JPH0159489B2 - - Google Patents
Info
- Publication number
- JPH0159489B2 JPH0159489B2 JP57076955A JP7695582A JPH0159489B2 JP H0159489 B2 JPH0159489 B2 JP H0159489B2 JP 57076955 A JP57076955 A JP 57076955A JP 7695582 A JP7695582 A JP 7695582A JP H0159489 B2 JPH0159489 B2 JP H0159489B2
- Authority
- JP
- Japan
- Prior art keywords
- furnace
- combustion
- desulfurization
- air
- supplied
- 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
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23C—METHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN A CARRIER GAS OR AIR
- F23C6/00—Combustion apparatus characterised by the combination of two or more combustion chambers or combustion zones, e.g. for staged combustion
- F23C6/04—Combustion apparatus characterised by the combination of two or more combustion chambers or combustion zones, e.g. for staged combustion in series connection
- F23C6/045—Combustion apparatus characterised by the combination of two or more combustion chambers or combustion zones, e.g. for staged combustion in series connection with staged combustion in a single enclosure
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Combustion & Propulsion (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Incineration Of Waste (AREA)
Description
【発明の詳細な説明】
この発明は固体燃焼炉における炉内脱硫法に関
する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an in-furnace desulfurization method in a solid combustion furnace.
硫黄分を含有する燃料の燃焼に伴つて発生する
硫黄酸化物(以下SOxと称する)は、公害の原因
物質であるため、これを効果的に除去する方法が
要望せられ、従来多くのSOx除去技術が提案ない
し実用化されている。しかしこれらの方法はいず
れも液体ないし気体燃料を対象としたものである
ため、固体燃焼炉からの排ガスのように多量のダ
ストを含んだ排ガスの脱硫に適用すると、ダスト
による脱硫装置の閉塞や脱硫率の低下などの問題
をまねいた。そこでこの問題の解決策として、石
灰石、消石灰、ドロマイトなどの固形のSOx吸収
剤を火炉内へ直接噴射する乾式炉内脱硫法が提案
された。しかしこの方法では高温の酸化雰囲気中
へ吸収剤を直接供給するため、SOxの吸収が悪
く、その結果吸収剤を多量必要とする欠点があつ
た。 Sulfur oxides (hereinafter referred to as SOx) generated when sulfur-containing fuel is burned are a substance that causes pollution, so there is a need for a method to effectively remove them. A technology has been proposed or put into practical use. However, all of these methods target liquid or gaseous fuels, so when applied to the desulfurization of exhaust gas that contains a large amount of dust, such as exhaust gas from a solid combustion furnace, the desulfurization equipment may be clogged with dust or desulfurization may occur. This led to problems such as a decline in the rate. As a solution to this problem, a dry in-furnace desulfurization method was proposed in which a solid SOx absorbent such as limestone, slaked lime, or dolomite is directly injected into the furnace. However, this method has the disadvantage that SOx absorption is poor because the absorbent is directly supplied into the high-temperature oxidizing atmosphere, and as a result, a large amount of absorbent is required.
本発明者らは、従来の炉内脱硫の効率が悪い原
因について検討を行なつたところ、つぎのような
知見を得た。すなわち、通常の火炉内雰囲気のよ
うに、酸化雰囲気ではあるが酸素濃度が1〜5%
以下と非常に低い場合、900℃程度の温度では
Na2O+SO2+1/2O2→Na2SO4 …(1)
CaO+SO2+1/2O2→CaSO4 …(2)
などの硫酸塩生成反応が起こりにくい。これに対
し、還元雰囲気では、900〜1300℃の高温域で
Na2O+H2S→Na2S+H2O …(3)
CaO+H2S→CaS+H2O …(4)
CaO+COS→CaS+CO2 …(5)
CaSO4+4CO→CaS+4CO2 …(6)
Na2O+SO2+3C→Na2S+3CO …(7)
などの硫化物生成反応が主となり、Na2SO4,
CaSO4などの硫酸塩よりNa2S,CaSなどの硫化
物の方が安定であることがわかつた。したがつて
Na2S,CaSなどの硫化物の生成量を増すには、
反応式(3)(4)(5)(6)(7)の平衡を右にかたよらせればよ
く、そのためには900〜1300℃の温度域において
還元性ガスであるH2S,COS,COなどのガス濃
度を高くし、かつ還元領域へ脱硫剤を供給してや
るのがよいことがわかる。 The present inventors investigated the cause of the poor efficiency of conventional in-furnace desulfurization and obtained the following knowledge. In other words, it is an oxidizing atmosphere like the atmosphere inside a normal furnace, but the oxygen concentration is 1 to 5%.
