JPS6357094B2 - - Google Patents
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- Publication number
- JPS6357094B2 JPS6357094B2 JP55128803A JP12880380A JPS6357094B2 JP S6357094 B2 JPS6357094 B2 JP S6357094B2 JP 55128803 A JP55128803 A JP 55128803A JP 12880380 A JP12880380 A JP 12880380A JP S6357094 B2 JPS6357094 B2 JP S6357094B2
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- Prior art keywords
- coal ash
- exhaust gas
- furnace
- temperature
- coal
- 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)
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
の脱硝、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 [Field of Industrial Application] The present invention is 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 for efficiently and economically removing black coal ash whose main components are ammonium compounds and unburned carbon contained therein.
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
300〜500℃の温度にて脱安を実施し、固気分離し
た後、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、分離した石炭灰を細
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、細粉をフライアツシユとして製品と
し、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
After detanking at a temperature of 300 to 500℃ and solid-gas separation, the cracked gas containing ammonia is reused as an ammonia source for the denitrification equipment, and the separated coal ash is used as fine powder and black materials such as unburned carbon. Black coal ash and ammonium compounds can be produced efficiently and thermoeconomically by classifying them into coarse powder containing coal ash, producing the fine powder as fly ash, and calcining and decolorizing the coarse powder at a temperature of 500 to 1100°C. The object of the present invention is to provide a method for treating coal ash that can be removed and used effectively.
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、アン
モニウム化合物熱分解炉11に投入するととも
に、高温燃焼排ガスをこの分解炉11に吹き込ん
で300〜500℃の温度にて固気接触させて石炭灰中
のアンモニウム化合物を分解せしめ、分解炉11
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、分離した石炭灰を分
級器14に投入して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、粗粉を脱色炉1
5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 put into the ammonium compound thermal decomposition furnace 11, and high-temperature combustion exhaust gas is blown into the decomposition furnace 11 to cause solid-gas contact at a temperature of 300 to 500°C to decompose the ammonium compounds in the coal ash. 11
After solid-gas separation of cracked gas containing coal ash,
The cracked gas containing ammonia is returned to the front of the denitrification device and reused as an ammonia source, and the separated coal ash is charged into a classifier 14 to classify it into fine powder and coarse powder containing black coal ash such as unburned carbon, Coarse powder in decolorizing furnace 1
5 and calcined and decolorized at a temperature of 500 to 1100°C.
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、アンモニウム化合物熱分解
炉11に投入するとともに、高温燃焼排ガスをこ
の分解炉11に吹き込んで300〜500℃の温度にて
固気接触させて石炭灰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 containing ammonium compounds produced by the reaction between leaked ammonia and SOx in the exhaust gas is charged into the ammonium compound pyrolysis furnace 11, and high-temperature combustion exhaust gas is blown into the decomposition furnace 11. Ammonium compounds in coal ash are thermally decomposed by solid-gas contact at a temperature of 300 to 500°C.
分解炉11よりの石炭灰を含む分解ガスを固気
分離器13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
ア源として再利用し、分離した石炭灰を気流分級
器などの分級器14に投入して細粉と、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。
分級器14で分級された粗粉は、脱色炉15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16を経て灰処理設備に
輸送され有効利用される。一方、分級器14で分
級された細粉は灰冷却器17を経由して灰処理設
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。 After the cracked gas containing coal ash from the cracking furnace 11 is introduced into the solid-gas separator 13 for solid-gas separation, the cracked gas containing ammonia is returned to the front of the denitrification device 2 and reused as an ammonia source, and the separated coal ash is The coal is put into a classifier 14 such as an air classifier and classified into fine powder and coarse powder containing black coal ash such as unburned carbon.
The coarse powder classified by the classifier 14 is put into a decolorizing furnace 15, where black coal ash is calcined and decolorized at a temperature of 500 to 1100°C, and then transported to an ash processing facility via an ash cooler 16 for effective use. . On the other hand, the fine powder classified by the classifier 14 is transported to an ash processing facility via an ash cooler 17 and is effectively used as fly ash.
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、脱硝装置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 denitrification device 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、アンモニ
ウム化合物熱分解炉11に投入するとともに、高
温燃焼排ガスをこの分解炉11に吹き込んで300
〜500℃、好ましくは350〜450℃の温度にて固気
接触させて石炭灰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11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11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12(熱風発生炉)により
さらに昇温した高温燃焼排ガス、または熱風発生
炉12のみよりの高温燃焼排ガスが用いられる。
分解炉11よりの石炭灰を含む分解ガスを固気分
離器13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
源として再利用し、分離した石炭灰を気流分級器
などの分級器14に投入して細粉と、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。前
記固気分離器13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。分級器1
4で分級された粗粉は、脱色炉15に投入され
500〜1100℃、好ましくは700〜900℃の温度にて
黒色石炭灰が燃焼・脱色され、灰冷却器16を経
て灰処理設備に輸送され有効利用される。一方、
分級器14で分級された細粉は灰冷却器17を経
由して灰処理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。前記脱色炉15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15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16,17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15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16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 denitration equipment 2 and SOx in the exhaust gas are fed into the ammonium compound pyrolysis furnace 11, and the high-temperature combustion exhaust gas is blown into this decomposition furnace 11 to produce 300
The ammonium compounds in the coal ash are thermally decomposed by solid-gas contact at a temperature of ~500°C, preferably 350~450°C. As the ammonium compound thermal decomposition furnace 11, an air conveyance type furnace such as a spouted bed, a fluidized bed, or a transport bed is used. In addition, the heat source of the ammonium compound pyrolysis furnace 11 is a coal-fired boiler 1.
