JPH0549855A - Method for decreasing nitrogen oxide of combustion gas - Google Patents
Method for decreasing nitrogen oxide of combustion gasInfo
- Publication number
- JPH0549855A JPH0549855A JP3234154A JP23415491A JPH0549855A JP H0549855 A JPH0549855 A JP H0549855A JP 3234154 A JP3234154 A JP 3234154A JP 23415491 A JP23415491 A JP 23415491A JP H0549855 A JPH0549855 A JP H0549855A
- Authority
- JP
- Japan
- Prior art keywords
- combustion gas
- ammonia
- combustion
- nitrogen oxides
- nozzle
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 title claims abstract description 117
- 239000000567 combustion gas Substances 0.000 title claims abstract description 58
- 238000000034 method Methods 0.000 title claims description 26
- 230000003247 decreasing effect Effects 0.000 title 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims abstract description 101
- 229910021529 ammonia Inorganic materials 0.000 claims abstract description 48
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 37
- 239000000779 smoke Substances 0.000 abstract description 26
- 239000007789 gas Substances 0.000 abstract description 14
- 230000035484 reaction time Effects 0.000 abstract description 3
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 abstract description 2
- 235000011114 ammonium hydroxide Nutrition 0.000 abstract description 2
- 238000002485 combustion reaction Methods 0.000 description 22
- 238000006243 chemical reaction Methods 0.000 description 15
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 14
- 238000007865 diluting Methods 0.000 description 11
- 239000000446 fuel Substances 0.000 description 8
- 239000003054 catalyst Substances 0.000 description 7
- 229910052757 nitrogen Inorganic materials 0.000 description 7
- 239000007921 spray Substances 0.000 description 7
- 230000008020 evaporation Effects 0.000 description 6
- 238000001704 evaporation Methods 0.000 description 6
- 238000006722 reduction reaction Methods 0.000 description 4
- 238000003915 air pollution Methods 0.000 description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 239000004215 Carbon black (E152) Substances 0.000 description 2
- 238000009841 combustion method Methods 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- 229930195733 hydrocarbon Natural products 0.000 description 2
- 150000002430 hydrocarbons Chemical class 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- 239000004071 soot Substances 0.000 description 2
- 238000005507 spraying Methods 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- 229910010413 TiO 2 Inorganic materials 0.000 description 1
- 230000001154 acute effect Effects 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000010531 catalytic reduction reaction Methods 0.000 description 1
- 230000003111 delayed effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000000839 emulsion Substances 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 238000003780 insertion Methods 0.000 description 1
- 230000037431 insertion Effects 0.000 description 1
- 239000003350 kerosene Substances 0.000 description 1
- 239000003915 liquefied petroleum gas Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
Abstract
(57)【要約】
【目的】 排ガス中の窒素酸化物の低減を図る。
【構成】 燃焼ガス10が流れ込む後部煙室8に、燃焼
ガス10の流れに対向してアンモニアを噴霧し得るよう
に、ノズル11を配設する。燃焼ガス10中の窒素酸化
物とアンモニア稀釈水との反応時間を長くできて燃焼ガ
ス中の窒素酸化物を大幅に低減できる。
(57) [Summary] [Purpose] To reduce nitrogen oxides in exhaust gas. A nozzle 11 is arranged in a rear smoke chamber 8 into which the combustion gas 10 flows so that ammonia can be sprayed so as to face the flow of the combustion gas 10. The reaction time between the nitrogen oxide in the combustion gas 10 and the diluted ammonia water can be lengthened, and the nitrogen oxide in the combustion gas can be significantly reduced.
Description
【0001】[0001]
【産業上の利用分野】本発明は、気体、液体及び固体等
の燃料を使用する各種燃焼炉の燃焼ガスの窒素酸化物低
減方法に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for reducing nitrogen oxides in combustion gas of various combustion furnaces using fuel such as gas, liquid and solid.