If the temperature is very low, below 900°C, sulfate producing reactions such as Na 2 O + SO 2 + 1/2O 2 →Na 2 SO 4 …(1) CaO+SO 2 +1/2O 2 →CaSO 4 …(2) occur. Hard to happen. On the other hand, in a reducing atmosphere, Na 2 O + H 2 S → Na 2 S + H 2 O ... (3) CaO + H 2 S → CaS + H 2 O ... (4) CaO + COS → CaS + CO 2 ... (5) CaSO 4 +4CO→CaS+4CO 2 …(6) Na 2 O+SO 2 +3C→Na 2 S+3CO …(7) The main sulfide-producing reactions are Na 2 SO 4 ,
It was found that sulfides such as Na 2 S and CaS are more stable than sulfates such as CaSO 4 . Therefore
To increase the amount of sulfides produced such as Na 2 S and CaS,
It is only necessary to shift the equilibrium of reaction equations (3)(4)(5)(6)(7) to the right, and to do so, the reducing gases H 2 S, COS, CO It can be seen that it is better to increase the concentration of such gases and to supply the desulfurization agent to the reduction region.
この発明は上記のような知見に基づいてなされ
たものであつて、ダストを高濃度で含む固体燃料
燃焼排ガスに対して適用した場合も、脱硫を効率
よく行なうことのできる脱硫法を提供することを
目的とする。 The present invention has been made based on the above findings, and an object of the present invention is to provide a desulfurization method that can efficiently desulfurize even when applied to solid fuel combustion exhaust gas containing a high concentration of dust. With the goal.
なお、以下の説明において、空気比とは、燃焼
に要する理論空気量に対する実際の空気量の割合
をいい、前後方向については、第1図を基準とし
て、その左方を前方、またその右方を後方と称す
ることとする。 In the following explanation, the air ratio refers to the ratio of the actual amount of air to the theoretical amount of air required for combustion, and with respect to the front-rear direction, the left side is the front, and the right side is the front, with reference to Figure 1. is referred to as the rear.
この発明による脱硫法は、燃焼用空気を2分割
して炉内に供給する空気2段燃焼法において、燃
焼用2次空気供給口より上流に形成された還元雰
囲気の1次燃焼域へアルカリ化合物またはアルカ
リ土類化合物よりなる無機脱硫剤を供給して、1
次燃焼域の温度範囲を900〜1300℃とし、生成し
た還元性硫黄化合物を硫化物の形態で吸収除去す
るすることを特徴とする。 The desulfurization method according to the present invention is a two-stage combustion method in which combustion air is divided into two parts and supplied into the furnace. Alternatively, by supplying an inorganic desulfurization agent made of an alkaline earth compound,
The temperature range of the next combustion zone is 900 to 1300°C, and the generated reducing sulfur compounds are absorbed and removed in the form of sulfides.
