JPS6127645B2 - - Google Patents
Info
- Publication number
- JPS6127645B2 JPS6127645B2 JP57071978A JP7197882A JPS6127645B2 JP S6127645 B2 JPS6127645 B2 JP S6127645B2 JP 57071978 A JP57071978 A JP 57071978A JP 7197882 A JP7197882 A JP 7197882A JP S6127645 B2 JPS6127645 B2 JP S6127645B2
- Authority
- JP
- Japan
- Prior art keywords
- combustion chamber
- primary
- supplied
- secondary combustion
- 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
Links
- 238000002485 combustion reaction Methods 0.000 claims description 91
- 238000006477 desulfuration reaction Methods 0.000 claims description 22
- 230000023556 desulfurization Effects 0.000 claims description 22
- 239000000446 fuel Substances 0.000 claims description 17
- 238000000034 method Methods 0.000 claims description 15
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 claims description 13
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 10
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 claims description 9
- 239000003795 chemical substances by application Substances 0.000 claims description 9
- 238000009841 combustion method Methods 0.000 claims description 7
- 229910052717 sulfur Inorganic materials 0.000 claims description 5
- 239000011593 sulfur Substances 0.000 claims description 5
- 150000003568 thioethers Chemical class 0.000 claims description 5
- 230000003009 desulfurizing effect Effects 0.000 claims description 3
- 239000007789 gas Substances 0.000 description 21
- 238000006243 chemical reaction Methods 0.000 description 10
- 239000000567 combustion gas Substances 0.000 description 5
- 239000003513 alkali Substances 0.000 description 4
- RMAQACBXLXPBSY-UHFFFAOYSA-N silicic acid Chemical compound O[Si](O)(O)O RMAQACBXLXPBSY-UHFFFAOYSA-N 0.000 description 3
- 235000012239 silicon dioxide Nutrition 0.000 description 3
- 238000007796 conventional method Methods 0.000 description 2
- 238000005260 corrosion Methods 0.000 description 2
- 230000007797 corrosion Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 230000001590 oxidative effect Effects 0.000 description 2
- 230000002829 reductive effect Effects 0.000 description 2
- 150000004760 silicates Chemical class 0.000 description 2
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 1
- 230000002745 absorbent Effects 0.000 description 1
- 239000002250 absorbent Substances 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
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
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Combustion & Propulsion (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Combustion Of Fluid Fuel (AREA)
- Treating Waste Gases (AREA)
Description
【発明の詳細な説明】
本発明は三段燃焼法を用いた脱硫法に関する。
従来、灰分が多く含まれる燃料の燃焼排ガスを脱
硫する方法の一つに炉内へ直接アルカリを供給
し、脱酸塩、あるいは亜硫酸塩として除去する方
法があつた。しかしながらこの方法では炉内温度
が高くなるにしたがつて
CaO+SO2+1/2O2→CaSO4 …(1)
Na2O+SO2+1/2O2→Na2SO4 …(2)
等の反応が起こりにくくなり、第1図に示す炉内
温度と脱硫率の関係からも明らかなように、1000
℃以上の高温では脱硫率が低下するという問題が
あつた。一方、還元雰囲気においては、
CaO+H2S→CaS+H2O …(3)
Na2O+H2S→Na2S+H2O …(4)
Na2O+SO2+3C→Na2S+3CO …(5)
などの硫化物を生成する反応が主反応となり、こ
れらの反応によつて生成した硫化物は高温におい
ても安定である。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a desulfurization method using a three-stage combustion method.
Conventionally, one method for desulfurizing combustion exhaust gas from fuel containing a large amount of ash was to supply alkali directly into the furnace and remove it as salt removal or sulfite. However, with this method, as the temperature inside the furnace increases, reactions such as CaO + SO 2 +1/2O 2 →CaSO 4 ...(1) Na 2 O + SO 2 +1/2O 2 →Na 2 SO 4 ...(2) become less likely to occur. As is clear from the relationship between furnace temperature and desulfurization rate shown in Figure 1, 1000
There was a problem that the desulfurization rate decreased at high temperatures above ℃. On the other hand, in a reducing atmosphere, sulfides such as CaO+H 2 S→CaS+H 2 O…(3) Na 2 O+H 2 S→Na 2 S+H 2 O…(4) Na 2 O+SO 2 +3C→Na 2 S+3CO…(5) The main reaction is to produce , and the sulfides produced by these reactions are stable even at high temperatures.