【0002】[0002]
【従来の技術】一般に燃焼炉において発生する窒素酸化
物(NOX)には、主に、(イ)各種燃料中に含まれて
いる窒素成分が酸化されて生じたものと、(ロ)特に、
重油、灯油、LPG等の炭化水素原料を燃焼する際に、
空気比(実際に供給する空気量/理論的に必要な空気
量)約0.5〜1.4の状態で、炭化水素が空気中の窒
素と反応し、更にいくつかの反応を経て即発的に生じた
もの(即発NO)と、(ハ)燃焼に伴ない、空気中の窒
素と酸素とが高温で反応して生じたもの(熱NO)があ
る。2. Description of the Related Art Generally, nitrogen oxides (NO x ) generated in a combustion furnace are mainly (a) those generated by oxidizing nitrogen components contained in various fuels, and (b) especially ,
When burning hydrocarbon raw materials such as heavy oil, kerosene, and LPG,
At an air ratio (actually supplied air amount / theoretical required air amount) of about 0.5 to 1.4, hydrocarbon reacts with nitrogen in the air, and promptly goes through some reactions. 2) (prompt NO), and (c) due to combustion, nitrogen and oxygen in the air react with each other at a high temperature (NO).
【0003】前述の窒素酸化物は大気汚染の面から問題
となっており、そのために下記の如き種々の窒素酸化物
の発生を抑制する方法が採用されている。 (i)燃焼用空気を二段に分けて燃焼室内へ供給し、第
一段では完全燃焼に必要な空気量よりも少ない空気で燃
料を燃焼させ、第二段で完全燃焼に必要な残りの空気を
供給する二段燃焼法。 (ii)燃焼により生じた排ガスを循環させて再び燃料
に混合する排ガスの再循環法。 (iii)水蒸気又は水を燃焼室に吹き込むインジェク
ション法。 (iv)低窒素燃料の使用に切換える燃料転換法。 (v)エマルジョン燃料を用いる方法。 (vi)燃焼域での酸素を低減する低酸素燃焼法。 等がある。The above-mentioned nitrogen oxides pose a problem from the viewpoint of air pollution, and therefore, the following methods for suppressing the generation of various nitrogen oxides have been adopted. (I) Combustion air is divided into two stages and supplied to the combustion chamber, the first stage burns the fuel with less air than the amount required for complete combustion, and the second stage uses the remaining amount required for complete combustion. A two-stage combustion method that supplies air. (Ii) Exhaust gas recirculation method in which exhaust gas generated by combustion is circulated and mixed again with fuel. (Iii) An injection method in which steam or water is blown into the combustion chamber. (Iv) Fuel conversion method to switch to the use of low nitrogen fuel. (V) A method using an emulsion fuel. (Vi) A low oxygen combustion method for reducing oxygen in the combustion zone. Etc.
【0004】前記(i)の方法にあっては、一次燃焼領
域における一般的な空気比の0.5〜1.0の範囲では
即発NOの発生を抑制できず、又空気比0.5付近に保
って即発NOの発生を極力抑制するように試みても、第
二の空気供給部において未燃焼分が空気と反応して即発
NOが発生することになるという問題点があり、更に発
煙に伴ない燃焼炉内壁や伝熱面に付着する煤が発生し、
燃焼用空気及び燃焼ガスの流れを阻害するという問題点
もある。In the above method (i), it is impossible to suppress the generation of prompt NO in the range of 0.5 to 1.0 which is a general air ratio in the primary combustion region, and the air ratio is around 0.5. Even if an attempt is made to suppress the generation of prompt NO as much as possible, there is a problem that unburned matter reacts with the air in the second air supply section to generate prompt NO. As a result, soot that adheres to the inner wall of the combustion furnace and the heat transfer surface is generated,
There is also a problem of obstructing the flow of combustion air and combustion gas.
