JPS6148042B2 - - Google Patents
Info
- Publication number
- JPS6148042B2 JPS6148042B2 JP52119944A JP11994477A JPS6148042B2 JP S6148042 B2 JPS6148042 B2 JP S6148042B2 JP 52119944 A JP52119944 A JP 52119944A JP 11994477 A JP11994477 A JP 11994477A JP S6148042 B2 JPS6148042 B2 JP S6148042B2
- Authority
- JP
- Japan
- Prior art keywords
- fluidized bed
- nitrogen oxides
- coal
- combustion
- combustion 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
Links
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 claims description 72
- 239000003245 coal Substances 0.000 claims description 25
- 238000002485 combustion reaction Methods 0.000 claims description 22
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 14
- 229910052799 carbon Inorganic materials 0.000 claims description 14
- 238000000034 method Methods 0.000 claims description 14
- 239000000567 combustion gas Substances 0.000 claims description 6
- 229910017464 nitrogen compound Inorganic materials 0.000 claims description 3
- 150000002830 nitrogen compounds Chemical class 0.000 claims description 3
- 238000010438 heat treatment Methods 0.000 claims 1
- 239000007789 gas Substances 0.000 description 17
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 6
- 239000002245 particle Substances 0.000 description 5
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 4
- 239000000446 fuel Substances 0.000 description 4
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 3
- 241000766026 Coregonus nasus Species 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
- 239000000126 substance Substances 0.000 description 3
- 229910002091 carbon monoxide Inorganic materials 0.000 description 2
- 229910001873 dinitrogen Inorganic materials 0.000 description 2
- 239000003546 flue gas Substances 0.000 description 2
- 239000001257 hydrogen Substances 0.000 description 2
- 229910052739 hydrogen Inorganic materials 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 238000006722 reduction reaction Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- XFXPMWWXUTWYJX-UHFFFAOYSA-N Cyanide Chemical compound N#[C-] XFXPMWWXUTWYJX-UHFFFAOYSA-N 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- 235000019738 Limestone Nutrition 0.000 description 1
- 244000292604 Salvia columbariae Species 0.000 description 1
- 235000012377 Salvia columbariae var. columbariae Nutrition 0.000 description 1
- 235000001498 Salvia hispanica Nutrition 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 239000012752 auxiliary agent Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 235000014167 chia Nutrition 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000010574 gas phase reaction Methods 0.000 description 1
- 150000002431 hydrogen Chemical class 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 239000011343 solid material Substances 0.000 description 1
- 239000004449 solid propellant Substances 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
- 229910052815 sulfur oxide Inorganic materials 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
Description
本発明は石炭燃焼器からの排ガス等窒素酸化物
を含有するガスからの窒素酸化物低減法に係り、
特に、固体燃料ないしはこれに準ずる炭素含有物
質を用いて効果的に排ガスから窒素酸化物を低減
させる方法に関する。
従来、石炭燃焼器の排ガス等から窒素酸化物を
低減・除去する方法としては、燃焼に要する空気
等の酸素含有ガスの低下・分散供給、及び燃料供
給方法の改良などにより燃焼領域の温度を均一化
したり最高温度を低下させ窒素酸化物の発生その
ものを低減させる燃焼制御法、発生した窒素酸化
物を気相反応・溶液吸収などにより排ガス中より
取り除く排煙脱硝法、及び両者を組合わせた方法
などが用いられてきた。燃焼制御法は主に気体・
液体の燃料を空気などの窒素ガスを含有するガス
を酸素源として用い燃焼した場合、火炎中の高温
領域で空気中等の窒素が窒素酸化物となる(言わ
ゆるサーマルNOx)のを抑制するのに効果的で
あるが、高い低減率が望めない、燃料中に含まれ
る窒素分から生成する窒素酸化物(言わゆるフユ
エルNOx)の抑制には効果が薄い等の欠点があ
る。
一方、排煙脱硝法は窒素酸化物の除去効果は高
いが新たな設備を要する、溶液(湿式)・アンモ
ニアガス(乾式)等の助剤が必要となるなど経費
がかさむ欠点がある。
本発明の目的は、石炭燃焼器排ガスを固体状の
炭素含有物質と接触させ排ガス中の窒素酸化物を
低減・除去すると同時に副生する低濃度の水素・
一酸化炭素・メタンなどの可燃性ガスを再燃焼さ
せ、排ガス中の窒素酸化物を経済的に低減・除去
することにある。
本発明は、石炭燃焼ガスを400℃以上の温度で
窒素酸化物が炭素により効果的に窒素ガスに還元
される原理を応用したもので、上記炭素源として
石炭を用いた場合に上記還元反応と同時に石炭中
の揮発分が一部乾留されてガス中に混合され、こ
の揮発分中に含まれるアンモニア−シアンなどの
窒素化合物が後の再燃焼過程で新たに窒素酸化物
生成の原因となつていることをつきとめ、上記炭
素源からの窒素化合物の発生を低減することによ
り全体として高い窒素酸化物除去率を実現しよう
とするものである。具体的には、炭素源として予
め乾留した炭素含有固体状物質を用いることにあ
る。
以下本発明の一実施例を図面に基いて説明す
る。
図は本発明の一実施例を示すもので、塔径50mm
φの流動層を用いた石炭の燃焼に応用した例であ
る。石炭供給管2より第1表(A)の性状を持つ
石炭を燃焼用流動層1に供給し、一方、空気導入
管5から供給された空気は分散器4により燃焼用
流動層1内に均一に分散され層内の石炭粒子を流
動化すると同時に石炭の燃焼に必要な酸素源とな
る。流動状態を円滑にするため燃焼用流動層1内
には石炭のほかに反応上不活性なアルミナ粒子等