そこで、空気二段燃焼法として知られている段
階燃焼法を用いて1次燃焼域を空気不足で還元燃
焼させ、この1次燃焼域へ還元剤を供給する方法
が考えられた。しかしながら、この方法では、1
次燃焼域で生成した硫化物の大部分は、過剰の空
気が供給され可燃分の完全燃焼が行なわれる2次
燃焼域以降で再び酸化され、捕捉したSを
CaO+3/2O2→CaO+SO2 …(6)
Na2S+3/2O2→NaO+SO2 …(7)
等の反応により放出するために、従来の脱硫法と
あまり差のない結果となつてしまうという問題が
あつた。 Therefore, a method has been devised in which a staged combustion method known as a two-stage air combustion method is used to carry out reductive combustion in the primary combustion zone in the absence of air, and a reducing agent is supplied to the primary combustion zone. However, in this method, 1
Most of the sulfides generated in the secondary combustion zone are oxidized again after the secondary combustion zone where excess air is supplied and combustibles are completely burned, and the captured S is converted into CaO+3/2O 2 →CaO+SO 2 ...( 6) Since it is released through reactions such as Na 2 S + 3/2O 2 →NaO + SO 2 (7), there was a problem that the results were not much different from conventional desulfurization methods.
また、灰分が多い場合においては、1次燃焼域
へ供給されるアルカリの多くは、Sとの反応以前
に灰分の主成分である珪酸と反応し、複雑な珪酸
塩化合物を作つてしまい脱硫効果は非常に低いも
のとなつてしまう場合が多いという問題もあつ
た。 Furthermore, when the ash content is high, most of the alkali supplied to the primary combustion zone reacts with silicic acid, which is the main component of the ash content, before reacting with S, creating complex silicate compounds and reducing the desulfurization effect. Another problem was that in many cases the value was very low.
本発明はこのような問題を解決することを目的
とし、燃料及び空気をそれぞれ分割供給する三段
燃焼法において、火炉を少なくとも1次燃焼室と
2次燃焼室に分割し、前記1次燃焼室を灰の流動
点以上の高温に保持して該1次燃焼室で1次燃料
を燃焼させ、これより灰を1次燃焼室から熔融状
態で取り出し、次に前記1次燃焼室の1次燃焼排
ガスを2次燃焼室へ供給し、該2次燃焼室で過剰
の2次燃料を供給して2次燃焼域を還元雰囲気に
保持しながら燃焼させるとともに脱硫剤を供給し
て脱硫を行い、これにより硫黄分を硫化物として
取り出し、次に2次燃焼排ガスをその後流から2
次空気を供給して3次燃焼させ該2次燃焼排ガス
中に含まれる未燃分を完全に燃焼、酸化させ、一
方前記2次燃焼室で生成した硫化物は炭酸化装置
に送つて炭酸塩とするとともに該炭酸塩を脱硫剤
として前記2次燃焼室へ供給して循環使用し、ま
た前記炭酸化装置内で発生したH2Sはクラウス炉
で単体硫黄として回収することを特徴とする三段
燃焼法を用いた脱硫法を提供することによつて、
その目的を達成するものであり、これにより従来
方法より燃焼排ガスの脱硫率を向上することがで
きるとともに脱硫剤の循環使用を可能にするプロ
セスを与えることができるものである。 The present invention aims to solve such problems, and in a three-stage combustion method in which fuel and air are separately supplied, the furnace is divided into at least a primary combustion chamber and a secondary combustion chamber, and the primary combustion chamber The primary fuel is combusted in the primary combustion chamber by maintaining the ash at a high temperature higher than the pour point of the ash, the ash is taken out in a molten state from the primary combustion chamber, and then the primary combustion in the primary combustion chamber is performed. Exhaust gas is supplied to a secondary combustion chamber, and in the secondary combustion chamber, excess secondary fuel is supplied to combust while maintaining the secondary combustion area in a reducing atmosphere, and a desulfurization agent is supplied to perform desulfurization. The sulfur content is extracted as sulfide, and then the secondary combustion exhaust gas is
Secondary air is supplied and tertiary combustion is performed to completely burn and oxidize the unburned components contained in the secondary combustion exhaust gas, while the sulfides generated in the secondary combustion chamber are sent to a carbonation device and converted into carbonate. At the same time, the carbonate is supplied as a desulfurization agent to the secondary combustion chamber for circulation use, and the H 2 S generated in the carbonation device is recovered as elemental sulfur in a Claus furnace. By providing a desulfurization method using a staged combustion method,
This objective is achieved by providing a process in which the desulfurization rate of combustion exhaust gas can be improved compared to conventional methods, and the desulfurization agent can be recycled.
