RPAC2 Proteins 0.000 description 2
- ATUOYWHBWRKTHZ-UHFFFAOYSA-N Propane Chemical compound CCC ATUOYWHBWRKTHZ-UHFFFAOYSA-N 0.000 description 2
- 102100034616 Protein POLR1D, isoform 2 Human genes 0.000 description 2
- 238000010790 dilution Methods 0.000 description 2
- 239000012895 dilution Substances 0.000 description 2
- 150000002013 dioxins Chemical class 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 230000001771 impaired effect Effects 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- 230000000717 retained effect Effects 0.000 description 2
- 239000002918 waste heat Substances 0.000 description 2
- 206010021143 Hypoxia Diseases 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000002950 deficient Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000004907 flux Effects 0.000 description 1
- 230000006698 induction Effects 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 239000001294 propane Substances 0.000 description 1
- 230000007480 spreading Effects 0.000 description 1
- 238000004056 waste incineration Methods 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Landscapes
- Incineration Of Waste (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、高温空気を利用し
た燃焼炉若しくは焼却炉、及びこれらの炉の排出ガス規
制分低減方法に係り、特にストーカ式焼却炉や流動層式
焼却炉におけるNOxやダイオキシン等の排ガス濃度を
低減する廃棄物焼却炉の燃焼制御方法とその装置に関す
る。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a combustion furnace or an incinerator using high-temperature air and a method for reducing the emission control of these furnaces. The present invention relates to a method and apparatus for controlling combustion in a waste incinerator that reduces the concentration of exhaust gas such as dioxin.
【0002】[0002]
【従来の技術】従来より、廃棄物焼却ストーカ炉・流動
層炉では、二次燃焼部に温度分布を持つため、比較的低
温部ではDXNsの未分解、同じく高温部ではサーマル
NOxの生成といった有害ガスを発生しており、その除
去は重要な課題である。これらの、有害ガスは、主とし
て、炉の出口経路に設けた排ガス処理系(特に反応バグ
フィルタ)にて除去している。2. Description of the Related Art Conventionally, in waste incineration stoker furnaces and fluidized bed furnaces, there is a temperature distribution in the secondary combustion part, so DXNs are not decomposed in relatively low temperature parts, and thermal NOx is generated in high temperature parts. Gas is generated, and its removal is an important issue. These harmful gases are mainly removed by an exhaust gas treatment system (especially a reaction bag filter) provided in the outlet path of the furnace.
【0003】更に炉出口よりの排ガスは、800℃以上
の高温であり、一方バグフィルタの耐熱温度は250℃
前後であり、このため炉出口よりの高温ガスは、ボイラ
や冷却器を通しながら250℃以下に冷却して反応バグ
フィルタに導入しなければならず、その間にダイオキシ
ンの再合成等が生じてしまう。Further, the exhaust gas from the furnace outlet has a high temperature of 800 ° C. or more, while the heat resistance temperature of the bag filter is 250 ° C.
Therefore, the hot gas from the furnace outlet must be cooled to 250 ° C. or lower while passing through a boiler or a cooler and introduced into the reaction bag filter, during which dioxin resynthesis occurs. .
【0004】[0004]
【発明が解決しようとする課題】本発明はかかる従来技
術の欠点に鑑み、炉の出口経路に設けた排ガス処理系で
ダイオキシンを除去するのではなく、前記炉の出口より
排出された排ガスを直接燃焼することにより、ダイオキ
シンやNOxの発生を直接抑制可能に構成し、これによ
り、炉の出口経路に設けた排ガス処理系の負担軽減と小
型化を図る事の出来る燃焼炉若しくは焼却炉、及びこれ
らの炉の排出ガス規制分低減方法を提供することを目的
とする。又本発明の他の目的は炉出口側の廃熱の限度ま
での有効利用を図ることにある。SUMMARY OF THE INVENTION In view of the drawbacks of the prior art, the present invention does not remove dioxin in an exhaust gas treatment system provided in an outlet path of a furnace, but directly removes exhaust gas discharged from the outlet of the furnace. Combustion furnaces or incinerators capable of directly suppressing the generation of dioxins and NOx by burning, thereby reducing the burden and reducing the size of the exhaust gas treatment system provided at the outlet path of the furnace, and It is an object of the present invention to provide a method for reducing exhaust gas regulations of furnaces. Another object of the present invention is to make effective use of waste heat at the furnace outlet side up to the limit.
