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JPH0661424B2 - Method for removing mercury and acid gas in combustion exhaust gas - Google Patents
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JPH0661424B2 - Method for removing mercury and acid gas in combustion exhaust gas - Google Patents

Method for removing mercury and acid gas in combustion exhaust gas

Info

Publication number
JPH0661424B2
JPH0661424B2 JP61059426A JP5942686A JPH0661424B2 JP H0661424 B2 JPH0661424 B2 JP H0661424B2 JP 61059426 A JP61059426 A JP 61059426A JP 5942686 A JP5942686 A JP 5942686A JP H0661424 B2 JPH0661424 B2 JP H0661424B2
Authority
JP
Japan
Prior art keywords
mercury
exhaust gas
gas
powder
acid 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.)
Expired - Lifetime
Application number
JP61059426A
Other languages
Japanese (ja)
Other versions
JPS62216630A (en
Inventor
和夫 魚屋
公利 小瀬
成元 富沢
光弘 洞口
丈二 殿村
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi 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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP61059426A priority Critical patent/JPH0661424B2/en
Publication of JPS62216630A publication Critical patent/JPS62216630A/en
Publication of JPH0661424B2 publication Critical patent/JPH0661424B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は都市ごみ焼却炉、産廃焼却炉、し尿・下水汚泥
焼却炉の排ガス処理方法に関し、該排ガス中より水銀
(又は水銀化合物)及び酸性ガスを同時に除去する方法
に関する。
TECHNICAL FIELD The present invention relates to an exhaust gas treatment method for an incinerator for municipal solid waste, an incinerator for industrial waste, an incinerator for night soil / sewage sludge, wherein mercury (or mercury compound) and acid are contained in the exhaust gas. It relates to a method for simultaneously removing gases.

〔従来の技術〕 燃焼排ガス中に含まれる酸性ガス(例えば、HCl,SOx)
と水銀(又は水銀化合物)を除去する方法としては、湿
式法、すなわちpHを7〜9位に調整したアルカリ吸収液
中に液体キレートを添加して、この吸収液と排ガスとの
気液接触を図り、酸性ガスと水銀を同時に吸収液側へ移
行させる方法がある。{井出・古角・茂中“都市と廃棄
物”vol.15,No.5,67〜86(1985)}しかしながら、乾式
法で酸性ガスと水銀を同時に除去する方法は従来なかつ
た。
[Prior Art] Acidic gas (eg HCl, SOx) contained in combustion exhaust gas
And mercury (or mercury compounds) can be removed by a wet method, that is, by adding a liquid chelate to an alkali absorbing liquid whose pH is adjusted to 7-9, and contacting this absorbing liquid with exhaust gas. There is a method of transferring acidic gas and mercury to the absorption liquid side at the same time. {Ide, Furukaku, Shigenaka "Urban and Waste" vol.15, No.5, 67-86 (1985)} However, the method of simultaneously removing acid gas and mercury by the dry method has never been used.

〔発明が解決しようとする問題点〕[Problems to be solved by the invention]

本発明は、今までに行われていなかつた燃焼排ガス中に
含まれる酸性ガスと水銀を乾式法で同時に除去できる方
法を提供しようとするものである。
The present invention is intended to provide a method capable of simultaneously removing acid gas and mercury contained in a combustion exhaust gas, which has never been performed so far, by a dry method.

すなわち、酸性ガスを乾式法で除去する方法は従来から
あつたので、本発明では、燃焼排ガス中の水銀を乾式法
で除去するための方法と前記の乾式法による酸性ガス除
去方法との調和的接合方法を提供することを技術的課題
とするものである。
That is, since the method of removing the acidic gas by the dry method has been conventionally provided, the present invention provides a method for removing mercury in the combustion exhaust gas by the dry method in harmony with the method for removing the acidic gas by the dry method. It is a technical object to provide a joining method.

〔問題点を解決するための手段〕[Means for solving problems]

本発明は、燃焼排ガスの煙道中に、反応助剤と水銀反応
剤の混合粉末を噴射して排ガス中の水銀を粉体側へ固定
するとともに、酸性ガス中和剤粉末を噴射して排ガス中
の酸性ガスを除去し、噴射後方にバグフイルターを設け
て排ガス中より燃焼ばいじんと一緒に系外へ排出するこ
とを特徴とする燃焼排ガス中の水銀及び酸性ガス除去方
法である。
The present invention sprays a mixed powder of a reaction aid and a mercury reactant into a flue of a combustion exhaust gas to fix mercury in the exhaust gas to the powder side, and sprays an acid gas neutralizer powder into the exhaust gas. The method for removing mercury and acid gas in combustion exhaust gas is characterized in that the acid gas is removed, and a bag filter is provided behind the injection to discharge the gas together with the combustion dust from the exhaust gas to the outside of the system.