以下本発明の方法をその一実施例を示す図面に
基づいて詳細に説明する。第2図において、1は
1次燃料2および1次空気3を供給されて1次燃
焼を行う1次燃焼室、4は該1次燃焼室1の1次
燃焼排ガス5を導入されるとともに2次燃料6お
よび脱硫剤として炭酸塩7を供給されて2次燃焼
を行う2次燃焼室8は該2次燃焼室4の2次燃焼
排ガス9を導入されるとともに2次空気10を供
給されて3次燃焼を行う3次燃焼室で、火炉はこ
れら1次燃焼室1、2次燃焼室4および3次燃焼
室8の三つに分割された燃焼室で形成されてい
る。11は前記3次燃焼室8の3次燃焼排ガス1
2を導入されて該3次燃焼排ガス12の2次処理
を行う例えば集塵装置、場合によつては脱硝装置
等の排ガス2次処理装置で、該排ガス2次処理装
置11を通過した燃焼ガス13は大気14へと放
出される。15は前記2次燃焼室4で炭酸塩7に
より生成された硫化物16を導入されて該硫化物
16を炭酸塩7に戻す炭酸化装置で、前記硫化物
16から灰分17も取り出し、内部にはH2S18
を発生する。該炭酸化装置15で得られた炭酸塩
7は前記2次燃焼室4へと循環される。19は炭
酸化装置15内で発生したH2S18を導入される
とともにO220を供給されて前記H2S18から単
体硫黄21を回収するクラウス炉で、SO2、H2O
を含んだ排ガス24は前記2次燃焼室4へと循環
される。 The method of the present invention will be explained in detail below based on the drawings showing one embodiment thereof. In FIG. 2, 1 is a primary combustion chamber that is supplied with primary fuel 2 and primary air 3 and performs primary combustion; 4 is a primary combustion chamber into which primary combustion exhaust gas 5 of the primary combustion chamber 1 is introduced; A secondary combustion chamber 8 is supplied with a secondary fuel 6 and a carbonate 7 as a desulfurizing agent and performs secondary combustion.The secondary combustion exhaust gas 9 of the secondary combustion chamber 4 is introduced into the secondary combustion chamber 8, and the secondary combustion chamber 8 is supplied with secondary air 10. A tertiary combustion chamber performs tertiary combustion, and the furnace is formed by three combustion chambers, a primary combustion chamber 1, a secondary combustion chamber 4, and a tertiary combustion chamber 8. 11 is the tertiary combustion exhaust gas 1 of the tertiary combustion chamber 8
The combustion gas that has passed through the exhaust gas secondary treatment device 11, such as a dust collector or, in some cases, a denitration device, which performs secondary treatment of the tertiary combustion exhaust gas 12 by introducing the 13 is released into the atmosphere 14. 15 is a carbonation device into which sulfide 16 generated from carbonate 7 is introduced in the secondary combustion chamber 4 and returns the sulfide 16 to carbonate 7; ash 17 is also taken out from the sulfide 16; is H 2 S18
occurs. The carbonate 7 obtained in the carbonation device 15 is circulated to the secondary combustion chamber 4. Reference numeral 19 denotes a Claus furnace into which H 2 S 18 generated in the carbonation device 15 is introduced and O 2 20 is supplied to recover elemental sulfur 21 from the H 2 S 18.