【0005】前述の(ii)の方法にあっては、窒素酸
化物の発生を効果的に抑制するために排ガスの再際循環
量を増すと、燃焼が不安定となるという問題点があり、
前記(iii)の方法にあっては、熱損失が大であると
いう問題点があり、前記(iv)(v)の方法にあって
は、コストアップになるという問題点があり、更に(v
i)の方法にあっては、前記(i)の方法と同様に発煙
に伴ない燃焼炉内壁や伝熱面に付着する煤が発生し、燃
焼用空気及び燃焼ガスの流れを阻害するという問題点が
ある。In the above method (ii), if the recirculation amount of exhaust gas is increased in order to effectively suppress the generation of nitrogen oxides, there is a problem that combustion becomes unstable.
The method (iii) has a problem that the heat loss is large, and the methods (iv) and (v) have a problem that the cost is increased.
In the method i), as in the method i), soot is attached to the inner wall of the combustion furnace and the heat transfer surface along with the smoke, and the flow of combustion air and combustion gas is obstructed. There is a point.
【0006】従って前記せる種々の問題点を配慮して、
下記の如き、アンモニアとの化学反応を利用して窒素酸
化物を低減する方法が考えられ、実施されている。Therefore, in consideration of the various problems mentioned above,
The following methods for reducing nitrogen oxides by utilizing a chemical reaction with ammonia have been conceived and implemented.
【0007】(vii)ハニカム状の触媒(材質TiO
2、V2O5等)を煙道に設置し、触媒設置場所より風上
部分からアンモニア水を風下方向に向け(燃焼ガスの流
れと同方向に)噴射して触媒でアンモニアと窒素酸化物
との反応を促進することにより窒素酸化物を低減するア
ンモニア接触還元法。(Vii) Honeycomb-shaped catalyst (material: TiO 2)
2 , V 2 O 5 etc.) is installed in the flue, and ammonia water is jetted downward (in the same direction as the flow of the combustion gas) from the windward part of the catalyst installation location to cause ammonia and nitrogen oxides on the catalyst. Ammonia catalytic reduction method that reduces nitrogen oxides by promoting the reaction with.
【0008】(viii)燃焼炉の燃焼ガス(800〜
1100℃)中に該燃焼ガスの流れと同方向にアンモニ
アガスを直接注入することにより、触媒なしで窒素と水
に分解して窒素酸化物を低減する高温無触媒式脱硝法。(Viii) Combustion gas of combustion furnace (800-
A high temperature non-catalytic denitration method in which ammonia gas is directly injected into the same direction as the flow of the combustion gas into 1100 ° C.) to decompose nitrogen and water without a catalyst to reduce nitrogen oxides.
【0009】[0009]
【発明が解決しようとする課題】しかしながら前記(v
ii)の方法にあっては、触媒が高価なものであると共
に、触媒設置場所及び触媒の管理の面から設備費が嵩む
という問題があり、又(viii)の方法にあっては、
燃焼ガスとアンモニアガスとが平行して流れるためにア
ンモニアガスと未反応の燃焼ガスが多量に生じ、そのた
めにアンモニアガスを多量に注入することも行われてい
るが、それにも拘わらず未反応な燃焼ガスと過剰なアン
モニアガスが大気に放出されていて大気汚染の面から好
ましくない。However, the above (v
In the method (ii), there is a problem that the catalyst is expensive, and the facility cost is increased in terms of the place where the catalyst is installed and the management of the catalyst, and in the method (viii),
Since the combustion gas and the ammonia gas flow in parallel, a large amount of the ammonia gas and the unreacted combustion gas are generated. Therefore, a large amount of the ammonia gas is also injected, but nevertheless unreacted. Combustion gas and excess ammonia gas are released to the atmosphere, which is not preferable from the viewpoint of air pollution.
【0010】本発明は、上記実情に鑑み、低コストにて
効率良く燃焼炉の燃焼ガス中の窒素酸化物を低減できる
燃焼ガスの窒素酸化物低減方法を提供することを目的と
するものである。In view of the above situation, it is an object of the present invention to provide a method for reducing nitrogen oxides in combustion gas, which is capable of efficiently reducing nitrogen oxides in combustion gas in a combustion furnace at low cost. ..
