JPS58124115A - Processing method of waste gas of coal boiler - Google Patents

Processing method of waste gas of coal boiler

Info

Publication number
JPS58124115A
JPS58124115A JP57006858A JP685882A JPS58124115A JP S58124115 A JPS58124115 A JP S58124115A JP 57006858 A JP57006858 A JP 57006858A JP 685882 A JP685882 A JP 685882A JP S58124115 A JPS58124115 A JP S58124115A
Authority
JP
Japan
Prior art keywords
fly ash
gas
boiler
salt
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.)
Granted
Application number
JP57006858A
Other languages
Japanese (ja)
Other versions
JPH0131084B2 (en
Inventor
Shigeyuki Noso
能祖 茂幸
Isamu Shimura
勇 志村
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sumitomo Heavy Industries Ltd
Original Assignee
Sumitomo Heavy Industries Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Sumitomo Heavy Industries Ltd filed Critical Sumitomo Heavy Industries Ltd
Priority to JP57006858A priority Critical patent/JPS58124115A/en
Publication of JPS58124115A publication Critical patent/JPS58124115A/en
Publication of JPH0131084B2 publication Critical patent/JPH0131084B2/ja
Granted legal-status Critical Current

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J3/00Removing solid residues from passages or chambers beyond the fire, e.g. from flues by soot blowers
    • F23J3/06Systems for accumulating residues from different parts of furnace plant

Landscapes

  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Chimneys And Flues (AREA)

Abstract

PURPOSE:To enable an easy deamination of NH4 salt from fly ash without using a particular deaminating device only by throwing the fly ash including NH4 salt into a circulative gas. CONSTITUTION:The fly ash generated from the boiler 1, passing thoug a denitrating device 2 and an air preheater 3, is gathered by a low temperature electric ash collecting device 4 as in the NH4 salt attached state. The fly ash attached with the NH4 salt and gathered by the device 4 is then thrown into the circulative gas to the boiler 1 and finally collected by the ash collector 9 which is provided for protecting a circulation blower 10. In this while, the fly ash is heated by a large amount of circulative gas and deaminated. Thus the deamination of NH4 salt from the fly ash can be easily performed without using any particular device.

Description

【発明の詳細な説明】 石炭だきボイラーに於て、窒素酸化物(以下NOメとい
う)の排出量を抑える経埼釣方法として。
[Detailed Description of the Invention] As a fishing method for reducing the amount of nitrogen oxides (hereinafter referred to as NOMe) emitted from coal-fired boilers.

2段燃焼あるいは排ガス循還方式による低yof燃焼方
式により、出来るかぎりボイラーからのMO□発生量を
おさえたのち、ボイラー排ガスを脱硝装置に導入し、N
Ox排出賞を抑えている。
After suppressing the amount of MO□ generated from the boiler as much as possible by using a low yof combustion method using two-stage combustion or an exhaust gas recirculation method, the boiler exhaust gas is introduced into the denitrification equipment and N
It suppresses the Ox emission award.

脱硝装置としては、現在では乾式のアンモニア接触分解
方式が主流である。ところが、上記脱硝装置を用いると
、脱硝装置からの漏洩アンモニアト排ガス中の硫黄酸化
物により硫酸アンモニウム塩(以下!’JH,4L[と
いう)が生成し、NH4’ 4を含んだガスが冷却され
ると、NH4塩を析出する。しかもガス中に微細なフラ
イアッシュが存在すると、NI?’。
Dry ammonia catalytic cracking systems are currently the mainstream denitrification equipment. However, when the above denitrification equipment is used, ammonium sulfate salt (hereinafter referred to as !'JH,4L) is produced by sulfur oxides in the ammonium exhaust gas leaking from the denitrification equipment, and the gas containing NH4'4 is cooled. and NH4 salt is precipitated. Moreover, if fine fly ash is present in the gas, NI? '.

塩は優先的に上記フライアッシュ表面に析出する。Salt preferentially precipitates on the surface of the fly ash.

