JPS6332494B2 - - Google Patents
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- Publication number
- JPS6332494B2 JPS6332494B2 JP55063135A JP6313580A JPS6332494B2 JP S6332494 B2 JPS6332494 B2 JP S6332494B2 JP 55063135 A JP55063135 A JP 55063135A JP 6313580 A JP6313580 A JP 6313580A JP S6332494 B2 JPS6332494 B2 JP S6332494B2
- Authority
- JP
- Japan
- Prior art keywords
- coal ash
- exhaust gas
- air
- gas
- 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.)
- Expired
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Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
- Y02P20/129—Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
Landscapes
- Chimneys And Flues (AREA)
- Processing Of Solid Wastes (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Description
【発明の詳細な説明】
本発明は、石炭だきボイラ排ガスを高ばいじん
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、系内で高温石炭灰と熱交換して加
熱された空気により集じん装置捕集石炭灰を輸送
しながら予熱して分解炉内に投入し、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を効
率よくかつ経済的に除去する方法に関するもので
ある。DETAILED DESCRIPTION OF THE INVENTION The present invention is a method for treating coal-fired boiler exhaust gas in the order of highly dust-based denitrification, air preheating, and low-temperature dust collection. The present invention relates to a method for efficiently and economically removing ammonium compounds contained in the coal ash collected by the dust collector by preheating the coal ash collected by the dust collector while transporting it and introducing it into a decomposition furnace.
石炭だきボイラの排ガスを高ばいじんの状態で
ア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、排ガスを低温電気集じん機
などの集じん装置に導入して除じんし、さらに排
ガスを脱硫装置に導入して脱硫処理を施す場合、
脱硝装置よりのリークアンモニアと排ガス中に含
まれる硫黄酸化物(以下、SOxと記す)との反応
に起因するアンモニウム化合物が集じん装置捕集
石炭灰中に含まれる。このアンモニウム化合物は
灰処理設備のみならず石炭灰の投棄、利用などに
も悪影響を及ぼすことが予想される。もちろん脱
硝装置よりのリークアンモニアの低減が検討され
ているが、不十分な結果しか得られていない現状
で、このためアンモニウム化合物対策が必要とな
る。 Exhaust gas from a coal-fired boiler is introduced in a highly dusty state to an ammonia catalytic reduction type denitrification device for denitrification, then the exhaust gas is introduced to an air preheater to preheat the combustion air, and then the exhaust gas is sent to a low-temperature electrostatic precipitator. When introducing the exhaust gas into a dust collector such as the
Ammonium compounds resulting from the reaction between leaked ammonia from the denitrification equipment and sulfur oxides (hereinafter referred to as SOx) contained in the exhaust gas are contained in the coal ash collected by the dust collector. This ammonium compound is expected to have an adverse effect not only on ash processing equipment but also on the dumping and utilization of coal ash. Of course, the reduction of leaked ammonia from the denitrification equipment is being considered, but the current results are insufficient, and therefore, countermeasures against ammonium compounds are needed.
集じん装置捕集石炭灰中に含まれるアンモニウ
ム化合物は、主として(NH4)2SO4、NH4HSO4
の形で存在する。アンモニウム化合物の石炭灰よ
りの除去方法として水洗法、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
に対する溶解度が高く、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
石炭灰の有効利用が難しく、またアンモニア(以
下、NH3と記す)を含む排水の処理が必要であ
るなどの問題点を有している。一方、アンモニウ
ム化合物の熱分解は次式にしたがつて進行する。 The ammonium compounds contained in the coal ash collected by the dust collector are mainly (NH 4 ) 2 SO 4 and NH 4 HSO 4
It exists in the form of Possible methods for removing ammonium compounds from coal ash include water washing and thermal decomposition. The water washing method has high solubility of ammonium compounds such as ammonium sulfate in water, and is expected to have a high removal rate.However, since the coal ash after treatment contains a large amount of water, it is difficult to use the coal ash effectively. There are problems such as the need to treat wastewater containing NH3 (denoted as NH3 ). On the other hand, thermal decomposition of ammonium compounds proceeds according to the following formula.
(NH4)2SO4→NH3+NH4HSO4
NH4HSO4→NH3+SO3+H2O
しかしながらアンモニウム化合物の熱分解には
かなりの高温を必要とし、このため熱源の供給が
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, thermal decomposition of ammonium compounds requires quite high temperatures, and the supply of a heat source is therefore a major problem. It was hot.