【0011】[0011]
【課題を解決するための手段】本発明は、燃焼ガスの温
度が略900〜1000℃の位置に、燃焼ガスの流れに
対向してアンモニア稀釈水を噴射することを特徴とする
燃焼ガスの窒素酸化物低減方法、にかかるものである。DISCLOSURE OF THE INVENTION The present invention is characterized by injecting ammonia diluted water at a position where the temperature of the combustion gas is approximately 900 to 1000 ° C. in opposition to the flow of the combustion gas. The present invention relates to an oxide reduction method.
【0012】[0012]
【作用】燃焼ガスにその流れに対向してアンモニア稀釈
水を噴射して、燃焼ガス中の窒素酸化物とアンモニアと
を化学反応させ、排ガス中の窒素酸化物の含有値を下げ
ると同時にアシストスマッド(煤の塊)も低減させるこ
とができる。[Operation] Ammonia diluted water is injected into the combustion gas in opposition to the flow thereof to chemically react the nitrogen oxides and ammonia in the combustion gas to lower the content of nitrogen oxides in the exhaust gas and at the same time to assist the gas. Muds can also be reduced.
【0013】[0013]
【実施例】本発明を、炉筒煙管ボイラを例にとり図1及
び図2に基づき説明する。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described with reference to FIGS. 1 and 2 by taking a flue tube boiler as an example.
【0014】炉筒煙管ボイラは、図2に示す如くボイラ
胴1内に、波形炉筒2と第一、第二、第三煙管群3,
4,5が同軸方向に配設された内だきボイラであり、波
形炉筒2のバーナ6側に前部煙室7を設けると共に、波
形炉筒2の反バーナ6側に後部煙室8及び排ガス排出室
9を設け、波形炉筒2と後部煙室8とを第一煙管群3に
より、後部煙室8と前部煙室7とを第二煙管群4によ
り、前部煙室7と排ガス排出室9とを第三煙管群5によ
り夫々連結して、燃焼ガス10を、波形炉筒2→第一煙
管群3→後部煙室8→第二煙管群4→前部煙室7→第三
煙管群5→排ガス排出室9の順序で流すようにしたもの
である。As shown in FIG. 2, the furnace tube smoke tube boiler has a corrugated furnace tube 2 and first, second, and third smoke tube groups 3 in a boiler cylinder 1.
Reference numerals 4 and 5 are inner-fired boilers arranged coaxially, and a front smoke chamber 7 is provided on the burner 6 side of the corrugated furnace tube 2, and a rear smoke chamber 8 and a rear smoke chamber 8 on the side opposite to the burner 6 of the corrugated furnace tube 2. An exhaust gas discharge chamber 9 is provided, the corrugated furnace tube 2 and the rear smoke chamber 8 are formed by the first smoke pipe group 3, the rear smoke chamber 8 and the front smoke chamber 7 are formed by the second smoke pipe group 4, and the front smoke chamber 7 is formed. The exhaust gas discharge chamber 9 is connected to each other by the third smoke pipe group 5, and the combustion gas 10 is converted into the corrugated furnace tube 2 → the first smoke pipe group 3 → the rear smoke chamber 8 → the second smoke pipe group 4 → the front smoke chamber 7 → The third smoke pipe group 5 and the exhaust gas discharge chamber 9 are made to flow in this order.
【0015】前記炉筒煙管ボイラの燃焼ガス10の温度
が略900〜1000℃である個所の後部煙室8の下側
部に、圧力噴霧式のノズル11をそのノズル口部分が第
一煙管群3から流入する燃焼ガスの流れに対向するよう
にして設置する。A pressure spray type nozzle 11 is provided at the lower side of the rear smoke chamber 8 where the temperature of the combustion gas 10 of the furnace tube smoke tube boiler is approximately 900 to 1000 ° C. It is installed so as to face the flow of combustion gas flowing in from 3.