従って脱硝装置より後の流れに世温EP4を設は走場合
にば、は温EPt’補果したフライアッシュにはNH4
塩が付層している。
Therefore, if Seon EP4 is installed in the flow after the denitrification equipment, the fly ash supplemented with Seon EPt' will have NH4
There is a layer of salt.

本発明はか\るフライアッシュからNH4mを分解・脱
離(以ド脱安という)するプロセスに関するもので、惺
めて簡単なプロセスで、しがも低いランニングコストの
脱安プロセスを提供しようとするものである。
The present invention relates to a process for decomposing and desorbing NH4m from fly ash (hereinafter referred to as deanxification), and aims to provide a deanxification process that is extremely simple and has low running costs. It is something to do.

現在脱安プロセスとして確立されたものはないが、促米
から一★的に第1図のものがしられている。石炭だきボ
イラー1から発”生じたフライアッシュは、脱銅装置2
及び空気予熱慎5を通過するコ(!: K L ツテ@
[I K M Ha塩を付層した状態で低温EP4でm
東される。は温ICP4で捕集されたNH4雀の付層し
たフライアッシュは、呪女装置5で昇温、脱安されて泉
−慎6によって回収される。
There is currently no established devaluation process, but the one in Figure 1 is generally known from the promotion of rice. The fly ash generated from coal-fired boiler 1 is transferred to decopper removal equipment 2.
and passing through the air preheating section 5 (!: K L Tsute@
[I K M M with a layer of Ha salt at low temperature EP4
To be easted. The fly ash layered with NH4 sparrow collected by the hot ICP 4 is heated and decompressed by the Jujo device 5 and recovered by the Izumi-Shin 6.

前に戻される。なお、脱安熱源としてはボイラー1から
の抽気ガスでも艮いし、補助燃料を用いて熱風発生炉7
から発生させた熱風でもよい。勿論両者の併用でもよい
be brought back to the front. In addition, the extraction gas from the boiler 1 can also be used as a heat source for detangling, and the hot air generating furnace 7 can be heated using auxiliary fuel.
It may also be hot air generated from. Of course, both may be used together.

第1図のプロセスはNOX抑制方式として脱硝装置2の
みについて考直しておシ、脱硝装置11i2と排ガス循
環方式を含む低NOX燃焼方式が併用された場合につい
ては考慮されていない。きらに成安装瀘5が必要である
ことから、プロセスは複鑵になる上に脱簀熱源を必要と
するため、脱安に要するランニングコストは可成り^く
なる。又NH4Mの分解に際し、硫黄酸化物が発生する
ため、硫黄酸化物が凝縮され、好ましくない机縁を惹起
する。
In the process shown in FIG. 1, only the denitrification device 2 is considered as the NOX suppression method, and the case where the denitrification device 11i2 and a low NOX combustion method including an exhaust gas circulation method are used together is not considered. Since a seian equipment 5 is required in the process, the process becomes complicated and requires a heat source for desalination, so the running cost required for desalination becomes considerable. Furthermore, since sulfur oxides are generated during the decomposition of NH4M, the sulfur oxides are condensed, causing unfavorable circumstances.

本発明は前記の欠点を補うべくlヨされたものである。The present invention has been developed to overcome the above-mentioned drawbacks.

以ドこれを第2図を参照に説明する。第2図はNOX抑
制方法として脱硝装置112と排ガス循環方式を含む低
NOX燃焼方式を併用した場合についての脱安プロセス
である。
This will be explained below with reference to FIG. FIG. 2 shows a deoxidization process when a denitrification device 112 and a low NOX combustion system including an exhaust gas circulation system are used together as a NOX suppression method.

ボイラー1より発生したフライアッシュは脱硝装置2及
び空気予熱愼3を通ることによって表面にNH4塩が付
着した状態で低m ff1P4で捕集される。
The fly ash generated from the boiler 1 passes through the denitrification device 2 and the air preheating tank 3 and is collected at a low mff1P4 with NH4 salts attached to the surface.