【0005】[0005]
【課題を解決するための手段】本発明はかかる課題を解
決するために、燃焼炉若しくは焼却炉の炉出口側に設け
た空域に助燃料を吹き込み、炉より排出される低酸素濃
度の高温排ガスを燃焼空気として、燃焼させることを特
徴とする。この場合燃焼炉には石炭炊き等の燃焼ボイラ
を含み、又焼却炉にはストーカや流動層等の廃棄物焼却
炉を含む。SUMMARY OF THE INVENTION In order to solve the above-mentioned problems, the present invention blows auxiliary fuel into an air space provided on the furnace outlet side of a combustion furnace or an incinerator, and discharges high-temperature exhaust gas having a low oxygen concentration discharged from the furnace. As combustion air. In this case, the combustion furnace includes a combustion boiler for burning coal, and the incinerator includes a waste incinerator such as a stoker or a fluidized bed.
【0006】かかる発明によれば、前記炉出口側空域に
供給された助燃料は、高温低酸素濃度空気により燃焼す
るため、均一温度場を形成する。その結果、未分解のD
XNsの分解が可能となる。また、緩慢な燃焼によりN
Oxを低減することが可能となる。又この方式では、従
来の高温空気燃焼に必要な高温空気発生装置自体を省略
することができる。According to this invention, the auxiliary fuel supplied to the furnace outlet side air space is burned by the high-temperature low-oxygen-concentration air, so that a uniform temperature field is formed. As a result, undecomposed D
Decomposition of XNs becomes possible. Also, due to slow combustion, N
Ox can be reduced. Further, in this method, the high-temperature air generator itself required for the conventional high-temperature air combustion can be omitted.
【0007】又ダイオキシンやNOxを効果的に低減す
るには、前記高温排ガスが、800℃以上、且つ酸素濃
度が略5〜11%であるのがよい。ただし800℃以下
ではダイオキシンが分解されず、酸素濃度が11%以上
ではNOxの低減が出来ない。更に酸素濃度が略5%以
下では助燃量を供給しても燃焼に至らない。In order to effectively reduce dioxins and NOx, the high-temperature exhaust gas preferably has a temperature of 800 ° C. or more and an oxygen concentration of about 5 to 11%. However, dioxin is not decomposed at 800 ° C. or lower, and NOx cannot be reduced at an oxygen concentration of 11% or more. Further, if the oxygen concentration is about 5% or less, combustion does not occur even if the auxiliary combustion amount is supplied.
【0008】本発明に至った経過を具体的に説明する。
炉出口側より得られる排ガスは炉内に一次燃焼及び二次
燃焼(フリーボード)により、酸素濃度は低下している
が、排ガスは高温であるが故にその酸素濃度を極端に極
端に希釈しても燃焼安定性は損なわれず、然もNOx発
生原因である燃焼最高温度は希釈により低下することが
期待できる。そしてこのような高温希簿燃焼により局所
高温域の減少とともに、均一燃焼温度場の形成が可能と
なり、低NOx化が実現できるとともに、800℃以上
の温度で燃焼場を形成することによりダイオキシンの低
減も可能である。尚、本発明者の実験結果では、図2に
示すように、温度が900〜1200℃、酸素濃度が5
〜11%が好ましいことが理解された。The process leading to the present invention will be specifically described.
