JPH05261244A - Method for removing hydrogen chloride in combustion gas - Google Patents

Method for removing hydrogen chloride in combustion gas

Info

Publication number
JPH05261244A
JPH05261244A JP4090078A JP9007892A JPH05261244A JP H05261244 A JPH05261244 A JP H05261244A JP 4090078 A JP4090078 A JP 4090078A JP 9007892 A JP9007892 A JP 9007892A JP H05261244 A JPH05261244 A JP H05261244A
Authority
JP
Japan
Prior art keywords
reactor
exhaust gas
desalting
desalting agent
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.)
Pending
Application number
JP4090078A
Other languages
Japanese (ja)
Inventor
Nobutake Yamamoto
信武 山本
Takao Sekino
隆夫 関野
Kazuyuki Koyama
一幸 小山
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.)
Denka Consultant and Engineering Co Ltd
Original Assignee
Denka Consultant and Engineering Co 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 Denka Consultant and Engineering Co Ltd filed Critical Denka Consultant and Engineering Co Ltd
Priority to JP4090078A priority Critical patent/JPH05261244A/en
Publication of JPH05261244A publication Critical patent/JPH05261244A/en
Pending legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Chimneys And Flues (AREA)

Abstract

PURPOSE:To effectively remove HCl in high temp. exhaust gas with equipment which is manufactured at low cost. CONSTITUTION:In the 1st reactor 3, high temp. exhaust gas is cooled to a low temp. and simultaneously humidified by cold water spraying and given dry desalting by spraying a powdery desalting agent from nozzles 5, 6. Next, in the 2nd reactor 8, after the exhaust gas is given semi-dry desalting by spraying (9) dilute anionic alkaline water solution, it is given solid-gas separation by a bag filter 11 together with the reactional product and unreacted material.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】この発明は、ゴミ焼却炉などから
排出する高温排ガス中の塩化水素ガスを除去する方法に
関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for removing hydrogen chloride gas in high temperature exhaust gas discharged from a refuse incinerator or the like.

【0002】[0002]

【従来の技術】高温排ガス中の塩化水素ガスを脱塩剤を
用いて科学的に除去する方法は多数提案されており脱塩
剤として消石灰とアルカリ性水溶液を用いる方法が公知
である。(例えば特開昭59−127656) この方法は、電気集塵機の前段で、消石灰粉末を乾式で
使用し、後段にアルカリ溶液を湿式で作用させるもので
ある。この除去方法においては電気集塵機が不可欠であ
る上、前段で作用させた脱塩剤が電気集塵機によって捕
捉されてしまい反応系における接触時間が短いため効率
が低い。更に、後段で作用させるアルカリ液は湿式で作
用させるので廃水処理設備が必要でコスト高になる。ま
た、この方法においてはダイオキシン等の有機系塩素化
合物を除去することが困難である。
2. Description of the Related Art Many methods for scientifically removing hydrogen chloride gas in high-temperature exhaust gas by using a desalting agent have been proposed, and a method using slaked lime and an alkaline aqueous solution as the desalting agent is known. (For example, Japanese Unexamined Patent Publication No. 59-127656) In this method, slaked lime powder is used in a dry type in the front stage of an electrostatic precipitator, and an alkaline solution is allowed to act in a wet stage in the rear stage. In this removal method, an electrostatic precipitator is indispensable, and the desalting agent acted in the previous stage is captured by the electrostatic precipitator, and the contact time in the reaction system is short, so that the efficiency is low. Further, since the alkaline liquid which acts in the latter stage is acted in a wet manner, a wastewater treatment facility is required and the cost becomes high. Moreover, it is difficult to remove organic chlorine compounds such as dioxins by this method.