空気2段燃焼法は、前壁に設けたバーナから炉
内へ、粉末燃料とこれを送るための燃料輸送用空
気とを供給し、燃焼用空気を2分割して炉内へ供
給し、燃焼用2次空気供給口より上流側に還元雰
囲気の1次燃焼域を形成するとともに、同供給口
より下流側に2次燃焼域を形成する燃焼法であ
る。 In the air two-stage combustion method, powdered fuel and air for transporting the fuel are supplied into the furnace from a burner installed on the front wall, and the combustion air is divided into two parts and supplied into the furnace to start combustion. This is a combustion method in which a primary combustion zone with a reducing atmosphere is formed upstream of a secondary air supply port, and a secondary combustion zone is formed downstream of the same supply port.
1次燃焼域への脱硫剤の供給は、燃焼用1次空
気供給口と同2次空気供給口の間において炉壁に
設けられた脱硫剤供給口によつて行なわれる。 The desulfurization agent is supplied to the primary combustion zone through a desulfurization agent supply port provided in the furnace wall between the primary combustion air supply port and the secondary air supply port.
燃料としては石炭を微粉化した微粉炭がよく用
いられる。また脱硫剤としては、Na2CO3,
CaCO3,Ca(OH)2、ドロマイトなどのアルカリ
がよく用いられる。 Pulverized coal, which is made by pulverizing coal, is often used as a fuel. In addition, as a desulfurizing agent, Na 2 CO 3 ,
Alkali such as CaCO 3 , Ca(OH) 2 and dolomite are often used.
まず、この発明において使用する燃焼炉の構造
について説明する。 First, the structure of the combustion furnace used in this invention will be explained.
第1図において、1は吸熱用ジヤケツトを有す
る円筒状周壁2とその両端に設けられた前壁3と
後壁4とからなる炉本体、5は前壁3の中央にあ
けられた開口で、前方突出状の燃焼用1次空気供
給口6を有する。7は燃焼用1次空気供給口6の
中心部に炉内向きに配されたバーナで、ここから
微粉炭と燃料輸送用空気の混合物が供給される。
8は前壁3の前面に設けられた風箱で、燃焼用1
次空気供給口6を介して炉内に通じている。9は
周壁2の長さの中央からやや後壁寄りに設けられ
た複数の燃焼用2次空気ノズル、10は燃焼用2
次空気ノズル9より上流側において周壁2に設け
られた複数の脱硫剤ノズル、11は周壁2の後端
部に設けられた煙道である。 In FIG. 1, 1 is a furnace body consisting of a cylindrical peripheral wall 2 having a heat absorbing jacket, a front wall 3 and a rear wall 4 provided at both ends thereof, 5 is an opening made in the center of the front wall 3, It has a combustion primary air supply port 6 projecting forward. Reference numeral 7 denotes a burner arranged in the center of the primary combustion air supply port 6 toward the inside of the furnace, from which a mixture of pulverized coal and air for fuel transportation is supplied.
8 is a wind box installed in front of the front wall 3, which is used for combustion.
It communicates with the inside of the furnace via the secondary air supply port 6. 9 is a plurality of combustion secondary air nozzles provided slightly closer to the rear wall from the center of the length of the peripheral wall 2; 10 is a combustion secondary air nozzle;
A plurality of desulfurizing agent nozzles are provided on the peripheral wall 2 on the upstream side of the secondary air nozzle 9, and 11 is a flue provided at the rear end of the peripheral wall 2.
上記構造の燃焼炉において、バーナ7から炉内
へ微粉炭と燃料輸送用空気の混合物を供給する。
さらに風箱8から炉内へ燃焼用1次空気を供給
し、空気比を1.0以下にする。 In the combustion furnace having the above structure, a mixture of pulverized coal and air for fuel transportation is supplied from the burner 7 into the furnace.
Furthermore, primary air for combustion is supplied from the wind box 8 into the furnace to reduce the air ratio to 1.0 or less.