Exhaust gas obtained from the furnace outlet side has reduced oxygen concentration in the furnace due to primary combustion and secondary combustion (free board), but since the exhaust gas is at a high temperature, the oxygen concentration is extremely diluted. However, combustion stability is not impaired, and it can be expected that the highest combustion temperature, which is a cause of NOx generation, will be lowered by dilution. Such high-temperature rare-burn combustion reduces the local high-temperature region and enables the formation of a uniform combustion temperature field, thereby realizing a low NOx reduction. In addition, the formation of a combustion field at a temperature of 800 ° C. or higher reduces dioxin. Is also possible. According to the experimental results of the inventor, as shown in FIG. 2, the temperature was 900 to 1200 ° C. and the oxygen concentration was 5 to 5.
It has been found that ~ 11% is preferred.
【0009】請求項3記載の発明はかかる発明を効果的
に実施するための装置に関する発明で、燃焼炉若しくは
焼却炉の炉出口側に空域を設け、該空域に助燃料を吹き
込み、炉より排出される低酸素濃度の高温排ガスを燃焼
空気として、燃焼可能に構成したことを特徴とする。こ
の場合前記空域は、炉出口側に仕切若しくは絞りを介し
て形成される空域であるのがよい。けだし単に通路上に
助燃量を供給しても酸素不足のために円滑な燃焼に至ら
ない。そこで炉出口側に仕切若しくは絞りを介して高温
ガスが滞留し且つ円滑な燃焼が形成される滞留空域であ
るのがよい。The invention according to claim 3 relates to an apparatus for effectively carrying out the invention, wherein an air space is provided on the furnace outlet side of a combustion furnace or an incinerator, auxiliary fuel is blown into the air space, and discharged from the furnace. The high-temperature exhaust gas having a low oxygen concentration is used as combustion air to be combustible. In this case, the air space is preferably an air space formed on the furnace outlet side through a partition or a throttle. However, simply supplying the auxiliary combustion amount on the passage does not result in smooth combustion due to lack of oxygen. Therefore, it is preferable that the high-temperature gas is retained at the furnace outlet side via a partition or a throttle and the retained air region is formed in which smooth combustion is formed.
【0010】更に前記空域を炉出口側のボイラ取付位置
直前若しくはボイラ内に設け、前記燃焼をボイラの吸熱
に利用可能に構成することにより、ボイラーが従来の廃
熱ボイラーではなく、燃焼ボイラーとして機能し、より
高温の蒸気が得られて好ましい。また、本発明では、ヒ
ートフラックスが増大する為、ボイラのコンパクト化が
可能となる。Further, the air space is provided immediately before the boiler mounting position on the furnace outlet side or in the boiler so that the combustion can be utilized for heat absorption of the boiler, so that the boiler functions as a combustion boiler instead of a conventional waste heat boiler. In addition, higher temperature steam is preferably obtained. Further, in the present invention, since the heat flux increases, the boiler can be made compact.