【0003】更に、他の方法として特開昭60−227
817に提案されているように集塵機の前段で脱塩剤を
乾式で作用させ、次いで該脱塩剤の水溶液又は水スラリ
ーを半乾式で作用させることも公知である。この方法
は、乾式と半乾式で用いる脱塩剤が同一物質であるので
温度と脱塩度を別個に管理できる長所がある反面、装置
の大型化、雑雑化が避けられず、また多量の脱塩剤が必
要(Ca/Cl当量比約3)であることからランニング
コストが高くなる。加えて脱塩度を高めるために燃焼ガ
ス中の湿分を高めることが必要でこのため装置の腐食等
を生じ易い欠点がある。
Further, as another method, JP-A-60-227
It is also known to act the desalting agent in a dry manner before the dust collector as proposed in 817, and then to act an aqueous solution or water slurry of the desalting agent in a semi-dry manner. This method has the advantage that the desalting agent used in the dry type and the semi-dry type are the same substance, so that the temperature and desalting degree can be controlled separately, but on the other hand, the size and complexity of the device are inevitable and a large amount of Since a desalting agent is necessary (Ca / Cl equivalent ratio of about 3), the running cost becomes high. In addition, it is necessary to increase the moisture content in the combustion gas in order to increase the degree of desalination, which causes a drawback that corrosion of the device is likely to occur.

【0004】[0004]

【解決しようとする問題点】本発明は、少量の脱塩剤で
高脱塩ができ、しかも特殊又は高級な機質を使用しない
通常の装置でも腐食のおそれがない脱塩方法を提供する
ものである。
DISCLOSURE OF THE INVENTION The present invention provides a desalting method capable of highly desalting with a small amount of a desalting agent and free from the risk of corrosion even in an ordinary apparatus that does not use a special or high-grade machine. Is.

【0005】[0005]

【解決するための手段】本発明方法は、燃焼装置から排
出された高温排ガスを第1反応器の底部に導入すると共
に冷水を噴霧して急冷と加湿を行い、次いで該反応器の
上部からアルカリ土類金属の水酸化物又はその塩からな
る粉末脱塩剤を噴射する工程と、前記第1反応器からの
ガスを第2反応容器の上部に導入してアルカリ水溶液の
噴霧微粒と接触せしめて降下させる工程と、前記第2反
応器の底部から濾布式集塵器を通して大気中に放出させ
る工程とからなるものであって脱塩剤の総使用量が従来
法より少なくなり、また操業が容易である。
According to the method of the present invention, high temperature exhaust gas discharged from a combustion apparatus is introduced into the bottom of a first reactor, and cold water is sprayed to perform quenching and humidification, and then an alkali is discharged from the top of the reactor. A step of injecting a powder desalting agent comprising a hydroxide of an earth metal or a salt thereof, and introducing gas from the first reactor into the upper part of the second reaction vessel to bring it into contact with atomized fine particles of an alkaline aqueous solution. The process comprises a step of lowering and a step of releasing from the bottom of the second reactor into the atmosphere through a filter cloth type dust collector, the total amount of the desalting agent used is smaller than in the conventional method, and the operation is It's easy.

【0006】本発明において、第1反応器内での未反応
粉末脱塩剤は第2反応器内においても脱塩作用を発揮で
きるばかりでなく濾布式集塵機においても脱塩余力を残
す粉体膜を形成し最后まで脱塩機能を維持する。このた
め使用する脱塩剤の総量は少なくなり経済的な操業が可
能になる。
In the present invention, the unreacted powder desalting agent in the first reactor can not only exert the desalting action in the second reactor but also leave a desalination reserve in the filter cloth type dust collector. A membrane is formed and the desalination function is maintained until the end. For this reason, the total amount of the desalting agent used becomes small, and economical operation becomes possible.