The exhaust gas 24 containing the above is circulated to the secondary combustion chamber 4.
係る構成で次に動作を述べる。先ず1次燃焼室
1へ1次燃料2と1次空気3を供給し、該1次燃
焼室1を灰分の流動点以上の高温に保持して1次
燃焼させる。これにより灰22を熔融状態で取り
出す。このとき1次空気3を1次燃料2の理論空
気量以上供給すると、1次燃焼室1内を酸化雰囲
気に保つて吸熱管等の腐食をさけることができ
る。次に前記1次燃焼室1の1次燃焼排ガス5を
2次燃焼室4へ導入し、また該2次燃焼室4へ過
剰の2次燃料6およびアルカリの炭酸塩
(CaCO3、Na2CO3等)7を供給して2次燃焼域
を還元雰囲気に保持しながら2次燃焼させる。こ
れにより硫黄分を硫化物16として取り出す。こ
の際、主な反応は、
CaCO3+H2O→CaS+CO2+H2O …(8)
Na2CO3+H2S→Na2S+CO2+H2O
…(9)
等である。なお2次燃料6として灰分の少ない燃
料を用いれば、炭酸塩7が灰中の珪酸によつて消
費されるのを大巾に減少することができ、反応の
促進を図ることができる。次に2次燃焼室4の2
次燃焼排ガス9を3次燃焼室8へと導入し、また
3次燃焼室8へ2次空気10を供給して3次燃焼
させる。これにより2次燃焼排ガス9中に含まれ
る未燃分を完全に燃焼、酸化させる。なお前述し
たように、該3次燃焼室8においても2次空気1
0を多量に供給して酸化雰囲気に保ちながら燃焼
させると、吸熱管等の腐食をさけることができ
る。次に3次燃焼室8の3次燃焼排ガス12を、
排ガス2次処理装置11に導入して、さらに3次
燃焼排ガス12を処理した後、燃焼ガス13とし
て大気14へ放出する。一方、前記2次燃焼室4
で生成した硫化物16は炭酸化装置15へ導入
し、該炭酸化装置15でスチーム23と燃焼ガス
13に接触させて炭酸塩7に戻す。なお燃焼ガス
13は、前記排ガス2次処理装置11から大気1
4に放出する燃焼ガス13の一部を炭酸化装置1
5に供給して有効利用するとよい。硫化物16が
炭酸塩7に戻る反応は、前記(8)式、(9)式の逆反応
による。炭酸化装置15で得られた炭酸塩7は2
次燃焼室4へ供給して、アルカリ吸収剤として循
環使用する。次に炭酸化装置15内で逆反応によ
り発生したH2S18はクラウス炉19へ導入し、
H2S+3/2O2→SO2+H2O …(10)
2H2S+SO2→3S+2H2O …(11)
の反応により単体硫黄21として回収する。 The operation of this configuration will be described next. First, primary fuel 2 and primary air 3 are supplied to primary combustion chamber 1, and primary combustion is performed while maintaining primary combustion chamber 1 at a high temperature higher than the pour point of ash. As a result, the ash 22 is taken out in a molten state. At this time, if the primary air 3 is supplied in an amount equal to or greater than the theoretical air amount of the primary fuel 2, the inside of the primary combustion chamber 1 can be maintained in an oxidizing atmosphere to avoid corrosion of the heat absorption pipes and the like. Next, the primary combustion exhaust gas 5 of the primary combustion chamber 1 is introduced into the secondary combustion chamber 4, and the excess secondary fuel 6 and alkali carbonates (CaCO 3 , Na 2 CO 3 , etc.) to perform secondary combustion while maintaining the secondary combustion area in a reducing atmosphere. As a result, sulfur content is extracted as sulfide 16. At this time, the main reactions are CaCO 3 +H 2 O→CaS+CO 2 +H 2 O (8) Na 2 CO 3 +H 2 S→Na 2 S+CO 2 +H 2 O (9), etc. Note that if a fuel with a low ash content is used as the secondary fuel 6, consumption of the carbonate 7 by silicic acid in the ash can be greatly reduced, and the reaction can be promoted. Next, 2 of secondary combustion chamber 4
The secondary combustion exhaust gas 9 is introduced into the tertiary combustion chamber 8, and the secondary air 10 is also supplied to the tertiary combustion chamber 8 for tertiary combustion. As a result, the unburned components contained in the secondary combustion exhaust gas 9 are completely combusted and oxidized. As mentioned above, the secondary air 1 is also in the tertiary combustion chamber 8.