【0011】[0011]
【発明の実施の形態】以下、本発明を図に示した実施例
を用いて詳細に説明する。但し、この実施例に記載され
る構成部品の寸法、形状、その相対配置などは特に特定
的な記載がない限り、この発明の範囲をそれのみに限定
する趣旨ではなく単なる説明例に過ぎない。図1は本発
明の実施形態にかかるストーカ式ごみ焼却炉の概略構成
を示し、11は生ごみが投入されるシュート(ホッパ)
で、図示はしていないがシュート1下方には、ごみの定
量供給装置としてのフィーダが配置されている。2はス
トーカで、フィーダよりのごみ投入側より後段に進むに
連れ、例えば乾燥ストーカ、燃焼ストーカ、更にはおき
燃焼ストーカが順次配設され、下方より一次空気3が導
入可能に構成されているとともに、更にその奥側に灰シ
ュート等の灰出し装置8が設けられている。そして前記
ストーカ2の上方には、上方に延在する再燃焼室4が設
けられ、該燃焼室4の入口側(下端側)のシュート1投
入側(前側)の炉壁と、これと対面する灰出し装置側
(後側)の炉壁との夫々に、OFAノズル(オーバーフ
ァイアエアノズル、若しくは二次空気供給ノズルともい
う)14、15が配設され、前記ノズル14、15への
二次空気の供給/開閉制御は夫々空気送給路に設けたダ
ンパ(図示せず)により行なわれる。そして炉出口側に
はボイラー設置空間5が形成されている。ボイラー設置
空間5は、入口側は炉壁51により下側が仕切られてお
り、又出口側は通路5bにより絞られ、下方空間に排出
ガスが滞留しながら循環する構成を取る。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below in detail with reference to an embodiment shown in the drawings. However, unless otherwise specified, dimensions, shapes, relative arrangements, and the like of the components described in this embodiment are not intended to limit the scope of the invention, but are merely illustrative examples. FIG. 1 shows a schematic configuration of a stoker-type incinerator according to an embodiment of the present invention, and 11 is a chute (hopper) into which garbage is put.
Although not shown, a feeder is disposed below the chute 1 as a device for quantitatively supplying dust. Reference numeral 2 denotes a stoker, for example, a drying stoker, a burning stoker, and further a burning stoker are sequentially arranged as the garbage enters from the feeder to a later stage, so that the primary air 3 can be introduced from below. Further, an ash removing device 8 such as an ash chute is provided on the back side. Above the stoker 2, a reburning chamber 4 extending upward is provided. The furnace wall on the chute 1 input side (front side) on the inlet side (lower side) of the combustion chamber 4 faces the furnace wall. OFA nozzles (also referred to as overfire air nozzles or secondary air supply nozzles) 14 and 15 are provided on the furnace wall on the ash removal device side (rear side), respectively, and secondary air is supplied to the nozzles 14 and 15. Is controlled by dampers (not shown) provided in the air supply passages. A boiler installation space 5 is formed on the furnace outlet side. The lower side of the boiler installation space 5 is partitioned by the furnace wall 51 on the inlet side, and the outlet side is narrowed by the passage 5b, so that the exhaust gas circulates while staying in the lower space.
【0012】又前記ボイラ設置空間5の入口側頂部に
は、助燃量供給ノズル12が設けられ、高温排気ガスが
滞留する下側空間に向けて助燃量を噴出させている。そ
して前記ボイラー設置空間5内壁には水管構造体からな
るボイラー5aが取り付けられている。そして、前記ボ
イラー設置空間5の出口通路5b側には、公知のように
減温塔7、バグフィルタのような反応集塵装置8、誘引
通風機9及び煙突10が配設されている。An auxiliary fuel supply nozzle 12 is provided at the top of the boiler installation space 5 on the inlet side, and blows the auxiliary fuel toward the lower space where high-temperature exhaust gas stays. A boiler 5a composed of a water pipe structure is attached to the inner wall of the boiler installation space 5. On the outlet passage 5b side of the boiler installation space 5, a cooling tower 7, a reaction dust collector 8 such as a bag filter, an induction ventilator 9, and a chimney 10 are provided in a known manner.