を充填しておくこともできる。定常的な運転では
上記不活性粒子は石炭の燃焼で生成する灰分で置
き換えられる。さらには、適当な粒径に破砕した
石灰石等を用いることにより、燃焼により生成す
る硫黄酸化物を燃焼用流動層1内で除去させるこ
とも可能である。
The present invention relates to a method for reducing nitrogen oxides from gas containing nitrogen oxides such as exhaust gas from a coal combustor,
In particular, the present invention relates to a method of effectively reducing nitrogen oxides from exhaust gas using solid fuel or a carbon-containing substance similar thereto. Conventionally, methods for reducing and removing nitrogen oxides from the exhaust gas of coal combustors include reducing and distributing the supply of oxygen-containing gas such as air required for combustion, and improving fuel supply methods to maintain a uniform temperature in the combustion area. Combustion control methods that reduce the generation of nitrogen oxides by lowering the maximum temperature and reducing the maximum temperature, flue gas denitrification methods that remove generated nitrogen oxides from exhaust gas by gas phase reaction or solution absorption, and methods that combine the two. etc. have been used. Combustion control methods are mainly used for gases and
When liquid fuel is burned using a gas containing nitrogen gas such as air as an oxygen source, it is possible to suppress the nitrogen in the air from turning into nitrogen oxides (so-called thermal NOx) in the high temperature region of the flame. Although it is effective, it has drawbacks such as a high reduction rate cannot be expected and it is not very effective in suppressing nitrogen oxides (so-called fuel NOx) generated from nitrogen contained in fuel. On the other hand, the flue gas denitrification method is highly effective in removing nitrogen oxides, but has the disadvantage of being expensive, such as requiring new equipment and auxiliary agents such as a solution (wet method) or ammonia gas (dry method). The purpose of the present invention is to bring coal combustor exhaust gas into contact with solid carbon-containing substances to reduce and remove nitrogen oxides from the exhaust gas, and at the same time to reduce and remove the low concentration of hydrogen and by-products.
The aim is to re-burn flammable gases such as carbon monoxide and methane to economically reduce and remove nitrogen oxides from exhaust gas. The present invention applies the principle that nitrogen oxides are effectively reduced to nitrogen gas by carbon at a temperature of 400°C or higher in coal combustion gas, and when coal is used as the carbon source, the above reduction reaction occurs. At the same time, some of the volatile content in the coal is carbonized and mixed into the gas, and nitrogen compounds such as ammonia and cyanide contained in this volatile content become a new cause of nitrogen oxide formation during the subsequent reburning process. The objective is to realize a high overall nitrogen oxide removal rate by reducing the generation of nitrogen compounds from the carbon source. Specifically, a carbon-containing solid substance that has been carbonized in advance is used as a carbon source. An embodiment of the present invention will be described below with reference to the drawings. The figure shows an example of the present invention, with a column diameter of 50 mm.
This is an example of application to coal combustion using a fluidized bed of φ. Coal having the properties shown in Table 1 (A) is supplied from the coal supply pipe 2 to the combustion fluidized bed 1, while air supplied from the air introduction pipe 5 is uniformly distributed within the combustion fluidized bed 1 by the disperser 4. It is dispersed in the coal particles and fluidizes the coal particles in the bed, and at the same time serves as a source of oxygen necessary for coal combustion. In order to maintain a smooth fluidized state, the combustion fluidized bed 1 may be filled with reactively inactive alumina particles in addition to coal. In steady-state operation, the inert particles are replaced by ash produced from the combustion of coal. Furthermore, it is also possible to remove sulfur oxides generated by combustion within the combustion fluidized bed 1 by using limestone or the like crushed to an appropriate particle size.