本発明は上記の問題点を解決すべく、本発明者
らの鋭意研究の結果なされたもので、脱硝装置よ
りのクークNH3と排ガス中のSOxとの反応に起
因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に投入す
るとともに、石炭だきボイラの高温燃焼排ガスを
この分解炉に吹き込み250〜700℃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
気分離器に導入し、分解ガスと石炭灰とを分離
し、石炭灰を冷却器にて空気で冷却した後灰処理
設備に輸送し、冷却器で高温石炭灰と熱交換した
後の加熱空気を分解炉上流側の石炭灰輸送管に吹
き込んでアンモニウム含有石炭灰分解炉投入用空
気およびアンモニウム含有石炭灰予熱用空気とし
て使用し、固気分離器よりの分解ガスを脱硝装置
前に戻しNH3源として再利用することにより、
アンモニウム化合物の熱分解熱源を他に求めるこ
となく、クローズドシステムで省エネルギ化をは
かることができる効率のよい石炭灰よりのアンモ
ニウム化合物の除去方法を提供せんとするもので
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. The coal ash collected by the device is put into an ammonium compound pyrolysis furnace, and high-temperature combustion exhaust gas from a coal-fired boiler is blown into this decomposition furnace to bring it into solid-gas contact at a temperature of 250 to 700°C to remove the ammonium compounds in the coal ash. The cracked gas containing coal ash from the cracking furnace is introduced into a solid-gas separator, where the cracked gas and coal ash are separated.The coal ash is cooled with air in a cooler and then transported to an ash processing facility. After exchanging heat with high-temperature coal ash in the cooler, the heated air is blown into the coal ash transport pipe on the upstream side of the cracking furnace and used as air for feeding the ammonium-containing coal ash into the cracking furnace and air for preheating the ammonium-containing coal ash. By returning the cracked gas from the gas separator to the front of the denitration equipment and reusing it as a NH3 source,
The present invention aims to provide an efficient method for removing ammonium compounds from coal ash that can save energy in a closed system without requiring any other heat source for thermal decomposition of ammonium compounds.
以下、本発明の構成を図面に基づいて説明す
る。図面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、バツ
グフイルタなどを用いることも可能である。8は
ボイラ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ウア供給管である。 Hereinafter, the configuration of the present invention will be explained based on the drawings. The drawing shows an example of a device for carrying out the method of the present invention, which includes a denitration device 2 in which the exhaust gas duct of a coal-fired boiler 1 is filled with an ammonia catalytic reduction denitration catalyst in a moving bed type or fixed bed type, and an air 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 filtration and dust collectors, multi-cyclones, bag filters, etc. Reference numeral 8 designates a economizer provided in the boiler, and reference numeral 10 designates an ammonia supply pipe connected to the upstream side of the denitrification device.
集じん装置4の下部に接続された石炭灰輸送管
11は灰ホツパ12を介してアンモニウム化合物
熱分解炉13に接続され、この分解炉13の上部
は石炭灰・分解ガス排出管14を介してマルチサ
イクロン、バツグフイルタ、グラベル式ろ過集じ
ん装置またはこれらを組み合わせたものなどから
なる固気分離器15に接続される。固気分離器1
5の分解ガス出口は分解ガス管16を介して脱硝
装置2の上流側に接続され、固気分離器15の石
炭灰出口は石炭灰輸送管17を介して空気により
冷却する型式の冷却器18に接続され、さらにこ
の冷却器18の石炭灰出口は石炭灰輸送管20を
介して灰処理設備21に接続される。またボイラ
の節炭器8の上流側または下流側に高温燃焼排ガ
ス管22を接続し、この排ガス管22を分解炉1
3の下部に接続する。分解炉13は流動層、輸送
層、噴流層などを採用するのが好適である。なお
排ガス管22に排ガス加熱用補助炉23を接続し
て、排ガス温度が低い場合に望ましい温度に昇温
するように構成することもある。24は石炭灰を
冷却する冷却器18に冷却用空気を供給するため
の冷却用空気供給管、25は冷却器18内で高温
の石炭灰と熱交換して加熱された空気を取り出す
加熱空気管で、この加熱空気管25を分解炉13
上流側の石炭灰輸送管11に接続して、アンモニ
ウム含有石炭灰を加熱空気により輸送、予熱して
分解炉13内に投入するように構成する。 A coal ash transport pipe 11 connected to the lower part of the dust collector 4 is connected to an ammonium compound thermal decomposition furnace 13 via an ash hopper 12, and an upper part of this decomposition furnace 13 is connected to a coal ash and cracked gas discharge pipe 14. It is connected to a solid-gas separator 15 consisting of a multi-cyclone, a bag filter, a gravel type filtration and dust collector, or a combination thereof. Solid gas separator 1
The cracked gas outlet of No. 5 is connected to the upstream side of the denitrification device 2 via a cracked gas pipe 16, and the coal ash outlet of the solid-gas separator 15 is connected to a cooler 18 which is cooled by air via a coal ash transport pipe 17. The coal ash outlet of this cooler 18 is further connected to ash processing equipment 21 via a coal ash transport pipe 20. In addition, a high-temperature combustion exhaust gas pipe 22 is connected to the upstream or downstream side of the economizer 8 of the boiler, and this exhaust gas pipe 22 is connected to the cracking furnace 1.