【0013】かかる焼却炉のごみ燃焼方法を以下に説明
する。シュート11内に投入されたごみは、不図示のフ
ィーダによってストーカ3上に定量的に供給され、該ス
トーカ2上を灰シュート18側に向かって搬送されなが
ら夫々のストーカ2下方より供給される一次空気3によ
り、順次乾燥、ガス化燃焼、火炎燃焼、おき燃焼された
後、該燃焼後の灰は灰シュート等の灰取り出し装置8側
に落下する。一方、前記ストーカ2の乾燥/燃焼により
生成されたCmHn等の未燃分は、再燃焼室4の入口側
(下端側)のOFA前側ノズル14及びOFA後側ノズ
ル15から供給する二次空気(オーバーファイアエア、
以下OFAという)により燃焼させる。The method of burning waste in such an incinerator will be described below. The refuse introduced into the chutes 11 is quantitatively supplied onto the stoker 3 by a feeder (not shown), and is supplied from below each stoker 2 while being conveyed on the stoker 2 toward the ash chute 18 side. After being sequentially dried, gasified, flame-fired, and ignited by the air 3, the ash after the combustion falls to the ash removal device 8 such as an ash chute. On the other hand, unburned components such as CmHn generated by drying / combustion of the stoker 2 are supplied to the secondary air (from the OFA front side nozzle 14 and the OFA rear side nozzle 15 on the inlet side (lower side) of the reburning chamber 4. Overfire air,
(Hereinafter referred to as OFA).
【0014】前記二次空気の燃焼により高温且つ酸素不
足となった排ガスは前記炉出口側よりボイラー設置空間
5内に導入され、一方ボイラー設置空間5の入口頂部に
配設された助燃料供給ノズル12より、ボイラー設置空
間5内に助燃量が供給され、高温低酸素濃度空気からな
る排ガスにより燃焼するため、局所高温域が減少して均
一温度場を形成する。その結果、未分解のDXNsの分
解が可能となる。また、緩慢な燃焼によりNOxを低減
することが可能となる。The exhaust gas, which has become hot and oxygen deficient due to the combustion of the secondary air, is introduced into the boiler installation space 5 from the furnace outlet side, while an auxiliary fuel supply nozzle arranged at the top of the inlet of the boiler installation space 5 From 12, the auxiliary combustion amount is supplied into the boiler installation space 5, and the fuel is burned by exhaust gas composed of high-temperature, low-oxygen-concentration air, so that the local high-temperature region is reduced to form a uniform temperature field. As a result, undecomposed DXNs can be decomposed. Further, NOx can be reduced by slow combustion.
【0015】尚、図2は本実施例に基づく実験結果でス
トーカ下方より供給する一次空気については酸素濃度を
21〜30%酸素富化側に変化させ、一方温度は常温か
ら200℃の間で可変させる。二次空気は酸素濃度を2
1〜8%の酸素不足側に変化させ、一方温度は常温から
600℃の間で可変させる。このようにして炉出口側の
温度が、300〜1200℃酸素濃度が5〜21%の種
々の排ガス状態が生成された。そしてこの状態で助燃料
供給ノズル12より、ボイラー設置空間5内にプロパン
ガスからなる助燃量を供給して燃焼状態を図2に示すよ
うに把握した。FIG. 2 shows the experimental results based on the present embodiment, in which the oxygen concentration of the primary air supplied from below the stoker is changed to 21-30% oxygen-enriched side, while the temperature is between normal temperature and 200 ° C. Make it variable. Secondary air has an oxygen concentration of 2
The oxygen deficiency is varied from 1 to 8%, while the temperature is varied from room temperature to 600 ° C. In this way, various exhaust gas states having a furnace outlet temperature of 300 to 1200 ° C. and an oxygen concentration of 5 to 21% were generated. Then, in this state, the auxiliary fuel supply nozzle 12 supplied an auxiliary combustion amount of propane gas into the boiler installation space 5 to grasp the combustion state as shown in FIG.