【0007】本発明においては、第1反応器の乾式部、
第2反応器の半乾式部のそれぞれの脱塩度は任意に調製
可能であるが、ランニングコストの低減装置への付着及
び腐食トラブル防止等の点から乾式部では排ガス含有塩
化物の化学中和当量より多い脱塩剤を添加し、半乾式部
では同化学中和当量より少ない脱塩剤量とする。即ち、
通常の排ガス処理において乾式部における粉末脱塩剤は
1.0〜2.0中和化学当量であり、半乾式部で添加す
るアルカリ液は0.1〜0.5中和化学当量で充分であ
る。
In the present invention, the dry section of the first reactor,
The desalination degree of each of the semi-dry section of the second reactor can be adjusted as desired, but in the dry section, chemical neutralization of the chloride containing exhaust gas is possible from the viewpoints of adhesion to the equipment for reducing running cost and prevention of corrosion trouble. The desalting agent is added in an amount larger than the equivalent amount, and the amount of the desalting agent in the semi-dry type portion is smaller than the chemical neutralization equivalent amount. That is,
In normal exhaust gas treatment, the powder desalting agent in the dry part has a neutralization chemical equivalent of 1.0 to 2.0, and the alkaline liquid added in the semi-dry part has a neutralization chemical equivalent of 0.1 to 0.5. is there.

【0008】更に本発明においては、第1反応器の底部
つまり高温排ガス導入域に主としてオキシダントの発生
を抑える目的で噴出させる水によって冷却と同時に加湿
が行われ、これによって乾式脱塩部での反応性が高めら
れ、高脱塩度が達成されるのである。また第2反応器で
は半乾式脱塩部となるから腐食限界温度より高い温度で
運転することができ、この結果高脱塩できる他、排液処
理等の付加設備も全く不要である。
Further, in the present invention, water is ejected mainly at the bottom of the first reactor, that is, the high temperature exhaust gas introduction region for the purpose of suppressing the generation of oxidant, while cooling and humidification are carried out, whereby the reaction in the dry desalination section is carried out. The property is enhanced and a high degree of desalination is achieved. Further, since the second reactor is a semi-dry desalination section, it can be operated at a temperature higher than the corrosion limit temperature, and as a result, high desalination can be performed, and additional equipment such as drainage treatment is not required at all.

【0009】[0009]

【装置の説明】図1において回転焼却炉1からのHCl
含有(1000〜2000mg/Nm3)高温排ガス
は、後燃焼室2を通って第1反応器3の底部3bに導入
され、ノズル4からの冷水噴霧によって300°以下に
急冷される。反応器の上部3aに設けられた脱塩剤噴射
ノズル5.6から消石灰(Ca(oH)2 粉末が噴射さ
れる。Ca(OH)2 の投入量は、排ガス中のHClに
対し化学当量比で1.0〜2.0である。この脱塩剤噴
射域を通過するガスは温度200°〜300°Cに低下
すると共に湿分19〜24重量%程度になる。排ガス
は、導管7によって第2反応器8の上部8aに導入さ
れ、噴霧ノズル9から0.1〜10重量%のNaOH液
を噴霧される。NaOHの投入量は前記排ガス中のHC
lに対して化学当量比0.5〜0.1とする。第2反応
器の底部8bにおいてガス温度は150〜200°Cに
降下し湿分22〜26重量%となる。この低温化脱塩排
ガスは、更に冷却導管10を通って濾布式集塵機11に
導入されて固気分離され、脱塩排ガスはファン12によ
って大気中に放出される。第1反応器の内面はキャスタ
張りであるが、第2反応器の内面はテフロンコートであ
って、その容積は第1容器より2倍以上大きいものが好
ましい。
[Explanation of apparatus] In FIG. 1, HCl from the rotary incinerator 1
The contained (1000 to 2000 mg / Nm3) high-temperature exhaust gas is introduced into the bottom portion 3b of the first reactor 3 through the post-combustion chamber 2, and is rapidly cooled to 300 ° or less by cold water spray from the nozzle 4. Slaked lime (Ca (oH) 2 powder is injected from a desalting agent injection nozzle 5.6 provided in the upper part 3a of the reactor. The amount of Ca (OH) 2 added is a chemical equivalent ratio to HCl in exhaust gas. The gas passing through the desalting agent injection region has a temperature of 200 ° to 300 ° C. and a moisture content of about 19 to 24% by weight. It is introduced into the upper portion 8a of the second reactor 8 and sprayed with 0.1-10 wt% of NaOH liquid from the spray nozzle 9. The amount of NaOH charged is HC in the exhaust gas.
The chemical equivalent ratio is 0.5 to 0.1 with respect to 1. In the bottom portion 8b of the second reactor, the gas temperature drops to 150 to 200 ° C and the moisture content becomes 22 to 26% by weight. The low temperature desalted exhaust gas is further introduced into the filter cloth type dust collector 11 through the cooling conduit 10 and solid-gas separated, and the desalted exhaust gas is discharged into the atmosphere by the fan 12. Although the inner surface of the first reactor is caster-tensioned, the inner surface of the second reactor is preferably Teflon-coated, and its volume is preferably at least twice as large as that of the first container.