Connect to the bottom of 3. It is preferable that the cracking furnace 13 employs a fluidized bed, a transport bed, a spouted bed, or the like. Note that an auxiliary exhaust gas heating furnace 23 may be connected to the exhaust gas pipe 22 to raise the exhaust gas temperature to a desired temperature when the exhaust gas temperature is low. 24 is a cooling air supply pipe for supplying cooling air to the cooler 18 that cools the coal ash, and 25 is a heating air pipe for extracting heated air by exchanging heat with the high-temperature coal ash in the cooler 18. Then, this heated air pipe 25 is connected to the decomposition furnace 13.
It is connected to the coal ash transport pipe 11 on the upstream side, and configured to transport ammonium-containing coal ash using heated air, preheat it, and charge it into the decomposition furnace 13.
上記のように構成された装置において、石炭だ
きボイラ排ガスを高ばいじん系脱硝、空気予熱、
低温集じん、脱硫からなるシステムにより処理す
る場合、集じん装置4より排出されるアンモニウ
ム化合物を含む集じん装置補集石炭灰を灰ホツパ
12を経てアンモニウム化合物熱分解炉13に投
入する。分解炉13の熱源として石炭だきボイラ
1の高温燃焼排ガスを導き、250〜700℃、好まし
くは350〜700℃、さらに好ましくは350〜500℃の
温度においてアンモニウム化合物の熱分解を行な
う。熱分解後の石炭灰と分解ガスは固気分離器1
5で分離され、分解ガスは脱硝装置2の前に戻し
NH3源として再利用する。石炭灰は冷却器18
にて空気で冷却した後灰処理設備21に輸送す
る。冷却器18で高温石炭灰と熱交換した後の
200〜500℃前後に加熱された空気は分解炉13の
上流側の石炭灰輸送管11に吹き込まれ、アンモ
ニウム含有石炭灰輸送用源として用いられる。こ
のようにアンモニウム化合物含有石炭灰を加熱空
気で輸送するため、輸送の途中で石炭灰を予熱す
ることができ、かつ分解炉13内で加熱空気と高
温燃焼排ガスとが衝突して石炭灰の混合、分散が
良くなり、石炭灰が均一に分散して熱分解に好適
な状態となる。このため分解炉をコンパクトにす
ることができる。 In the device configured as described above, coal-fired boiler exhaust gas is denitrified with high dust content, air preheated, and
When processing with a system consisting of low-temperature dust collection and desulfurization, the dust collector-collected coal ash containing ammonium compounds discharged from the dust collector 4 is fed into the ammonium compound thermal decomposition furnace 13 via the ash hopper 12. High-temperature combustion exhaust gas from the coal-fired boiler 1 is introduced as a heat source to the decomposition furnace 13, and the ammonium compound is thermally decomposed at a temperature of 250 to 700°C, preferably 350 to 700°C, and more preferably 350 to 500°C. Coal ash and cracked gas after pyrolysis are transferred to solid-gas separator 1
5, and the cracked gas is returned to the front of denitrification equipment 2.
Reuse as NH3 source. Coal ash goes to cooler 18
After being cooled with air at the ash processing facility 21, the ash is transported to the ash processing facility 21. After heat exchange with high temperature coal ash in cooler 18
Air heated to around 200 to 500°C is blown into the coal ash transport pipe 11 on the upstream side of the cracking furnace 13, and is used as a source for transporting ammonium-containing coal ash. Since the ammonium compound-containing coal ash is transported using heated air in this way, the coal ash can be preheated during transportation, and the heated air and high-temperature combustion exhaust gas collide in the cracking furnace 13 to mix the coal ash. , the dispersion is improved, and the coal ash is uniformly dispersed, making it suitable for thermal decomposition. Therefore, the decomposition furnace can be made compact.
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アンモニウム化
合物をきわめて効率よく熱分解できる上に、アン
モニウム化合物熱分解炉からの分解ガスを脱硝装
置のNH3源として再利用することができ、かつ
分解熱源を系外に求めることなく、系内の高温燃
焼排ガスを使用することができ、このためクロー
ズドシステムで省エネルギ化をはかることがで
き、また処理システム量の増大など他の排ガス処
理構成技術に及ぼす影響が殆どないので、安定し
た石炭だきボイラ排ガス処理を行なうことができ
るなどの効果がある。 As explained above, according to the method of the present invention, the ammonium compounds contained in the coal ash collected by the dust collector can be thermally decomposed extremely efficiently, and the cracked gas from the ammonium compound thermal decomposition furnace can be The high-temperature combustion exhaust gas within the system can be reused as a source of decomposition heat, and the high-temperature combustion exhaust gas within the system can be used without requiring a source of decomposition heat outside the system. Therefore, it is possible to save energy in a closed system, and the processing Since there is almost no effect on other exhaust gas treatment configuration technologies such as an increase in system volume, there are effects such as stable coal-fired boiler exhaust gas treatment.