【0016】本図より明らかなように800℃以下の低
酸素域では不燃域が形成され、又酸素濃度が15〜21
%では局所燃焼域の存在が見られた。しかしながら、8
00℃〜1200℃の温度域で且つ5〜11%の低酸素
域では青白い炎とともに、ボイラー設置空間全体に波及
する燃焼が見られた。従って本実施例によれば、炉出口
側より得られる排ガスは炉内に一次燃焼及び二次燃焼
(フリーボード)により、酸素濃度は低下しているが、
排ガスは高温であるが故にその酸素濃度5〜11%程度
に希釈しても燃焼安定性は損なわれず、然もNOx発生
原因である燃焼最高温度は希釈により低下することが期
待できる。そしてこのような高温希簿燃焼により局所高
温域の減少とともに、均一燃焼温度場の形成が可能とな
り、低NOx化が実現できるとともに、800℃以上の
温度で燃焼場を形成することによりダイオキシンの低減
も可能である。尚、特にその範囲は図2に示すように、
温度が850〜1200℃、酸素濃度が5〜11%が好
ましいことが理解された。As is apparent from the figure, in the low oxygen region below 800 ° C., a non-combustible region is formed, and the oxygen concentration becomes 15 to 21.
%, The presence of a local combustion zone was observed. However, 8
In the temperature range of 00 ° C. to 1200 ° C. and the low oxygen range of 5% to 11%, burning spreading to the entire boiler installation space was observed together with pale flame. Therefore, according to the present embodiment, the exhaust gas obtained from the furnace outlet side has a reduced oxygen concentration due to primary combustion and secondary combustion (free board) in the furnace.
Since the exhaust gas has a high temperature, even if it is diluted to an oxygen concentration of about 5 to 11%, combustion stability is not impaired, and it can be expected that the highest combustion temperature, which is a cause of NOx generation, is lowered by dilution. Such high-temperature rare-burn combustion reduces the local high-temperature region and enables the formation of a uniform combustion temperature field, thereby realizing a low NOx emission. Is also possible. In particular, the range is as shown in FIG.
It has been understood that the temperature is preferably 850 to 1200 ° C. and the oxygen concentration is preferably 5 to 11%.
【0017】[0017]
【発明の効果】以上記載のごとく本発明によれば、焼却
炉排ガスを燃焼空気とした高温均一空気燃焼の実現によ
り低NOxとダイオキシンの低減が可能になるととも
に、排ガスボイラのコンパクト化は排ガス処理系の付加
の軽減につながる。As described above, according to the present invention, low NOx and dioxin can be reduced by realizing high-temperature uniform air combustion using incinerator exhaust gas as combustion air, and a compact exhaust gas boiler is used for exhaust gas treatment. This leads to a reduction in system addition.
【図1】 本発明の実施形態たるストーカ式ごみ焼却炉
の概略構成図を示す。FIG. 1 shows a schematic configuration diagram of a stoker-type incinerator as an embodiment of the present invention.
【図2】 図1の焼却炉における排ガスの燃焼状態を酸
素濃度と排ガス温度の関係によって示すグラフ図であ
る。FIG. 2 is a graph showing a combustion state of exhaust gas in the incinerator of FIG. 1 by a relationship between an oxygen concentration and an exhaust gas temperature.
4 再燃焼室 5 ボイラー設置空間 12 ストーカ 12 助燃量供給ノズル 14、15 OFAノズル 51 炉壁 5b 通路 5a ボイラー Reference Signs List 4 Reburning chamber 5 Boiler installation space 12 Stalker 12 Fuel supply amount supply nozzle 14, 15 OFA nozzle 51 Furnace wall 5b Passage 5a Boiler
フロントページの続き Fターム(参考) 3K061 AA02 AA11 AB01 AC01 AC19 BA01 BA08 BA09 CA01 HA05 HA18 HA29 3K065 AA01 AA11 AB01 AC01 AC19 BA01 BA08 GA03 GA12 GA14 GA32 3K078 AA01 AA08 AA09 BA03 BA22 BA26 CA03 CA06 CA12 CA21Continued on the front page F-term (reference) 3K061 AA02 AA11 AB01 AC01 AC19 BA01 BA08 BA09 CA01 HA05 HA18 HA29 3K065 AA01 AA11 AB01 AC01 AC19 BA01 BA08 GA03 GA12 GA14 GA32 3K078 AA01 AA08 AA09 BA03 BA22 BA26 CA21
Claims (5)
た空域に助燃料を吹き込み、炉より排出される低酸素濃
度の高温排ガスを燃焼空気として、燃焼させることを特
徴とする燃焼炉若しくは焼却炉の規制分低減方法。A combustion furnace characterized in that auxiliary fuel is blown into an air space provided on the furnace outlet side of a combustion furnace or an incinerator, and high-temperature exhaust gas with a low oxygen concentration discharged from the furnace is burned as combustion air. How to reduce regulations for incinerators.