If a large amount of 0 is supplied and burned while maintaining an oxidizing atmosphere, corrosion of the heat absorbing tubes etc. can be avoided. Next, the tertiary combustion exhaust gas 12 in the tertiary combustion chamber 8,
The tertiary combustion exhaust gas 12 is introduced into a secondary exhaust gas treatment device 11 and further treated, and then released into the atmosphere 14 as a combustion gas 13. On the other hand, the secondary combustion chamber 4
The sulfide 16 produced in is introduced into a carbonation device 15, where it is brought into contact with steam 23 and combustion gas 13 and returned to carbonate 7. The combustion gas 13 is transferred from the exhaust gas secondary treatment device 11 to the atmosphere 1.
A part of the combustion gas 13 to be released into the carbonator 1
It is recommended to supply it to 5 and make effective use of it. The reaction in which the sulfide 16 returns to the carbonate 7 is the reverse reaction of the above formulas (8) and (9). The carbonate 7 obtained in the carbonation device 15 is 2
It is supplied to the next combustion chamber 4 and used for circulation as an alkali absorbent. Next, H 2 S18 generated by the reverse reaction in the carbonation device 15 is introduced into the Claus furnace 19, and H 2 S + 3/2O 2 →SO 2 +H 2 O …(10) 2H 2 S+SO 2 →3S+2H 2 O …( 11) It is recovered as elemental sulfur 21 through the reaction.
以上本発明の方法によれば、炉内温度が高い場
合でも脱硫率を低下させることがなく、また一次
燃焼室に脱硫剤を供給しないので、灰の主成分で
ある珪酸と脱硫剤を反応させて複雑な珪酸塩の化
合物を造つてしまい脱硫効果を少なくするという
ことがなく、従来方法より燃焼排ガスの脱硫率を
向上することができる。しかも2次燃焼室から取
り出される硫黄分を単体硫黄として回収しまた脱
硫剤の循環使用を可能にするプロセスを与えるこ
とができるものである。 As described above, according to the method of the present invention, the desulfurization rate does not decrease even when the temperature inside the furnace is high, and since the desulfurization agent is not supplied to the primary combustion chamber, the desulfurization agent is reacted with silicic acid, which is the main component of the ash. This method does not reduce the desulfurization effect due to the production of complex silicate compounds, and the desulfurization rate of combustion exhaust gas can be improved compared to conventional methods. Moreover, it is possible to provide a process in which the sulfur content taken out from the secondary combustion chamber is recovered as elemental sulfur, and the desulfurization agent can be recycled.
第1図は従来の脱硫法による炉内温度と脱硫率
の関係をあらわす図、第2図は本発明に係る方法
の一実施例を示すフロシート図である。
1……1次燃焼室、2……1次燃料、4……2
次燃料室、5……1次燃焼排ガス、6……2次燃
料、7……炭酸塩、8……3次燃焼室、9……2
次燃焼排ガス、10……2次空気、15……炭酸
化装置、16……硫化物、17……灰分、18…
…H2S、19……クラウス炉、21……単体硫
黄。
FIG. 1 is a diagram showing the relationship between furnace temperature and desulfurization rate in a conventional desulfurization method, and FIG. 2 is a flow sheet diagram showing an embodiment of the method according to the present invention. 1...Primary combustion chamber, 2...Primary fuel, 4...2
Secondary fuel chamber, 5... Primary combustion exhaust gas, 6... Secondary fuel, 7... Carbonate, 8... Tertiary combustion chamber, 9... 2
Secondary combustion exhaust gas, 10... Secondary air, 15... Carbonation device, 16... Sulfide, 17... Ash content, 18...