【表】
燃焼により生成する灰分は溢流管3より取り出
され燃焼用流動層1の層高はほぼ一定に保たれ
る。炭素質供給管7からは第1表予め乾留した炭
素含有固体状物質として(B)の性状を持つ石炭
乾留チヤーを供給し脱硝用流動層6を形成させ
る。燃焼用流動層1からの燃焼排ガスは分散器9
により脱硝用流動層6内に均一に分散され、ここ
でチヤーと反応した窒素酸化物を除去する。本実
施例では脱硝用流動層6の層高を保持するため、
溢流管8を設け余剰のチヤーを系外に取り出した
が、溢流管8の出口は燃焼用流動層1内に導入し
てもよく、更には、分散器9の開孔比・穴径を適
当な値に選びチヤーを分散器9の開孔部から燃焼
用流動層1に落下させ炭素質供給管7からのチヤ
ー供給速度を調整することにより脱硝用流動層6
の層高がほぼ一定に保持できれば、溢流管8は省
略してもよい。脱硝用流動層6を通過したガスに
は微量の水素・一酸化炭素・メタン等の可燃性成
分が含まれるため二次空気導入管10より上記可
燃性成分を燃焼するに十分な量の空気を供給し、
二次空気分散器11によりフリーボード12に均
一に分散させる。脱硝用流動層6を出た可燃性成
分を含むガスはフリーボード12内を上昇する間
に上記二次空気により燃焼され、排気管13より
系外に排気される。石炭供給管2からの石炭供給
量55g/h、空気導入管5からの空気供給量
400Nl/h、炭素質供給管7からのチヤー供給量
10g/h、燃焼用流動層1及び脱硝用流動層6の
温度を1,000℃に保ち、二次空気導入管10か
らの約300℃に余熱した空気の流量を変化させ、
分散器9直下及び排気管13出口でサンプリング
したガスの分析結果を第2表に示す。[Table] The ash produced by combustion is taken out from the overflow pipe 3, and the bed height of the combustion fluidized bed 1 is kept almost constant. From the carbonaceous supply pipe 7, carbonized coal coal having the properties shown in (B) as a carbon-containing solid material previously carbonized in Table 1 is supplied to form a fluidized bed 6 for denitrification. The combustion exhaust gas from the combustion fluidized bed 1 is sent to the disperser 9
The nitrogen oxides are uniformly dispersed in the denitrification fluidized bed 6, and the nitrogen oxides that have reacted with the char are removed there. In this embodiment, in order to maintain the bed height of the denitrification fluidized bed 6,
Although the overflow pipe 8 was provided to take out the excess chia out of the system, the outlet of the overflow pipe 8 may be introduced into the combustion fluidized bed 1. The denitrification fluidized bed 6 is selected by selecting an appropriate value and dropping the chires from the openings of the disperser 9 into the combustion fluidized bed 1, and adjusting the speed of supplying the chires from the carbonaceous supply pipe 7.
The overflow pipe 8 may be omitted if the bed height can be maintained substantially constant. Since the gas that has passed through the denitrification fluidized bed 6 contains trace amounts of flammable components such as hydrogen, carbon monoxide, and methane, a sufficient amount of air is introduced from the secondary air introduction pipe 10 to burn off the combustible components. supply,
The secondary air distributor 11 distributes the air uniformly onto the freeboard 12. The gas containing combustible components leaving the denitrification fluidized bed 6 is burned by the secondary air while rising within the freeboard 12 and is exhausted to the outside of the system through the exhaust pipe 13. Coal supply amount from coal supply pipe 2 55g/h, air supply amount from air introduction pipe 5
400Nl/h, amount of chir supplied from carbonaceous supply pipe 7
10g/h, keeping the temperature of the combustion fluidized bed 1 and the denitrification fluidized bed 6 at 1,000°C, and changing the flow rate of air preheated to about 300°C from the secondary air introduction pipe 10,
Table 2 shows the analysis results of the gas sampled directly below the disperser 9 and at the outlet of the exhaust pipe 13.