【0016】又アンモニア稀釈水収納タンク12を、バ
ルブ14を組込んだ配管13を介しポンプ15に連結す
ると共に、前記ノズル11に一端を連結したフレキシブ
ルパイプ16の他端を配管17を介し前記ポンプ15に
連結して該ポンプ15によりアンモニア稀釈水収納タン
ク12からノズル11にアンモニア稀釈水を圧送し得る
ようにする。Further, the ammonia diluting water storage tank 12 is connected to a pump 15 via a pipe 13 incorporating a valve 14, and the other end of a flexible pipe 16 having one end connected to the nozzle 11 is connected via a pipe 17 to the pump. The pump 15 is connected to the pump 15 so that the ammonia diluted water can be pumped from the ammonia diluted water storage tank 12 to the nozzle 11.
【0017】更に前記ノズル11における後部煙室8へ
の設置部及びその近傍個所にシール管18を外嵌せしめ
て該シール管18の分岐管19からシールエア20をシ
ール管18の内側とノズル11の外側との空間に吹込み
該ノズル11をエアシールして冷却し得るようにする。Further, a seal pipe 18 is externally fitted to a portion of the nozzle 11 which is installed in the rear smoke chamber 8 and a portion in the vicinity thereof, and seal air 20 is supplied from a branch pipe 19 of the seal pipe 18 to the inside of the seal pipe 18 and the nozzle 11. The nozzle 11 is blown into the space with the outside and air-sealed so that the nozzle 11 can be cooled.
【0018】以下、窒素酸化物(NOX)の低減方法に
ついて説明する。A method of reducing nitrogen oxides (NO x ) will be described below.
【0019】先ずバルブ14を開にしポンプ15を駆動
することにより、アンモニア稀釈水収納タンク12から
アンモニア稀釈水をバルブ14→配管13→ポンプ15
→配管17→フレキシブルパイプ16→ノズル11の順
に圧送し、該ノズル11のノズル口からアンモニア稀釈
水を燃焼ガスの流れに対向して後部煙室8内に噴霧し、
下記の式のようにアンモニアと窒素酸化物との反応を起
こさせて窒素と水を得、燃焼ガス中の窒素酸化物を無窒
化し、燃焼ガス中の窒素酸化物を低減する。First, by opening the valve 14 and driving the pump 15, the ammonia diluted water is supplied from the ammonia diluted water storage tank 12 to the valve 14 → the pipe 13 → the pump 15
→ Pipe 17 → Flexible pipe 16 → Nozzle 11 is pressure-fed in that order, and ammonia diluted water is sprayed from the nozzle opening of the nozzle 11 into the rear smoke chamber 8 in opposition to the flow of combustion gas.
As shown in the following formula, a reaction between ammonia and nitrogen oxides is caused to obtain nitrogen and water, the nitrogen oxides in the combustion gas are denitrified, and the nitrogen oxides in the combustion gas are reduced.
【0020】 NH3+1/4O2→NH2+1/2H2O…(I) NH2+NO→N2+H2O …(II)NH 3 + 1 / 4O 2 → NH 2 + 1 / 2H 2 O (I) NH 2 + NO → N 2 + H 2 O (II)
【0021】この場合、燃焼ガスの流れにアンモニア稀
釈水を対向して噴霧するので、燃焼ガス中の窒素酸化物
とアンモニアとの反応時間を長くできて未反応な窒素酸
化物を大幅に少なくし得られ、燃焼ガス中の窒素酸化物
を大幅に低減できる。In this case, since the ammonia diluting water is sprayed so as to face the combustion gas flow, the reaction time between the nitrogen oxide and ammonia in the combustion gas can be lengthened and unreacted nitrogen oxide can be greatly reduced. As a result, nitrogen oxides in the combustion gas can be significantly reduced.
【0022】次に貫流ボイラに適用する場合について図
3に基づき説明する。Next, the case of application to a once-through boiler will be described with reference to FIG.
【0023】一側部に燃焼ガス流通用隙間22を軸方向
にあけて円筒状に配設された内側蒸発管群21の外側に
同芯状にして燃焼ガス通路24をあけて、該内側蒸発管
群21と連通する外側蒸発管群23が円筒状に配設され
ている。Combustion gas passages 24 are opened concentrically on the outside of a group of inner evaporation tubes 21 arranged in a cylindrical shape with a combustion gas distribution gap 22 formed in one side thereof in the axial direction, and the inner evaporation is carried out. An outer evaporation tube group 23 communicating with the tube group 21 is arranged in a cylindrical shape.