低d WF2で捕集されたNH4mの付着したフライア
ッシュはボイラー1への循還ガス中に投入され、循環ブ
ロワ−10の保禮のために設けられた集塵機9で回収さ
れるまでに大量の循環ガスによって昇温、脱安され集1
lII機9で回収される。
The fly ash with adhering NH4m collected by the low d WF2 is put into the circulating gas to the boiler 1, and a large amount of fly ash is collected by the dust collector 9 installed to protect the circulating blower 10. The temperature is raised by the circulating gas, and the temperature is removed.
Recovered by II machine 9.

ダンパー11及び12は循環ガス温度のコントロールの
ために設けられている。即ち、ボイラー1の出口の主循
環ガスm度が世過ぎる場合にはフライアブシュの脱安4
が低くなる。このような場合ボイラー1から高温ガス(
例えばエコノマイザ−人口ガス)を抽気し、主循環ガス
に加え、一方では主循環ガス蓋を減少させて、循環ガス
温度を一定に保つ為のガス量調節ダ/バーとして設けら
れている。
Dampers 11 and 12 are provided for controlling the circulating gas temperature. That is, if the main circulating gas at the outlet of the boiler 1 is too high, the fly bush will be de-assembled.
becomes lower. In such a case, hot gas (
For example, an economizer (artificial gas) is extracted and added to the main circulating gas, while the main circulating gas cap is reduced to serve as a gas volume control da/bar to keep the circulating gas temperature constant.

第2図においては、フライアッシュの投入場所は主循環
ガスとボイラー1からの抽気ガスが混合した゛あとで示
しておるが、ボイラー1からの抽気ガス蓋を低減するた
めにダンパー12の直鎖に投入する方法も考えられる。
In Fig. 2, the place where fly ash is introduced is shown after the main circulation gas and the bleed gas from boiler 1 are mixed, but in order to reduce the bleed gas from boiler 1, the damper 12 is placed in a straight chain. Another possible method is to invest in

集塵機9を通過した清浄な循環ガスはボイラー1に戻さ
れるため、脱安過程で生じた硫黄酸化物は分解され、硫
黄酸化物の濃縮という現象は起らない。
Since the clean circulating gas that has passed through the dust collector 9 is returned to the boiler 1, the sulfur oxides generated during the desulfurization process are decomposed, and the phenomenon of concentration of sulfur oxides does not occur.

第3図は4編機9の効率が低く、極めて微細なフライア
ッシュが集m機9で捕集されずに循環し、本プロセス中
のフライアッシュ濃度が増加してしまう場合の対策例て
゛ある。即ち低温IP4で捕集したフライアッシュの極
めて微細なフライアッシュを循環ガス中に投入する前に
分子Itk機13でとシ除いてしまう方法である。
Figure 3 shows an example of countermeasures in the case where the efficiency of the four-knitting machine 9 is low and extremely fine fly ash circulates without being collected by the collector 9, increasing the fly ash concentration during this process. . That is, this is a method in which the extremely fine fly ash collected in the low-temperature IP4 is removed by the molecular Itk machine 13 before being introduced into the circulating gas.

以上の如き構成であって、NH4塩の付着したフライア
ッシュを循環ガス中に投入することによって[4ガスの
熱によってフライアッシュは脱安さnるので、特殊な脱
安装置を必要とせず、フライアッシュからNH4塩の脱
安を行うことができる。
With the above configuration, by introducing the fly ash with NH4 salt attached into the circulating gas, the heat of the gas debases the fly ash, so there is no need for a special debasement device. The NH4 salt can be removed from the ash.

本発明によれば、脱安装置が必g1なく、極めて蘭素化
された脱安プロセスとなる。さらに脱安熱源を必要とし
ないので、脱安のためのランニング又脱安排ガスはボイ
ラーに戻されるため、NH4塩の分解によって生じた硫
黄酸化物は分解され、硫黄酸化物の濃縮は起らない。
According to the present invention, the de-anxification device is not required and the de-anxification process is extremely simple. Furthermore, since a heat source for desulfurization is not required, the running for desulfurization and the desulfurization exhaust gas are returned to the boiler, so the sulfur oxides produced by the decomposition of NH4 salts are decomposed, and no concentration of sulfur oxides occurs. .

