JPS6357095B2 - - Google Patents
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- Publication number
- JPS6357095B2 JPS6357095B2 JP55128804A JP12880480A JPS6357095B2 JP S6357095 B2 JPS6357095 B2 JP S6357095B2 JP 55128804 A JP55128804 A JP 55128804A JP 12880480 A JP12880480 A JP 12880480A JP S6357095 B2 JPS6357095 B2 JP S6357095B2
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- JP
- Japan
- Prior art keywords
- coal ash
- exhaust gas
- furnace
- temperature
- 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.)
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- Gasification And Melting Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Chimneys And Flues (AREA)
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は、石炭だきボイラ排ガスを高ダスト系
脱硝、空気予熱、低温集じんの順序で処理する方
法において、集じん装置捕集石炭灰中に含まれる
アンモニウム化合物および未燃カーボンを主成分
とする黒色石炭灰を効率よくかつ経済的に除去す
る石炭灰の処理方法に関するものである。[Detailed Description of the Invention] [Industrial Application Field] The present invention provides a method for treating coal-fired boiler exhaust gas in the order of high-dust denitrification, air preheating, and low-temperature dust collection. The present invention relates to a coal ash processing method that efficiently and economically removes black coal ash whose main components are ammonium compounds and unburned carbon contained in the coal ash.
石炭だきボイラ排ガスを技術的、経済的に優れ
た高ダスト系脱硝−空気予熱−低温集じんによる
システムで処理する場合、燃料比(固定炭素/揮
発分)の高い炭種の燃焼、二段燃焼や排ガス混合
などの窒素酸化物(NOx)低減燃焼対策の実施
により発生する未燃カーボンを主体とする黒色石
炭灰、脱硝装置よりのリークアンモニアと排ガス
中の硫黄酸化物(SOx)との反応に起因するアン
モニウム化合物が集じん器捕集石炭灰中に含まれ
る。石炭火力発電所における通常の灰処理として
は、粗粉は投棄され、細粉はフライアツシユとし
て販売されセメント混和材などに用いられてい
る。
When treating coal-fired boiler exhaust gas with a technically and economically superior high-dust system of denitrification, air preheating, and low-temperature dust collection, combustion of coal types with a high fuel ratio (fixed carbon/volatile matter) and two-stage combustion are recommended. Black coal ash, which is mainly composed of unburnt carbon, generated by implementing combustion measures to reduce nitrogen oxides (NOx) such as combustion and exhaust gas mixing, and the reaction between leaked ammonia from the denitrification equipment and sulfur oxides (SOx) in the exhaust gas. The ammonium compounds responsible are contained in the coal ash collected by the dust collector. In normal ash processing at coal-fired power plants, coarse powder is dumped, and fine powder is sold as fly ash and used in cement admixtures.
しかし黒色石炭灰発生時は製品として販売でき
ないので全量投棄しなければならず問題となつて
いる。またアンモニウム化合物はアンモニア臭気
の発生、水系へのアンモニアの溶出などのため、
石炭灰の投棄、利用に際し悪影響が予想される。
However, when black coal ash is generated, it cannot be sold as a product, so the entire amount must be dumped, which poses a problem. In addition, ammonium compounds generate ammonia odor and elute ammonia into water systems, so
Negative effects are expected when dumping and using coal ash.
石炭灰中に含まれる黒色石炭灰の主成分は未燃
カーボンであり、未燃カーボン以外にもFe3O4が
黒色化の原因と考えられている。未燃カーボンお
よびFe3O4は、次式のように500℃以上の高温に
よる燃焼により除去することができる。 The main component of black coal ash contained in coal ash is unburned carbon, and in addition to unburned carbon, Fe 3 O 4 is thought to be the cause of blackening. Unburned carbon and Fe 3 O 4 can be removed by combustion at a high temperature of 500°C or higher as shown in the following equation.
C+O2→CO2
4Fe3O4+O2→6Fe2O3
一方、アンモニウム化合物は(NH4)2SO4、
NH4HSO4の形で含まれ、除去方法としては水洗
法、熱分解法が考えられる。水洗法は硫安などの
アンモニウム化合物の水に対する溶解度の高いこ
とに着目したもので、高除去率が期待されるが、
処理後の石炭灰に多量の水分が含まれるので石炭
灰の製品化が難しく、またアンモニア臭気の発
生、水へのアンモニアの溶出などの問題点があ
る。一方、アンモニウム化合物の熱分解は温度
300℃以上で次式にしたがつて定量的に進行する。 C+O 2 →CO 2 4Fe 3 O 4 +O 2 → 6Fe 2 O 3 On the other hand, ammonium compounds are (NH 4 ) 2 SO 4 ,
It is contained in the form of NH 4 HSO 4 and can be removed by washing with water or thermal decomposition. The water washing method focuses on the high solubility of ammonium compounds such as ammonium sulfate in water, and is expected to have a high removal rate.