【0024】前記外側蒸発管群23には、内側蒸発管群
21から燃焼ガス通路24に流入した燃焼ガスが分岐し
て流れ合流する部分に軸方向に燃焼ガス排出用通路25
が形成されていると共に、燃焼ガス通路24を流れる燃
焼ガス温度が900〜1000℃に該当する外側蒸発管
群23の部分に軸方向に隙間26をあけてノズル11の
挿入用間口を形成してあり、該間口からノズル11を燃
焼ガス通路24に、燃焼ガスの流れに対向してアンモニ
ア稀釈水を噴霧し得るように差し込んであり、ノズル1
1の根元部は外壁に固定されている。In the outer evaporation pipe group 23, a combustion gas discharge passage 25 is formed in the axial direction at a portion where the combustion gas flowing from the inner evaporation pipe group 21 into the combustion gas passage 24 branches and merges.
Is formed, and a gap 26 is formed in the axial direction in the portion of the outer evaporation pipe group 23 where the temperature of the combustion gas flowing in the combustion gas passage 24 corresponds to 900 to 1000 ° C. to form an insertion opening for the nozzle 11. The nozzle 1 is inserted into the combustion gas passage 24 from the opening so as to face the flow of the combustion gas so that the ammonia diluting water can be sprayed.
The root portion of 1 is fixed to the outer wall.
【0025】前記ノズル11へアンモニア稀釈水を供給
する系統、エアシール系統は図1に示す如くなってい
る。The system for supplying ammonia diluted water to the nozzle 11 and the air seal system are as shown in FIG.
【0026】従ってノズル11からアンモニア稀釈水を
燃焼ガスの流れに対向して噴霧することにより、前記反
応式(I)(II)のようなアンモニアと燃焼ガス中の
窒素酸化物との反応を起させて窒素と水を得、燃焼ガス
中の窒素酸化物を無窒素化し、燃焼ガス中の窒素酸化物
を低減せしめることができる。Therefore, by spraying ammonia diluted water from the nozzle 11 so as to face the flow of the combustion gas, the reaction between ammonia and the nitrogen oxide in the combustion gas as in the above reaction formulas (I) and (II) is caused. By doing so, nitrogen and water are obtained, and nitrogen oxides in the combustion gas are made nitrogen-free, so that the nitrogen oxides in the combustion gas can be reduced.
【0027】更に前記せるように、ノズル11へアンモ
ニア稀釈水を供給する系統、エアシール系統はボイラ等
の燃焼設備とは独立しているので、例え故障したとして
も燃焼設備の稼働に影響を及ぼすことはない。Further, as described above, the system for supplying the ammonia diluted water to the nozzle 11 and the air seal system are independent of the combustion equipment such as the boiler, so that even if a failure occurs, the operation of the combustion equipment is affected. There is no.
【0028】前記反応式(I)(II)の反応は、反応
雰囲気の温度及びアンモニアの添加量に左右される。The reactions of the above reaction formulas (I) and (II) depend on the temperature of the reaction atmosphere and the amount of ammonia added.
【0029】反応雰囲気の温度である燃焼ガス温度と窒
素酸化物低減値との関係について種々実験したところ、
図4に示す如くなり、この図4によれば900〜100
0℃程度の燃焼ガス温度の時に窒素酸化物低減値が急峻
に変化していることがわかる。Various experiments were conducted on the relationship between the combustion gas temperature, which is the temperature of the reaction atmosphere, and the nitrogen oxide reduction value.
As shown in FIG. 4, according to FIG.
It can be seen that the nitrogen oxide reduction value sharply changes at the combustion gas temperature of about 0 ° C.