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は従来公知石炭だきボイラ排ガスの処理方法。 第2図は本発明に係る石炭だき排ガスの処理方法。 第3図は本発明の他の実施例を示す図である。 図において; 1  石炭だきボイラー    2 脱硝装置3  空
気予熱機     4 低温電気集塵装置5 脱安装置
     6 集 塵 機7  熱風発生炉     
 8  回収フライアッシュ9 果 塵 機   1G
  循環ブロワ−11ダンパー    12  ダンパ
ー13分級機 以上 出願人 住友重慎械工業株式会社 代理人 弁理士小山酩三部(外l 復代理人 弁理士 大 橋   勇 第1WJ 1 第3図 第2図
Figure 1 shows a conventional method for treating coal-fired boiler exhaust gas. FIG. 2 shows a method for treating coal-fired exhaust gas according to the present invention. FIG. 3 is a diagram showing another embodiment of the present invention. In the figure: 1 Coal-fired boiler 2 Denitrification device 3 Air preheater 4 Low-temperature electrostatic precipitator 5 De-balance device 6 Dust collector 7 Hot air generator
8 Recovered fly ash 9 Fruit dust machine 1G
Circulating blower - 11 dampers 12 dampers 13 classifiers and above Applicant: Sumitomo Heavy Industries Co., Ltd. Agent: Patent Attorney Kazuo Koyama, Sub-agent: Isamu Ohashi, Patent Attorney 1st WJ 1 Fig. 3 Fig. 2

Claims (1)

【特許請求の範囲】[Claims] 石炭だきボイラ排ガスをアンモニア接触還元方式の脱硝
装置に導入して脱硝し、低温集塵装置に導入して商塵し
、かつ、ボイラ出口併ガスの一部を前記ボイラに再循環
する方法において、前記低温集塵装置で捕集したアンモ
ニウム塩付着フライアッシュを前記再ON庫排ガス中へ
導入してアンモニウム塩を分解脱離し、さらに8備環排
ガスライン甲に設けた集塵装置によってフライアッシュ
を亦去することを%僅とする石炭だきボイラ排ガスの処
理方法。
A method in which coal-fired boiler exhaust gas is introduced into an ammonia catalytic reduction type denitrification device to denitrify it, introduced into a low-temperature dust collector to collect commercial dust, and a part of the boiler outlet gas is recycled to the boiler, The ammonium salt-adhered fly ash collected by the low-temperature dust collector is introduced into the re-ON storage exhaust gas to decompose and remove ammonium salts, and the fly ash is further removed by the dust collector installed in the 8-ring exhaust gas line A. A method for treating coal-fired boiler exhaust gas that requires very little waste gas.
JP57006858A 1982-01-21 1982-01-21 Processing method of waste gas of coal boiler Granted JPS58124115A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57006858A JPS58124115A (en) 1982-01-21 1982-01-21 Processing method of waste gas of coal boiler

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57006858A JPS58124115A (en) 1982-01-21 1982-01-21 Processing method of waste gas of coal boiler

Publications (2)

Publication Number Publication Date
JPS58124115A true JPS58124115A (en) 1983-07-23
JPH0131084B2 JPH0131084B2 (en) 1989-06-23

Family

ID=11649930

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57006858A Granted JPS58124115A (en) 1982-01-21 1982-01-21 Processing method of waste gas of coal boiler

Country Status (1)

Country Link
JP (1) JPS58124115A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6439138B1 (en) * 1998-05-29 2002-08-27 Hamon Research-Cottrell, Inc. Char for contaminant removal in resource recovery unit

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6439138B1 (en) * 1998-05-29 2002-08-27 Hamon Research-Cottrell, Inc. Char for contaminant removal in resource recovery unit
US6595147B2 (en) 1998-05-29 2003-07-22 Hamon Research-Cottrell, Inc. Method for adsorbing contaminants from flue gas

Also Published As

Publication number Publication date
JPH0131084B2 (en) 1989-06-23

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