Since treated coal ash contains a large amount of water, it is difficult to commercialize coal ash, and there are also problems such as the generation of ammonia odor and the elution of ammonia into water. On the other hand, the thermal decomposition of ammonium compounds occurs at
It progresses quantitatively at temperatures above 300°C according to the following formula.
(NH4)2SO4→NH3+NH4HSO4
NH4HSO4→NH3+SO3+H2O
しかしながら黒色石炭灰の焼成、アンモニウム
化合物の熱分解には高温を必要とし、この熱源の
供給が大きな問題であつた。 (NH 4 ) 2 SO 4 →NH 3 +NH 4 HSO 4 NH 4 HSO 4 →NH 3 +SO 3 +H 2 O However, the burning of black coal ash and the thermal decomposition of ammonium compounds require high temperatures, and the supply of this heat source is It was a big problem.
本発明は上記の問題点を解決すべく、本発明者
らが鋭意研究の結果なされたもので、本発明者ら
が実験により知見し確認した事実、すなわち黒色
石炭灰は粗粉側にアンモニウム化合物は細粉側に
殆ど含まれるという事実に着目して、石炭だきボ
イラ排ガスを高ダスト系脱硝−低温集じんで処理
する方法において、黒色石炭灰およびアンモニウ
ム化合物を含む集じん装置捕集石炭灰を、まず分
級器に投入してアンモニウム化合物を含む細粉
と、未燃カーボンなどの黒色石炭灰を含む粗粉と
に分級し、細粉は300〜500℃の温度にて脱安を実
施し、固気分離した後、フライアツシユとして製
品化し、アンモニアを含む分解ガスを脱硝装置の
アンモニア源として再利用し、一方、粗粉を500
〜1100℃の温度で焼成、脱色することにより、黒
色石炭灰およびアンモニウム化合物を効率よくか
つ熱経済的に除去して石炭灰を有効利用し得る石
炭灰の処理方法を提供することを目的とするもの
である。 The present invention was made as a result of intensive research by the present inventors in order to solve the above-mentioned problems. Focusing on the fact that most of the coal ash is contained in fine powder, in the method of treating coal-fired boiler exhaust gas by high-dust denitrification and low-temperature dust collection, black coal ash and coal ash collected by a dust collector containing ammonium compounds are used. First, it is put into a classifier and classified into fine powder containing ammonium compounds and coarse powder containing black coal ash such as unburned carbon. After solid-gas separation, it is commercialized as flyash, and the cracked gas containing ammonia is reused as an ammonia source for the denitrification equipment.
The purpose of the present invention is to provide a coal ash processing method that can effectively utilize coal ash by efficiently and thermoeconomically removing black coal ash and ammonium compounds by calcining and decolorizing at a temperature of ~1100°C. It is something.
上記の目的を達成するために、本発明の石炭灰
の処理方法は、図面に示すように、石炭だきボイ
ラ排ガスを高ダストの状態でアンモニア接触還元
方式の脱硝装置2に導入して脱硝し、ついで排ガ
スを空気予熱器3に導入して燃焼用空気を予熱し
た後、排ガスを低温集じん装置4に導入して除じ
んする方法において、黒色石炭灰およびアンモニ
ウム化合物を含む集じん装置捕集石炭灰を、分級
器11に投入してアンモニウム化合物を含む細粉
と未燃カーボンなどの黒色石炭灰を含む粗粉とに
分級し、細粉をアンモニウム化合物熱分解炉12
に投入するとともに、高温燃焼排ガスをこの分解
炉12に吹き込んで300〜500℃の温度にて固気接
触させて細粉中のアンモニウム化合物を分解せし
め、分解炉12よりの石炭灰を含む分解ガスを固
気分離した後、アンモニアを含む分解ガスを脱硝
装置前に戻しアンモニア源として再利用し、一
方、分級した粗粉を脱色炉16に投入し500〜
1100℃の温度にて焼成・脱色するようにしたもの
である。
In order to achieve the above object, the coal ash processing method of the present invention, as shown in the drawing, introduces coal-fired boiler exhaust gas in a highly dusty state into an ammonia catalytic reduction type denitrification device 2 to denitrify it, Next, the exhaust gas is introduced into the air preheater 3 to preheat the combustion air, and then the exhaust gas is introduced into the low-temperature dust collector 4 for dust removal. The ash is charged into a classifier 11 and classified into fine powder containing ammonium compounds and coarse powder containing black coal ash such as unburned carbon, and the fine powder is transferred to an ammonium compound pyrolysis furnace 12.