【0030】アンモニア稀釈水について述べるに、アン
モニア稀釈水の濃度を濃くし過ぎるとアンモニア稀釈水
の噴霧量の調整が難しく小容量のボイラではアンモニア
稀釈水の量を絞りきれずに大量に供給することになって
排ガス中の残存アンモニアとして排ガスと共に排出され
ることになり、又アンモニア稀釈水の噴霧量が過剰にな
ると排ガス中の残存アンモニア量が増えることになる。Regarding the ammonia diluted water, if the concentration of the ammonia diluted water is too high, it is difficult to adjust the spray amount of the ammonia diluted water, and in the case of a small capacity boiler, the amount of ammonia diluted water must be supplied in a large amount without being restricted. As a result, the residual ammonia in the exhaust gas is discharged together with the exhaust gas, and when the amount of sprayed ammonia diluting water becomes excessive, the amount of residual ammonia in the exhaust gas increases.
【0031】前記せる事柄を配慮して、アンモニア稀釈
水の噴霧量と残存アンモニア量との関係について種々実
験したところ、図5に示す如くなり、この図5によれば
燃料噴射量に対するアンモニア稀釈水の割合が10%以
下であれば残存アンモニア量が微量の状態を維持してい
ることがわかる。Various experiments were conducted on the relationship between the spray amount of the ammonia diluting water and the residual ammonia amount in consideration of the above-mentioned matters. As shown in FIG. 5, according to this FIG. 5, the ammonia diluting water with respect to the fuel injection amount was diluted. It can be seen that when the ratio is 10% or less, the residual ammonia amount maintains a trace amount.
【0032】アンモニア稀釈水を噴霧するノズルの噴霧
角度は、あまり鋭角であるとアンモニア稀釈水を噴霧し
なくなり、アンモニア稀釈水は棒状に噴射され燃焼ガス
中の窒素酸化物との反応が遅くなり、逆にノズルの噴霧
角度が広角だと壁にアンモニア稀釈水が当り燃焼ガス中
に効果的に拡散しない、等の問題が発生する。If the spray angle of the nozzle for spraying the ammonia diluting water is too acute, the ammonia diluting water will not be sprayed, and the ammonia diluting water will be sprayed in a rod shape and the reaction with the nitrogen oxides in the combustion gas will be delayed, On the contrary, if the spray angle of the nozzle is wide, problems such as ammonia diluted water hitting the wall and not effectively diffusing into the combustion gas occur.
【0033】そこで窒素酸化物を消去する方向に化学反
応を進行するために、前記せる事柄を配慮してノズル1
1の設置場所を、900〜1000℃程度の燃焼ガスに
対しアンモニア稀釈水を噴霧可能な場所にし、アンモニ
ア稀釈水の濃度を1〜5%とし、アンモニア稀釈水の噴
霧量を生バーナの燃焼量の1〜10%とし、ノズル11
のアンモニア稀釈水の噴霧角度を10°〜80°(炉筒
煙管ボイラの場合は60°〜80°)とし、ノズル11
からアンモニア稀釈水を噴霧する圧力を7〜10Kg/
cm2程度としたところ、各種燃焼炉においてきわめて
良好に反応式(II)の反応が進行し、燃焼ガス中の窒
素酸化物の低減をなし得た。Therefore, in order to proceed the chemical reaction in the direction of erasing nitrogen oxides, the nozzle 1 should be considered in consideration of the above-mentioned matters.
The installation place of No. 1 is a place where the ammonia diluted water can be sprayed to the combustion gas of about 900 to 1000 ° C, the concentration of the ammonia diluted water is set to 1 to 5%, and the spray amount of the ammonia diluted water is the combustion amount of the raw burner. 1 to 10% of the nozzle 11
The ammonia diluting water is sprayed at an angle of 10 ° to 80 ° (60 ° to 80 ° in the case of a fire tube boiler), and the nozzle 11
Ammonia diluted water is sprayed from 7 to 10 kg /
When it was set to about cm 2 , the reaction of the reaction formula (II) proceeded extremely well in various combustion furnaces, and the nitrogen oxides in the combustion gas could be reduced.