The high-temperature combustion exhaust gas before or after the economizer 8 is used as it is, the high-temperature combustion exhaust gas further heated by the auxiliary combustion furnace 12 (hot-air generator), or the high-temperature combustion exhaust gas only from the hot-air generator 12 is used.
After the cracked gas containing coal ash from the cracking furnace 11 is introduced into the solid-gas separator 13 for solid-gas separation, the cracked gas containing ammonia is returned to the front of the denitrification device 2 and reused as an ammonia source, and the separated coal ash is The coal is put into a classifier 14 such as an air classifier and classified into fine powder and coarse powder containing black coal ash such as unburned carbon. As the solid-gas separator 13, an electrostatic precipitator, a bag filter, the above-mentioned gravel type filtration and dust collector, a multi-cyclone, etc. can be used. It is preferable to use a filter and dust collector. Classifier 1
The coarse powder classified in step 4 is put into a decolorizing furnace 15.
Black coal ash is burned 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 16 for effective use. on the other hand,
The fine powder classified by the classifier 14 is transported to an ash processing facility via an ash cooler 17 and is effectively used as fly ash. As the decolorizing furnace 15, an air flow conveyance type furnace such as a spouted bed, a fluidized bed, a transport bed, a kiln type furnace, etc. are used.As a heating method for the decolorizing furnace 15, a burner 20 is installed in the decolorizing furnace and fuel is heated. 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 16 and 17, it is desirable to use fluidized bed type coolers in order to recover waste heat. In the decolorization furnace 15,
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 16.
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……アンモ
ニウム化合物熱分解炉、12……助熱炉(熱風発
生炉)、13……固気分離器、14……分級器、
15……脱色炉、16,17……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 ... Ammonium compound heat Decomposition furnace, 12... Reheating furnace (hot air generation furnace), 13... Solid-gas separator, 14... Classifier,
15... Decolorization furnace, 16, 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、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石炭灰中
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、分離した石炭灰を分級器
に投入して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、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 this method, coal ash collected by a dust collector containing black coal ash and ammonium compounds is introduced into an ammonium compound pyrolysis furnace, and high-temperature combustion exhaust gas is blown into the decomposition furnace to heat the coal ash at 300 to 500°C. The ammonium compounds in the coal ash are decomposed by solid-gas contact at a temperature of The recycled and separated coal ash is put into a classifier to classify it into fine powder and coarse powder containing black coal ash such as unburned carbon, and the coarse powder is put into a decolorizing furnace.
A coal ash processing method characterized by firing and decolorizing at a temperature of 500 to 1100°C.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP55128803A JPS5753224A (en) | 1980-09-17 | 1980-09-17 | Treatment of coal ash |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP55128803A JPS5753224A (en) | 1980-09-17 | 1980-09-17 | Treatment of coal ash |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5753224A JPS5753224A (en) | 1982-03-30 |
| JPS6357094B2 true JPS6357094B2 (en) | 1988-11-10 |
Family
ID=14993805
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP55128803A Granted JPS5753224A (en) | 1980-09-17 | 1980-09-17 | Treatment of coal ash |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5753224A (en) |
Families Citing this family (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0741653Y2 (en) * | 1988-12-27 | 1995-09-27 | 日本車輛製造株式会社 | Vehicle connecting hood device |
| JPH0624929B2 (en) * | 1989-01-23 | 1994-04-06 | 株式会社成田製作所 | Automatic connection and release device for vehicle hood |
| JPH0624930B2 (en) * | 1989-11-09 | 1994-04-06 | 株式会社成田製作所 | Connecting hood for vehicles |
| KR100460624B1 (en) * | 2002-10-31 | 2004-12-09 | 한국전력공사 | Device for removing an adhesive gas of coal ash |
| US7641878B2 (en) | 2006-02-21 | 2010-01-05 | Pmi Ash Technologies, Llc | Fly ash beneficiation systems with sulfur removal and methods thereof |
| US7867462B2 (en) | 2006-09-25 | 2011-01-11 | Pmi Ash Technologies, Llc | Coal combustion systems with emissions control and fly ash beneficiation and methods thereof |
| US8545598B2 (en) * | 2007-06-19 | 2013-10-01 | Pmi Ash Technologies, Llc | Mercury removal systems using beneficiated fly ash particles and methods thereof |
-
1980
- 1980-09-17 JP JP55128803A patent/JPS5753224A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5753224A (en) | 1982-03-30 |
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