またノズル9から炉内へ実質的に理論量の燃焼
用2次空気を供給する。この結果ノズル9より上
流側に1次燃焼域aが形成されるとともに、ノズ
ル9より下流側に2次燃焼域bが形成される。1
次燃焼域aは温度900〜1300℃の還元雰囲気であ
るので、炉内脱硫を行なうには最適条件を備えて
いる。そこでノズル10から脱硫剤を炉内に供給
し、効果的に炉内脱硫を行なう。 Further, a substantially stoichiometric amount of secondary air for combustion is supplied into the furnace from the nozzle 9. As a result, a primary combustion area a is formed upstream of the nozzle 9, and a secondary combustion area b is formed downstream of the nozzle 9. 1
Since the secondary combustion zone a is a reducing atmosphere with a temperature of 900 to 1300°C, it has optimal conditions for in-furnace desulfurization. Therefore, a desulfurizing agent is supplied into the furnace from the nozzle 10 to effectively perform desulfurization in the furnace.
第2図は燃焼炉の変形を示すものである。この
炉21は箱形の大型垂直炉であつて、前壁22の
下端部に第1図の燃焼炉のものと同じ構造の燃焼
用1次空気供給口23とバーナ24と風箱25が
設けられ、バーナ24から微粉炭と燃料輸送用空
気の混合物が供給され、風箱25から燃焼用1次
空気が供給される。またバーナ24の上方におい
て前壁22に燃焼用2次空気ノズル26が設けら
れ、同ノズル26とバーナ24の間において前壁
22に脱硫剤ノズル27が設けられている。そし
てこの場合も燃焼用2次空気ノズル26より上流
側に還元雰囲気の1次燃焼域cが形成されるとと
もに、ノズル26の下流側に2次燃焼域dが形成
される。そこでノズル27から1次燃焼域cに脱
硫剤を供給する。 FIG. 2 shows a modification of the combustion furnace. This furnace 21 is a box-shaped large vertical furnace, and the lower end of the front wall 22 is provided with a primary combustion air supply port 23, a burner 24, and a wind box 25, which have the same structure as the combustion furnace shown in FIG. A mixture of pulverized coal and air for fuel transportation is supplied from the burner 24, and primary air for combustion is supplied from the wind box 25. Further, a combustion secondary air nozzle 26 is provided on the front wall 22 above the burner 24, and a desulfurizing agent nozzle 27 is provided on the front wall 22 between the nozzle 26 and the burner 24. Also in this case, a primary combustion zone c of a reducing atmosphere is formed upstream of the secondary combustion air nozzle 26, and a secondary combustion zone d is formed downstream of the nozzle 26. Therefore, the desulfurizing agent is supplied from the nozzle 27 to the primary combustion zone c.
第3図は、この発明による空気2段燃焼法にお
ける脱硫法と、単段燃焼法における脱硫法との場
合について、酸素濃度3%、CaO/SO2および
NaO/SO2当量比それぞれ4における炉内温度と
脱硫率の関係を示すものである。同図から明らか
なように、この発明の脱硫法によれば、脱硫率を
大幅に向上させることができる。 Figure 3 shows the desulfurization method in the two-stage air combustion method and the desulfurization method in the single-stage combustion method according to the present invention at an oxygen concentration of 3%, CaO/SO 2 and
This figure shows the relationship between the furnace temperature and the desulfurization rate at a NaO/SO 2 equivalent ratio of 4. As is clear from the figure, according to the desulfurization method of the present invention, the desulfurization rate can be significantly improved.
この発明の炉内脱硫法によれば、1次燃焼域の
温度範囲を900〜1300℃とすることによつて、排
ガス中の硫黄化合物を還元性ガスであるH2S,
COSなどの硫黄化合物とし、この還元雰囲気の
1次燃焼域にアルカリ化合物またはアルカリ土類
化合物よりなる無機脱硫剤を供給することによつ
て、上記還元性硫黄化合物をNa2S,CaSなどの
硫化物の形態で吸収除去することができる。こう
して、この発明の脱硫法によれば、炉内で発生し
た硫黄化合物特にSOxを、硫酸塩に比べて安定の
よい硫化物として吸収除去することができる。 According to the in-furnace desulfurization method of this invention, by setting the temperature range of the primary combustion zone to 900 to 1300°C, sulfur compounds in the exhaust gas are converted to H 2 S, which is a reducing gas,
By supplying an inorganic desulfurization agent made of an alkali compound or an alkaline earth compound to the primary combustion zone of this reducing atmosphere, the reducing sulfur compound can be converted to sulfurization such as Na 2 S, CaS, etc. It can be absorbed and removed in the form of objects. Thus, according to the desulfurization method of the present invention, sulfur compounds, particularly SOx, generated in the furnace can be absorbed and removed as sulfides, which are more stable than sulfates.