【0034】尚本発明は、図示し説明した実施例にのみ
限定されることなく、本発明の要旨を逸脱しない限り種
々の変更を加え得ることは勿論である。The present invention is not limited to the embodiments shown and described, and it goes without saying that various modifications can be made without departing from the gist of the present invention.
【0035】[0035]
【発明の効果】本発明の燃焼ガスの窒素酸化物低減方法
によれば、燃焼ガスに対向してアンモニア稀釈水を噴霧
するので、アンモニアと燃焼ガスの窒素酸化物との反応
時間を長くできて排ガス中の窒素酸化物を大幅に低減で
き、大気汚染防止を行い得られて公害対策上有益であ
る、等の優れた効果を奏し得る。According to the method for reducing nitrogen oxides in combustion gas of the present invention, the ammonia diluting water is sprayed against the combustion gas, so that the reaction time between ammonia and nitrogen oxides in combustion gas can be lengthened. The nitrogen oxides in the exhaust gas can be significantly reduced, and the air pollution can be prevented, which is advantageous in terms of pollution control.
【図1】本発明の燃焼ガスの窒素酸化物低減方法を炉筒
煙管ボイラに適用した例を示す部分断面図である。FIG. 1 is a partial sectional view showing an example in which a method for reducing nitrogen oxides in combustion gas according to the present invention is applied to a flue tube boiler.
【図2】図1における炉筒煙管ボイラの構成要領を示す
斜視図である。2 is a perspective view showing a configuration procedure of a flue tube boiler in FIG. 1. FIG.
【図3】本発明の燃焼ガスの窒素酸化物低減方法を貫流
ボイラに適用した例を示す図である。FIG. 3 is a diagram showing an example in which the method for reducing nitrogen oxides in combustion gas of the present invention is applied to a once-through boiler.
【図4】燃焼ガス温度と窒素酸化物低減値との関係を示
すグラフである。FIG. 4 is a graph showing the relationship between combustion gas temperature and nitrogen oxide reduction value.
【図5】アンモニア稀釈水噴霧量と残存アンモニア量と
の関係を示すグラフである。FIG. 5 is a graph showing the relationship between the amount of ammonia diluted water spray and the amount of residual ammonia.
2 波形炉筒 3 第一煙管群 4 第二煙管群 8 後部煙室 10 燃焼ガス 11 ノズル 12 アンモニア稀釈水収納タンク 15 ポンプ 18 シール管 20 シールエア 2 Corrugated furnace tube 3 First smoke tube group 4 Second smoke tube group 8 Rear smoke chamber 10 Combustion gas 11 Nozzle 12 Ammonia diluted water storage tank 15 Pump 18 Seal tube 20 Seal air
Claims (1)
の位置に、燃焼ガスの流れに対向してアンモニア稀釈水
を噴射することを特徴とする燃焼ガスの窒素酸化物低減
方法。1. The temperature of the combustion gas is approximately 900 to 1000 ° C.
A method for reducing nitrogen oxides in combustion gas, characterized in that ammonia diluted water is injected to the position of, facing the flow of combustion gas.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3234154A JPH0549855A (en) | 1991-08-21 | 1991-08-21 | Method for decreasing nitrogen oxide of combustion gas |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3234154A JPH0549855A (en) | 1991-08-21 | 1991-08-21 | Method for decreasing nitrogen oxide of combustion gas |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH0549855A true JPH0549855A (en) | 1993-03-02 |
Family
ID=16966499
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP3234154A Pending JPH0549855A (en) | 1991-08-21 | 1991-08-21 | Method for decreasing nitrogen oxide of combustion gas |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0549855A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR100833307B1 (en) * | 2007-04-05 | 2008-05-28 | 박정봉 | Nitrogen Oxide Reduction Boiler |
-
1991
- 1991-08-21 JP JP3234154A patent/JPH0549855A/en active Pending
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR100833307B1 (en) * | 2007-04-05 | 2008-05-28 | 박정봉 | Nitrogen Oxide Reduction Boiler |
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