【0010】[0010]

【実施例】温度830°C、Hcl含有量1700mg
/Nm3 の高温排ガスを第1反応器3に1050Nm3
/Hrで導入した。反応器の中間部での温度は280°
Cに冷却された。噴射ノズル5.6からCa(OH)2
粉末をCa/cl当量比1.3量として噴射させて1次
脱塩した後、第2反応器8のノズル9から0.5%Na
OH水溶液をNa/cl比0.2量で噴霧した。反応器
底部8bの温度は180°Cであった。反応器を通過し
た反応物、未反応物の固気混合物中の固形分はバグフィ
ルタ11で除去され、大気放出前のHCl濃度は平均5
2mg/Nm3 であった。
Example: Temperature 830 ° C, Hcl content 1700 mg
/ Nm 3 of high temperature exhaust gas into the first reactor 3 by 1050 Nm 3
/ Hr. Temperature in the middle of the reactor is 280 °
Cooled to C. Ca (OH) 2 from the injection nozzle 5.6
After spraying the powder at a Ca / cl equivalent ratio of 1.3 to perform primary desalting, 0.5% Na was discharged from the nozzle 9 of the second reactor 8.
Aqueous OH was sprayed at a Na / cl ratio of 0.2 volume. The temperature of the bottom part 8b of the reactor was 180 ° C. The solid content in the solid-gas mixture of the reactants and unreacted materials that have passed through the reactor is removed by the bag filter 11, and the HCl concentration before being released into the atmosphere is 5 on average.
It was 2 mg / Nm 3 .

【0011】[0011]

【効果】本発明は、第1反応器において粉末脱塩剤を使
用し、第2反応器においては液体脱塩剤を使用し両者を
夫々単独で取扱うので操業が容易である上、トラブル発
生が少なくなる。脱塩性能が化学中和当量で約2倍程度
まで改善されるので脱塩剤使用量が少なくなりランニン
グコストが低減される。各反応器における反応生成物及
び未反応脱塩剤含有物が粉末状物として系外に取出せる
ので作業が簡単になる。また、スラリー化装置等附属設
備が不要で装置の全体構成が簡略化できる等の利点があ
る。
[Effect] According to the present invention, since the powder desalting agent is used in the first reactor and the liquid desalting agent is used in the second reactor, both of them are handled individually, which facilitates the operation and causes no trouble. Less. Since the desalination performance is improved to about twice as much as the chemical neutralization equivalent, the amount of desalting agent used is reduced and the running cost is reduced. Since the reaction product in each reactor and the unreacted desalting agent-containing material can be taken out of the system as a powdery product, the work is simplified. Further, there is an advantage that an auxiliary equipment such as a slurry forming device is not required and the entire structure of the device can be simplified.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明方法を実施する装置の全体構成図FIG. 1 is an overall configuration diagram of an apparatus for carrying out the method of the present invention.