図面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……焦じん装置、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、11,17,20…
…石炭灰輸送管、12……灰ホツパ、13……ア
ンモニウム化合物熱分解炉、14……石炭灰・分
解ガス排出管、15……固気分離器、16……分
解ガス管、18……冷却器、21……灰処理設
備、22……高温燃焼排ガス管、23……排ガス
加熱用補助炉、24……冷却用空気供給管、25
……加熱空気管。
The drawing 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...scorch device, 5...heat exchanger, 6...desulfurization device, 7...chimney, 8...coal economizer,
10...Ammonia supply pipe, 11, 17, 20...
... Coal ash transport pipe, 12 ... Ash hopper, 13 ... Ammonium compound pyrolysis furnace, 14 ... Coal ash/cracking gas discharge pipe, 15 ... Solid gas separator, 16 ... Cracking gas pipe, 18 ... Cooler, 21... Ash processing equipment, 22... High temperature combustion exhaust gas pipe, 23... Auxiliary furnace for heating exhaust gas, 24... Cooling air supply pipe, 25
...Heated air pipe.
Claims (1)
ア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、前記脱硝装置
よりのリークアンモニアと排ガス中の硫黄酸化物
との反応に起因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
解炉に投入するとともに、石炭だきボイラの高温
燃焼排ガスをこの分解炉に吹き込み固気接触させ
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器
に導入して分解ガスと石炭灰とを分離し、石炭灰
を冷却器にて空気で冷却した後灰処理設備に輸送
し、冷却器で高温石炭灰と熱交換した後の加熱空
気を分解炉上流側の石炭灰輸送管に吹き込んでア
ンモニウム含有石炭灰分解炉投入用空気およびア
ンモニウム含有石炭灰予熱用空気として使用し、
固気分離器よりの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することを特徴とする石
炭灰よりのアンモニウム化合物の除去方法。1 Coal-fired boiler exhaust gas is introduced in a highly dusty state to an ammonia catalytic reduction type denitrification device for denitrification, then the exhaust gas is introduced to an air preheater to preheat the combustion air, and then the exhaust gas is passed to a low-temperature dust collector. In the method of introduction and dust removal, the coal ash collected by the dust collector containing ammonium compounds resulting from the reaction between leaked ammonia from the denitrification equipment and sulfur oxides in the exhaust gas is introduced into an ammonium compound pyrolysis furnace. At the same time, high-temperature combustion exhaust gas from a coal-fired boiler is blown into this decomposition furnace and brought into solid-gas contact to decompose ammonium compounds in the coal ash.
The cracked gas containing coal ash from the cracking furnace is introduced into a solid-gas separator to separate the cracked gas and coal ash.The coal ash is cooled with air in a cooler and then transported to an ash processing facility. The heated air that has undergone heat exchange with the high-temperature coal ash is blown into the coal ash transport pipe on the upstream side of the cracking furnace and used as air for charging the ammonium-containing coal ash into the cracking furnace and as air for preheating the ammonium-containing coal ash.
A method for removing ammonium compounds from coal ash, characterized in that the cracked gas from the solid-gas separator is returned to the front of the denitrification device and reused as an ammonia source.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6313580A JPS56161823A (en) | 1980-05-13 | 1980-05-13 | Removal of ammonium compound from coal ash |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6313580A JPS56161823A (en) | 1980-05-13 | 1980-05-13 | Removal of ammonium compound from coal ash |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS56161823A JPS56161823A (en) | 1981-12-12 |
| JPS6332494B2 true JPS6332494B2 (en) | 1988-06-30 |
Family
ID=13220517
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP6313580A Granted JPS56161823A (en) | 1980-05-13 | 1980-05-13 | Removal of ammonium compound from coal ash |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS56161823A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2003507153A (en) | 1999-08-17 | 2003-02-25 | ウィスコンシン エレクトリック パワー カンパニー | Removal of ammonia from fly ash |
| KR100469583B1 (en) * | 2002-10-28 | 2005-02-02 | 한국전력공사 | Apparatus and Process for purifying fly ash by using a continuous operating reactor with rotary guide blades |
-
1980
- 1980-05-13 JP JP6313580A patent/JPS56161823A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS56161823A (en) | 1981-12-12 |
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