At the same time, high-temperature combustion exhaust gas is blown into this cracking furnace 12 and brought into solid-gas contact at a temperature of 300 to 500°C to decompose ammonium compounds in the fine powder, and the cracked gas containing coal ash from the cracking furnace 12 is After solid-gas separation, the cracked gas containing ammonia is returned to the front of the denitrification equipment and reused as an ammonia source, while the classified coarse powder is fed into the decolorization furnace 16 and
It is fired and decolored at a temperature of 1100℃.
石炭だきボイラ1の排ガスは、高ダストの状態
でアンモニア接触還元方式の脱硝装置2に導入さ
れて脱硝され、ついで排ガスは空気予熱器3に導
入されて燃焼用空気を予熱した後、低温集じん装
置4に導入されて除じんされる。石炭だきボイラ
1において生成した黒色石炭灰および脱硝装置2
よりのリークアンモニアと排ガス中のSOxとの反
応により生成するアンモニウム化合物を含む集じ
ん装置捕集石炭灰を、気流分級器などの分級器1
1に投入してアンモニウム化合物を含む細粉と、
未燃カーボンなどの黒色石炭灰を含む粗粉とに分
級する。細粉をアンモニウム化合物熱分解炉12
に投入するとともに、高温燃焼排ガスをこの分解
炉12に吹き込んで300〜500℃の温度にて固気接
触させて細粉中のアンモニウム化合物を熱分解せ
しめる。
The exhaust gas from the coal-fired boiler 1 is introduced in a highly dusty state to the ammonia catalytic reduction type denitrification device 2 to be denitrified, and then the exhaust gas is introduced to the air preheater 3 to preheat the combustion air, and then to the low-temperature dust collector. It is introduced into the device 4 to remove dust. Black coal ash generated in coal-fired boiler 1 and denitration equipment 2
The coal ash collected by the dust collector, which contains ammonium compounds generated by the reaction between leaked ammonia and SOx in the exhaust gas, is collected by a classifier such as an air classifier 1.
Fine powder containing an ammonium compound is added to 1,
It is classified into coarse powder containing black coal ash such as unburned carbon. Ammonium compound thermal decomposition furnace 12
At the same time, high-temperature combustion exhaust gas is blown into the decomposition furnace 12 and brought into solid-gas contact at a temperature of 300 to 500°C to thermally decompose ammonium compounds in the fine powder.
ついで分解炉12よりの石炭灰を含む分解ガス
を固気分離器14に導入して固気分離した後、ア
ンモニアを含む分解ガスを脱硝装置2前に戻しア
ンモニア源として再利用する。固気分離器14で
分離された石炭灰は灰冷却器15を経由して灰冷
却設備へ輸送されフライアツシユなどとして有効
利用される。一方、分級器11で分級された粗粉
は、脱色炉16に投入され500〜1100℃の温度に
て黒色石炭灰が焼成・脱色され、灰冷却器17を
経て灰処理設備に輸送され有効利用される。 Next, the cracked gas containing coal ash from the cracking furnace 12 is introduced into the solid-gas separator 14 for solid-gas separation, and then the cracked gas containing ammonia is returned to the front of the denitrification device 2 and reused as an ammonia source. The coal ash separated by the solid-gas separator 14 is transported to an ash cooling facility via the ash cooler 15 and is effectively used as fly ash. On the other hand, the coarse powder classified by the classifier 11 is put into the decolorization furnace 16, where the black coal ash is calcined and decolorized at a temperature of 500 to 1100°C, and then transported to the ash processing equipment via the ash cooler 17 for effective use. be done.