【符号の説明】[Explanation of symbols]

3は第1反応器 5、6は粉末脱塩剤噴射ノズル 8は第2反応器 9はアルカリ水溶液噴霧ノズル 11はバグフィルタ 3 is a first reactor 5, 6 is a powder desalting agent injection nozzle 8 is a second reactor 9 is an alkaline aqueous solution spray nozzle 11 is a bag filter

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】粉末脱塩剤とアルカリ水溶液を使用して燃
焼ガス中の塩化水素を除去する方法において、高温排ガ
スを第1反応器の底部に導入すると共に冷水を噴霧して
急冷と加湿を行い、次いで該反応器の上部からアルカリ
土類金属の水酸化物又はその塩からなる粉末脱塩剤を噴
射する工程と、前記第1反応器からのガスを第2反応容
器の上部に導入してアルカリ水溶液の噴霧微粒と接触せ
しめて降下させる工程と、前記第2反応器内の粉体含有
気体を濾布式集塵器に導入して通過脱塩排ガスを大気中
に放出させる工程とからなる燃焼ガス中の塩化水素を除
去する方法。
1. A method for removing hydrogen chloride in a combustion gas using a powder desalting agent and an alkaline aqueous solution, wherein hot exhaust gas is introduced into the bottom of a first reactor and cold water is sprayed to quench and humidify. And then injecting a powdered desalting agent consisting of an alkaline earth metal hydroxide or its salt from the upper part of the reactor, and introducing the gas from the first reactor to the upper part of the second reaction vessel. Contacting with the sprayed fine particles of the alkaline aqueous solution to lower it, and introducing the powder-containing gas in the second reactor into the filter cloth type dust collector to release the passing desalted exhaust gas into the atmosphere. Method for removing hydrogen chloride from combustion gas.
【請求項2】粉末脱塩剤の量が排ガス中の塩化水素に対
して1.0〜2.0化学当量であり、噴霧アルカリ水溶
液の量が0.1〜0.5化学当量である請求項1記載の
方法。
2. The amount of the powder desalting agent is 1.0 to 2.0 chemical equivalents to the hydrogen chloride in the exhaust gas, and the amount of the sprayed alkaline aqueous solution is 0.1 to 0.5 chemical equivalents. The method according to item 1.
JP4090078A 1992-03-17 1992-03-17 Method for removing hydrogen chloride in combustion gas Pending JPH05261244A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4090078A JPH05261244A (en) 1992-03-17 1992-03-17 Method for removing hydrogen chloride in combustion gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4090078A JPH05261244A (en) 1992-03-17 1992-03-17 Method for removing hydrogen chloride in combustion gas

Publications (1)

Publication Number Publication Date
JPH05261244A true JPH05261244A (en) 1993-10-12

Family

ID=13988492

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4090078A Pending JPH05261244A (en) 1992-03-17 1992-03-17 Method for removing hydrogen chloride in combustion gas

Country Status (1)

Country Link
JP (1) JPH05261244A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008229416A (en) * 2007-03-16 2008-10-02 Mitsui Eng & Shipbuild Co Ltd Apparatus and method for removing acidic gas contained in exhaust gas
JP2010234175A (en) * 2009-03-30 2010-10-21 Jfe Engineering Corp Exhaust gas treatment method

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5660626A (en) * 1979-10-22 1981-05-25 Hitachi Plant Eng & Constr Co Ltd Process for treating hydrogen-chloride-containing waste gas
JPS56119415A (en) * 1980-02-25 1981-09-19 Mitsubishi Heavy Ind Ltd Waste incinerating furnace

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5660626A (en) * 1979-10-22 1981-05-25 Hitachi Plant Eng & Constr Co Ltd Process for treating hydrogen-chloride-containing waste gas
JPS56119415A (en) * 1980-02-25 1981-09-19 Mitsubishi Heavy Ind Ltd Waste incinerating furnace

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008229416A (en) * 2007-03-16 2008-10-02 Mitsui Eng & Shipbuild Co Ltd Apparatus and method for removing acidic gas contained in exhaust gas
JP2010234175A (en) * 2009-03-30 2010-10-21 Jfe Engineering Corp Exhaust gas treatment method

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