...H 2 S, 19...Klaus reactor, 21...Elementary sulfur.
Claims (1)
焼法において、火炉を少なくとも1次燃焼室と2
次燃焼室に分割し、前記1次燃焼室を灰の流動点
以上の高温に保持して該1次燃焼室で1次燃料を
燃焼させ、これにより灰を1次燃焼室から熔融状
態で取り出し、次に前記1次燃焼室の1次燃焼排
ガスを2次燃焼室へ供給し、該2次燃焼室で過剰
の2次燃料を供給して2次燃焼域を還元雰囲気に
保持しながら燃焼させるとともに脱硫剤を供給し
て脱硫を行い、これにより硫黄分を硫化物として
取り出し、次に2次燃焼排ガスをその後流から2
次空気を供給して3次燃焼させ該2次燃焼排ガス
中に含まれる未燃分を完全に燃焼、酸化させ、一
方前記2次燃焼室で生成した硫化物は炭酸化装置
に送つて炭酸塩とするとともに該炭酸塩を脱硫剤
として前記2次燃焼室へ供給して循環使用し、ま
た前記炭酸化装置内で発生したH2Sはクラウス炉
で単体硫黄として回収することを特徴とする三段
燃焼法を用いた脱硫法。1 In the three-stage combustion method where fuel and air are supplied separately, the furnace is divided into at least a primary combustion chamber and a secondary combustion chamber.
The primary combustion chamber is divided into secondary combustion chambers, the primary combustion chamber is maintained at a high temperature above the pour point of the ash, the primary fuel is combusted in the primary combustion chamber, and the ash is removed from the primary combustion chamber in a molten state. , Next, the primary combustion exhaust gas in the primary combustion chamber is supplied to a secondary combustion chamber, and in the secondary combustion chamber, excess secondary fuel is supplied and burned while maintaining the secondary combustion area in a reducing atmosphere. At the same time, a desulfurizing agent is supplied to perform desulfurization, thereby extracting the sulfur content as sulfide, and then removing the secondary combustion exhaust gas from its downstream side.
Secondary air is supplied and tertiary combustion is performed to completely burn and oxidize the unburned components contained in the secondary combustion exhaust gas, while the sulfides generated in the secondary combustion chamber are sent to a carbonation device and converted into carbonate. At the same time, the carbonate is supplied as a desulfurization agent to the secondary combustion chamber for circulation use, and the H 2 S generated in the carbonation device is recovered as elemental sulfur in a Claus furnace. Desulfurization method using staged combustion method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57071978A JPS58190606A (en) | 1982-04-28 | 1982-04-28 | Desulfurization using three-stage combustion |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57071978A JPS58190606A (en) | 1982-04-28 | 1982-04-28 | Desulfurization using three-stage combustion |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS58190606A JPS58190606A (en) | 1983-11-07 |
| JPS6127645B2 true JPS6127645B2 (en) | 1986-06-26 |
Family
ID=13476055
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57071978A Granted JPS58190606A (en) | 1982-04-28 | 1982-04-28 | Desulfurization using three-stage combustion |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS58190606A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2009030893A (en) * | 2007-07-27 | 2009-02-12 | Takuma Co Ltd | Combustion method for suppressing production of hexavalent chromium from chromium-containing fuel |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS61208412A (en) * | 1985-03-14 | 1986-09-16 | Hitachi Zosen Corp | Three-stage combustion method to suppress nox with simultaneous desulphurization |
| JPS61208411A (en) * | 1985-03-14 | 1986-09-16 | Hitachi Zosen Corp | Two-stage combustion method to suppress nox development with simultaneous desulphurization |
| EP0301714A3 (en) * | 1987-07-30 | 1989-07-19 | Trw Inc. | Sulfur removal by sorbent injection in secondary combustion zones |
-
1982
- 1982-04-28 JP JP57071978A patent/JPS58190606A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2009030893A (en) * | 2007-07-27 | 2009-02-12 | Takuma Co Ltd | Combustion method for suppressing production of hexavalent chromium from chromium-containing fuel |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS58190606A (en) | 1983-11-07 |
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