酸素濃度が略5〜11%であることを特徴とする燃焼炉
若しくは焼却炉の排出ガス規制分低減方法。2. A method according to claim 1, wherein said high-temperature exhaust gas has a temperature of 800 ° C. or more and an oxygen concentration of about 5 to 11%.
を設け、該空域に助燃料を吹き込み、炉より排出される
低酸素濃度の高温排ガスを燃焼空気として、燃焼可能に
構成したことを特徴とする燃焼炉若しくは焼却炉。3. An air space is provided on a furnace outlet side of a combustion furnace or an incinerator, auxiliary fuel is blown into the air space, and high-temperature exhaust gas having a low oxygen concentration discharged from the furnace is burnable as combustion air. Combustion furnace or incinerator characterized by the following.
を介して形成される空域であることを特徴とする請求項
3記載の燃焼炉若しくは焼却炉。4. The combustion furnace or the incinerator according to claim 3, wherein the air space is an air space formed on the furnace outlet side through a partition or a throttle.
前若しくはボイラ内に設け、前記燃焼をボイラの吸熱に
利用可能に構成したことを特徴とする請求項3記載の燃
焼炉若しくは焼却炉。5. The combustion furnace or incinerator according to claim 3, wherein the air space is provided immediately before the boiler mounting position on the furnace outlet side or in the boiler so that the combustion can be utilized for heat absorption of the boiler.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2001025894A JP2002228130A (en) | 2001-02-01 | 2001-02-01 | Combustion furnace or incinerator, and method for reducing discharge of regulated gas content of the furnaces |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2001025894A JP2002228130A (en) | 2001-02-01 | 2001-02-01 | Combustion furnace or incinerator, and method for reducing discharge of regulated gas content of the furnaces |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JP2002228130A true JP2002228130A (en) | 2002-08-14 |
Family
ID=18890805
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2001025894A Withdrawn JP2002228130A (en) | 2001-02-01 | 2001-02-01 | Combustion furnace or incinerator, and method for reducing discharge of regulated gas content of the furnaces |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2002228130A (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2003093728A1 (en) * | 2002-05-02 | 2003-11-13 | Jfe Engineering Corporation | Method of operating waste incinerator and waste incinerator |
| JP2004028548A (en) * | 2002-05-02 | 2004-01-29 | Jfe Engineering Kk | Operating method of waste incinerator and waste incinerator |
| JP2004077014A (en) * | 2002-08-15 | 2004-03-11 | Jfe Engineering Kk | How to operate a waste incinerator |
| JP2004077013A (en) * | 2002-08-15 | 2004-03-11 | Jfe Engineering Kk | Operating method of waste incinerator and waste incinerator |
-
2001
- 2001-02-01 JP JP2001025894A patent/JP2002228130A/en not_active Withdrawn
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2003093728A1 (en) * | 2002-05-02 | 2003-11-13 | Jfe Engineering Corporation | Method of operating waste incinerator and waste incinerator |
| JP2004028548A (en) * | 2002-05-02 | 2004-01-29 | Jfe Engineering Kk | Operating method of waste incinerator and waste incinerator |
| JP2004077014A (en) * | 2002-08-15 | 2004-03-11 | Jfe Engineering Kk | How to operate a waste incinerator |
| JP2004077013A (en) * | 2002-08-15 | 2004-03-11 | Jfe Engineering Kk | Operating method of waste incinerator and waste incinerator |
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