以下、本発明の実施例を図面に基づいて説明す
る。第1図は本発明の方法を実施する装置の一例
を示すもので、石炭だきボイラ1の排ガスダクト
にアンモニア接触還元方式の脱硝触媒を移動床式
または固定床式に充填した脱硝装置2、空気予熱
器3、電気集じん機などの集じん装置4、熱交換
器5、脱硫装置6および煙突7が直列に接続され
ている。集じん装置としては電気集じん機の代り
に他の装置、たとえば砂、砂利、セラミツクスな
どの粒塊状ろ過材をルーバ、金網、パンチングメ
タルなどの支持体間に移動可能に充填してなるグ
ラベル式ろ過集じん装置、マルチサイクロン、バ
グフイルタなどを用いることも可能である。8は
ボイラ1に設けられた節炭器、10は脱硝装置の
上流側に接続されたアンモニア供給管である。
Embodiments of the present invention will be described below based on the drawings. Fig. 1 shows an example of an apparatus for carrying out the method of the present invention. A preheater 3, a dust collector 4 such as an electrostatic precipitator, a heat exchanger 5, a desulfurizer 6, and a chimney 7 are connected in series. Instead of an electrostatic precipitator, the dust collector is replaced by another device, such as a gravel type, in which a granular filter material such as sand, gravel, or ceramics is movably filled between supports such as louvers, wire mesh, or punched metal. It is also possible to use filter dust collectors, multi-cyclones, bag filters, etc. Reference numeral 8 designates an economizer provided in the boiler 1, and reference numeral 10 designates an ammonia supply pipe connected to the upstream side of the denitrification device.
石炭だきボイラ1の排ガスは、高ダストの状態
でアンモニア接触還元方式の脱硝装置2に導入さ
れて脱硝され、ついで排ガスは空気予熱器3に導
入されて燃焼用空気を予熱した後、低温集じん装
置4に導入されて除じんされる。石炭だきボイラ
1において、燃料比の高い炭種を燃焼させたり、
二段燃焼、排ガス混合などのNOx低減燃焼対策
を行なつたりする場合には、未燃カーボンを主成
分とする黒色石炭灰が生成する。この黒色石炭灰
および脱硝装置2よりのリークアンモニアと排ガ
ス中のSOxとの反応により生成するアンモニウム
化合物を含む集じん装置捕集石炭灰を、気流分級
器などの分級器11に投入してアンモニウム化合
物を含む細粉と、未燃カーボンなどの黒色石炭灰
を含む粗粉とに分級する。細粉をアンモニウム化
合物熱分解炉12に投入するとともに、高温燃焼
排ガスをこの分解炉12に吹き込んで300〜500
℃、好ましくは350〜450℃の温度にて固気接触さ
せて細粉中のアンモニウム化合物を熱分解せしめ
る。アンモニウム化合物熱分解炉12としては、
噴流層、流動層、輸送層などの気流搬送式のもの
が用いられる。またアンモニウム化合物熱分解炉
12の熱源としては、石炭だきボイラ1の節炭器
8の前もしくは後の高温燃焼排ガスをそのままも
しくは助燃炉13(熱風発生炉)によりさらに昇
温した高温燃焼排ガス、熱風発生炉13のみより
の高温燃焼排ガス、または/および後述の脱色炉
よりの高温排ガスが用いられる。ついで分解炉1
2よりの石炭灰を含む分解ガスを固気分離器14
に導入して固気分離した後、アンモニアを含む分
解ガスを脱硝装置2前に戻しアンモニア源として
再利用する。固気分離器14としては、電気集じ
ん機、バグフイルタ、前述のグラベル式ろ過集じ
ん装置、マルチサイクロンなどを用いることがで
きるが、温度、粒径を考慮すれば電気集じん機、
グラベル式ろ過集じん装置を用いるのが望まし
い。固気分離器14で分離された石炭灰は灰冷却
器15を経由して灰冷却設備へ輸送されフライア
ツシユなどとして有効利用される。一方、分級器
11で分級された粗粉は、脱色炉16に投入され
500〜1100℃、好ましくは700〜900℃の温度にて
黒色石炭灰が焼成・脱色され、灰冷却器17を経
て灰処理設備に輸送され有効利用される。前記脱
色炉16としては、噴流層、流動層、輸送層など
の気流搬送式の炉、キルン式の炉などが用いら
れ、脱色炉16の加熱方法としては、脱色炉にバ
ーナ20を設けて燃料を直接燃焼させる方法、脱
色炉に熱風発生炉21を接続して高温の燃焼排ガ
スを供給する方法、または/および石炭だきボイ
ラ1の高温燃焼排ガスをそのまま供給する方法な
どが用いられる。黒色石炭灰の焼成は非常に高温
であるので焼成、固気分離後の排ガスをアンモニ
ウム化合物熱分解炉に投入することにより排熱を
利用、回収することも可能である。また灰冷却器
15,17としては、排熱を回収するために流動
層方式のものを用いるのが望ましい。脱色炉16
においては、黒色石炭灰の焼成により大量の熱が
発生するので、この熱は上記流動層方式の灰冷却
器17で回収される。 The exhaust gas from the coal-fired boiler 1 is introduced in a highly dusty state to the ammonia catalytic reduction type denitrification device 2 to be denitrified, and then the exhaust gas is introduced to the air preheater 3 to preheat the combustion air, and then to the low-temperature dust collector. It is introduced into the device 4 to remove dust. In the coal-fired boiler 1, a type of coal with a high fuel ratio is burned,
When NOx reduction combustion measures are taken, such as two-stage combustion or exhaust gas mixing, black coal ash, which is mainly composed of unburned carbon, is produced. This black coal ash and the coal ash collected by the dust collector containing ammonium compounds produced by the reaction between leaked ammonia from the denitrification equipment 2 and SOx in the exhaust gas are fed into a classifier 11 such as an air classifier to collect ammonium compounds. It is classified into fine powder containing black coal ash and coarse powder containing black coal ash such as unburned carbon. The fine powder is put into the ammonium compound pyrolysis furnace 12, and high-temperature combustion exhaust gas is blown into the decomposition furnace 12 to