第1図はこの発明の実施例を示す燃焼炉の垂直
縦断面図、第2図は変形例を示す炉前部の垂直断
面図、第3図は炉内温度と脱硫率の関係を示すグ
ラフである。
FIG. 1 is a vertical cross-sectional view of a combustion furnace showing an embodiment of the present invention, FIG. 2 is a vertical cross-sectional view of the front part of the furnace showing a modified example, and FIG. 3 is a graph showing the relationship between furnace temperature and desulfurization rate. It is.
Claims (1)
2段燃焼法において、燃焼用2次空気供給口より
上流側に形成された還元雰囲気の1次燃焼域にア
ルカリ化合物またはアルカリ土類化合物よりなる
無機脱硫剤を供給して、1次燃焼域の温度範囲を
900〜1300℃とし、生成した還元性硫黄化合物を
硫化物の形態で吸収除去することを特徴とする固
体燃焼炉における炉内脱硫法。1 In the air two-stage combustion method in which combustion air is divided into two and supplied into the furnace, alkaline compounds or alkaline earth compounds are added to the primary combustion zone of the reducing atmosphere formed upstream of the secondary combustion air supply port. By supplying an inorganic desulfurization agent consisting of
An in-furnace desulfurization method in a solid combustion furnace, characterized in that the temperature is 900 to 1300°C, and the generated reducing sulfur compounds are absorbed and removed in the form of sulfides.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7695582A JPS58193013A (en) | 1982-05-07 | 1982-05-07 | In-furnace desulfurization method in solid combustion furnace |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7695582A JPS58193013A (en) | 1982-05-07 | 1982-05-07 | In-furnace desulfurization method in solid combustion furnace |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS58193013A JPS58193013A (en) | 1983-11-10 |
| JPH0159489B2 true JPH0159489B2 (en) | 1989-12-18 |
Family
ID=13620196
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP7695582A Granted JPS58193013A (en) | 1982-05-07 | 1982-05-07 | In-furnace desulfurization method in solid combustion furnace |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS58193013A (en) |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6196318A (en) * | 1984-10-16 | 1986-05-15 | Hitachi Zosen Corp | Low NOx combustion method that simultaneously performs desulfurization |
| JPS6196319A (en) * | 1984-10-16 | 1986-05-15 | Hitachi Zosen Corp | Low NOx combustion method that simultaneously performs desulfurization |
| US5291841A (en) * | 1993-03-08 | 1994-03-08 | Dykema Owen W | Coal combustion process for SOx and NOx control |
| US6206685B1 (en) | 1999-08-31 | 2001-03-27 | Ge Energy And Environmental Research Corporation | Method for reducing NOx in combustion flue gas using metal-containing additives |
| CN116221738B (en) * | 2023-02-28 | 2025-12-19 | 东南大学 | Rotary kiln incinerator capable of desulfurizing in furnace and desulfurizing method |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5432834A (en) * | 1977-08-19 | 1979-03-10 | Mitsubishi Heavy Ind Ltd | Processing system for exhaust combustion gas |
| US4285283A (en) * | 1979-12-07 | 1981-08-25 | Exxon Research & Engineering Co. | Coal combustion process |
-
1982
- 1982-05-07 JP JP7695582A patent/JPS58193013A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS58193013A (en) | 1983-11-10 |
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