【表】
比較のため、実施例1と同じ装置を用いて、炭
素質供給管7から第1表(A)の石炭を10g/h
で供給して同様な実験を行つたところ、第3表の
結果を得た。[Table] For comparison, using the same equipment as in Example 1, 10 g/h of the coal shown in Table 1 (A) was fed from the carbonaceous supply pipe 7.
When a similar experiment was carried out by supplying the same, the results shown in Table 3 were obtained.
【表】
本発明によれば、窒素酸化物低減後の再燃焼で
新たな窒素酸化物の生成を防止でき、全体として
高い窒素酸化物除去率の維持が可能となる。[Table] According to the present invention, it is possible to prevent the generation of new nitrogen oxides through re-combustion after reducing nitrogen oxides, and it is possible to maintain a high nitrogen oxide removal rate as a whole.
図は本発明の一実施例の様態を示した図であ
る。
1……燃焼用流動層、2……石炭供給管、3,
8……溢流管、4,9……分散器、5……空気導
入管、6……脱硝用流動層、7……炭素質供給
管、10……二次空気導入管、11……二次空気
分散器、12……フリーボード、13……排気
管。
The figure is a diagram showing an aspect of an embodiment of the present invention. 1...Fluidized bed for combustion, 2...Coal supply pipe, 3,
8... Overflow pipe, 4,9... Distributor, 5... Air introduction pipe, 6... Fluidized bed for denitrification, 7... Carbonaceous supply pipe, 10... Secondary air introduction pipe, 11... Secondary air distributor, 12...freeboard, 13...exhaust pipe.
Claims (1)
化物を含有する高温の石炭燃焼ガスを、前記流動
層上に設けられた粒状炭素中に導入して該粒状炭
素の流動層を形成させるとともに前記粒状炭素の
流動層の温度を400℃以上に保持して前記燃焼ガ
ス中の窒素酸化物濃度を低減し、かつ、前記粒状
炭素の流動層上に設けられた空気分散器より前記
流動層より出て来た可燃性成分を含む高温の前記
石炭燃焼ガス中に空気を供給し、燃焼除去する方
法であつて、前記粒状炭素として予め乾留して揮
発性成分中の窒素酸化物に変化し得る窒素化合物
を少なくした炭素を用い、前記流動層の層高さを
一定の値に保持しながら前記石炭を燃焼させ加熱
源に利用することを特徴とする石炭燃焼ガスの窒
素酸化物の低減方法。1. Introducing high-temperature coal combustion gas containing nitrogen oxides produced by a fluidized bed for coal combustion into the granular carbon provided on the fluidized bed to form a fluidized bed of the granular carbon, and The temperature of the fluidized bed of granular carbon is maintained at 400° C. or higher to reduce the concentration of nitrogen oxides in the combustion gas, and the temperature of the fluidized bed of granular carbon is maintained at 400° C. or higher to reduce the concentration of nitrogen oxides in the combustion gas, and A method of supplying air to the hot coal combustion gas containing combustible components that has come out and burning and removing it, which can be carbonized in advance as the granular carbon and converted into nitrogen oxides among the volatile components. A method for reducing nitrogen oxides in coal combustion gas, characterized by using carbon with reduced nitrogen compounds and burning the coal while maintaining the bed height of the fluidized bed at a constant value and using it as a heating source.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP11994477A JPS5453667A (en) | 1977-10-07 | 1977-10-07 | Decreasing method for nitrogen oxides with carbon |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP11994477A JPS5453667A (en) | 1977-10-07 | 1977-10-07 | Decreasing method for nitrogen oxides with carbon |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5453667A JPS5453667A (en) | 1979-04-27 |
| JPS6148042B2 true JPS6148042B2 (en) | 1986-10-22 |
Family
ID=14774030
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP11994477A Granted JPS5453667A (en) | 1977-10-07 | 1977-10-07 | Decreasing method for nitrogen oxides with carbon |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5453667A (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6138618A (en) * | 1984-07-31 | 1986-02-24 | Asahi Cokes Kogyo Kk | Treatment of waste gas |
| JPS6164318A (en) * | 1984-09-07 | 1986-04-02 | Asahi Cokes Kogyo Kk | Treatment of gas |
| CN105003911B (en) * | 2015-08-05 | 2017-06-16 | 冯之军 | The nitric oxide production device of removing in a kind of biomass combustion furnace and stove |
| CN105833682B (en) * | 2016-04-21 | 2018-07-27 | 成都华西堂环保科技有限公司 | A kind of boiler air classification low nitrogen burning and denitrating technique |
-
1977
- 1977-10-07 JP JP11994477A patent/JPS5453667A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5453667A (en) | 1979-04-27 |
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