The ammonium compound in the fine powder is thermally decomposed by solid-gas contact at a temperature of 350 to 450°C. As the ammonium compound pyrolysis furnace 12,
Air flow conveyance types such as spouted bed, fluidized bed, and transport bed are used. The heat source of the ammonium compound pyrolysis furnace 12 is the high-temperature combustion exhaust gas before or after the economizer 8 of the coal-fired boiler 1, or the high-temperature combustion exhaust gas that has been further heated in the auxiliary combustion furnace 13 (hot air generation furnace), or hot air. High-temperature combustion exhaust gas from only the generation furnace 13 and/or high-temperature exhaust gas from a decolorization furnace (described later) is used. Next, decomposition furnace 1
The cracked gas containing coal ash from No. 2 is transferred to a solid-gas separator 14.
After solid-gas separation, the cracked gas containing ammonia is returned to the front of the denitrification device 2 and reused as an ammonia source. As the solid-gas separator 14, an electrostatic precipitator, a bag filter, the above-mentioned gravel filter dust collector, a multi-cyclone, etc. can be used.
It is preferable to use a gravel filtration device. The coal ash separated by the solid-gas separator 14 is transported to an ash cooling facility via the ash cooler 15 and is effectively used as fly ash. On the other hand, the coarse powder classified by the classifier 11 is fed into the decolorization furnace 16.
The black coal ash is calcined and decolorized at a temperature of 500 to 1100°C, preferably 700 to 900°C, and is transported to an ash processing facility via an ash cooler 17 for effective use. As the decolorizing furnace 16, an air flow conveyance type furnace such as a spouted bed, a fluidized bed, a transport bed, a kiln type furnace, etc. are used.The decolorizing furnace 16 is heated by installing a burner 20 in the decolorizing furnace and using fuel. A method of directly combusting the decolorizing furnace, a method of connecting a hot air generating furnace 21 to the decolorizing furnace and supplying high-temperature combustion exhaust gas, and/or a method of supplying high-temperature combustion exhaust gas of the coal-fired boiler 1 as it is, etc. are used. Since black coal ash is fired at a very high temperature, it is also possible to utilize and recover the exhaust heat by inputting the exhaust gas after firing and solid-gas separation into an ammonium compound thermal decomposition furnace. Further, as the ash coolers 15 and 17, it is desirable to use fluidized bed type coolers in order to recover waste heat. Decolorization furnace 16
Since a large amount of heat is generated by burning the black coal ash, this heat is recovered by the fluidized bed type ash cooler 17.
以上説明したように、本発明の方法によれば集
じん装置捕集石炭灰中に含まれる黒色石炭灰およ
びアンモニウム化合物をきわめて効率よく除去す
ることができる上に、分解ガスを脱硝装置のアン
モニア源として再利用することができ、全体とし
て省エネルギ化を図ることができ、かつ石炭灰の
有効利用に寄与することができるなどの効果を奏
する。
As explained above, according to the method of the present invention, the black coal ash and ammonium compounds contained in the coal ash collected by the dust collector can be removed very efficiently, and the cracked gas can be used as an ammonia source for the denitration equipment. It has the following effects: it can be reused as coal ash, it can save energy as a whole, and it can contribute to the effective use of coal ash.
第1図は本発明の方法を実施する装置の一例を
示す系統的説明図である。
1……石炭だきボイラ、2……脱硝装置、3…
…空気予熱器、4……集じん装置、5……熱交換
器、6……脱硫装置、7……煙突、8……節炭
器、10……アンモニア供給管、11……分級
器、12……アンモニウム化合物熱分解炉、13
……助燃炉(熱風発生炉)、14……固気分離器、
15……灰冷却器、16……脱色炉、17……灰
冷却器、20……バーナ、21……熱風発生炉。
FIG. 1 is a systematic explanatory diagram showing an example of an apparatus for carrying out the method of the present invention. 1...Coal-fired boiler, 2...Denitration equipment, 3...
... Air preheater, 4 ... Dust collector, 5 ... Heat exchanger, 6 ... Desulfurization device, 7 ... Chimney, 8 ... Carbon economizer, 10 ... Ammonia supply pipe, 11 ... Classifier, 12... Ammonium compound thermal decomposition furnace, 13
... auxiliary combustion furnace (hot air generating furnace), 14 ... solid-gas separator,
15... Ash cooler, 16... Decolorization furnace, 17... Ash cooler, 20... Burner, 21... Hot air generating furnace.
Claims (1)
ンモニア接触還元方式の脱硝装置に導入して脱硝
し、ついで排ガスを空気予熱器に導入して燃焼用
空気を予熱した後、排ガスを低温集じん装置に導
入して除じんする方法において、黒色石炭灰およ
びアンモニウム化合物を含む集じん装置捕集石炭
灰を、分級器に投入してアンモニウム化合物を含
む細粉と未燃カーボンなどの黒色石炭灰を含む粗
粉とに分級し、細粉をアンモニウム化合物熱分解
炉に投入するとともに、高温燃焼排ガスをこの分
解炉に吹き込んで300〜500℃の温度にて固気接触
させて細粉中のアンモニウム化合物を分解せし
め、分解炉よりの石炭灰を含む分解ガスを固気分
離した後、アンモニアを含む分解ガスを脱硝装置
前に戻しアンモニア源として再利用し、一方、分
級した粗粉を脱色炉に投入し500〜1100℃の温度
にて焼成・脱色することを特徴とする石炭灰の処
理方法。1 Coal-fired boiler exhaust gas in a highly dusty state is introduced into an ammonia catalytic reduction type denitrification device for denitrification, then the exhaust gas is introduced into an air preheater to preheat the combustion air, and then the exhaust gas is sent to a low-temperature dust collector. In the method of introducing dust removal, coal ash collected by a dust collector containing black coal ash and ammonium compounds is fed into a classifier to separate fine powder containing ammonium compounds and coarse coal ash containing black coal ash such as unburned carbon. The fine powder is charged into an ammonium compound thermal decomposition furnace, and high-temperature combustion exhaust gas is blown into the decomposition furnace to cause solid-gas contact at a temperature of 300 to 500°C to decompose the ammonium compounds in the fine powder. After separating the cracked gas containing coal ash from the cracking furnace into solid and gas, the cracked gas containing ammonia is returned to the front of the denitrification equipment and reused as an ammonia source, while the classified coarse powder is fed into the decolorization furnace. A coal ash processing method characterized by firing and decolorizing at a temperature of ~1100℃.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP55128804A JPS5753225A (en) | 1980-09-17 | 1980-09-17 | Treatment of coal ash |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP55128804A JPS5753225A (en) | 1980-09-17 | 1980-09-17 | Treatment of coal ash |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5753225A JPS5753225A (en) | 1982-03-30 |
| JPS6357095B2 true JPS6357095B2 (en) | 1988-11-10 |
Family
ID=14993829
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP55128804A Granted JPS5753225A (en) | 1980-09-17 | 1980-09-17 | Treatment of coal ash |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5753225A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR100460624B1 (en) * | 2002-10-31 | 2004-12-09 | 한국전력공사 | Device for removing an adhesive gas of coal ash |
| CN104214787A (en) * | 2014-08-22 | 2014-12-17 | 合肥四方磷复肥有限责任公司 | Surplus heat utilization method for boil tail gas |
-
1980
- 1980-09-17 JP JP55128804A patent/JPS5753225A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5753225A (en) | 1982-03-30 |
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