本発明においては、バグフイルターの通気性を高め、か
つ吸湿防止を図るために排ガス中に噴射する水銀反応剤
(S,FeS,ZnS,CaS,Cus)の粉末に反応助剤(ゼオライト,
アルミナ,ケイソウ土,パーライト,活性白土,カオリ
ン,長石等)の粉末を予め混合しておき、これらを同時
に排ガス煙道中に噴射する。反応助剤と水銀反応剤の混
合比は、排ガス条件によつて左右されるが、一般的には
重量比で水銀反応剤:反応助剤=1:1〜50、好まく
は1:1〜10である。
In the present invention, a mercury reactant that is injected into exhaust gas in order to increase the air permeability of the bag filter and prevent moisture absorption.
(S, FeS, ZnS, CaS, Cus) powder on the reaction aid (zeolite,
Powders of alumina, diatomaceous earth, perlite, activated clay, kaolin, feldspar, etc.) are mixed in advance, and these are simultaneously injected into the exhaust gas flue. The mixing ratio of the reaction auxiliary agent and the mercury reaction agent depends on the exhaust gas conditions, but generally, the weight ratio is as follows: mercury reaction agent: reaction auxiliary agent = 1: 1 to 50, preferably 1: 1 to It is 10.

又、酸性ガス中和剤(消石灰,炭酸カルシウム,酸化カ
ルシウム,水酸化マグネシウム,炭酸マグネシウム,酸
化マグネシウム等)粉末は上記混合粉末の噴射の前又は
後に排ガス煙道中に噴射する。水銀反応剤は酸性ガスの
共存下で活性化され易いので、酸性ガス中和剤は上記混
合粉末の噴射後に噴射することが好ましい。
Also, the acid gas neutralizing agent (slaked lime, calcium carbonate, calcium oxide, magnesium hydroxide, magnesium carbonate, magnesium oxide, etc.) powder is injected into the exhaust gas flue before or after the injection of the mixed powder. Since the mercury reactant is easily activated in the coexistence of the acidic gas, it is preferable to inject the acidic gas neutralizing agent after injecting the mixed powder.

このようにして、煙道中に噴射した粉末との各々の反応
生成物及び燃焼ばいじんをバグフイルタによつて効率よ
く捕集除去する。
In this way, each reaction product with the powder injected into the flue and combustion dust are efficiently collected and removed by the bag filter.

〔作用〕[Action]

(1) 本発明方法により、酸性ガスと水銀を同時に除去
できる。
(1) Acid gas and mercury can be removed simultaneously by the method of the present invention.

(2) 水銀反応剤を反応助剤に混合して同時に排ガス中
へ噴射できるため、水銀除去のため新たな設備を必要と
しない。
(2) Since the mercury reactant can be mixed with the reaction aid and injected into the exhaust gas at the same time, no new equipment is required for mercury removal.

(3) 水銀反応剤を反応助剤に混合するので、水銀反応
剤の粉末希釈が図れ、単独噴射の場合に比べて、排ガス
中への分散効果が高まる。
(3) Since the mercury reactant is mixed with the reaction aid, the mercury reactant can be diluted with powder, and the dispersion effect in the exhaust gas is enhanced as compared with the case of single injection.

(4) バグフイルター上で一部未反応の水銀反応剤及び
酸性ガス中和剤のケーキ層が形成されるので、その層を
排ガスが通過するとき、水銀と反応剤及び酸性ガスと中
和剤との固気反応が進行し、それぞれの除去効率が高ま
る。
(4) Since a cake layer of partially unreacted mercury reactant and acid gas neutralizer is formed on the bag filter, when exhaust gas passes through the layer, mercury and reactant and acid gas and neutralizer are formed. The solid-gas reaction with and progresses, and each removal efficiency improves.

以下、本発明の実施態様を第1図によつて詳述する。Hereinafter, an embodiment of the present invention will be described in detail with reference to FIG.

第1図において、1は燃焼排ガス発生源(例えば都市ご
み焼却炉,産廃焼却炉,し尿・下水汚泥焼却炉)、2は
排ガスダクト、3はバグフイルタ、4は排気フアン、5
は煙突、6は反応助剤と水銀反応剤混合サイロ、7,7′
は粉体定量供給機、8,8′は粉体輸送空気フアン、9は
酸性ガス中和剤サイロ、10,10′は粉供給ノズル、11
は捕集灰である。
In FIG. 1, 1 is a combustion exhaust gas generation source (eg, municipal waste incinerator, industrial waste incinerator, human waste / sewage sludge incinerator), 2 is an exhaust gas duct, 3 is a bag filter, 4 is an exhaust fan, and 5
Is a chimney, 6 is a silo for mixing a reaction aid and a mercury reactant, 7,7 '
Is a powder quantitative feeder, 8,8 'is a powder transportation air fan, 9 is an acid gas neutralizer silo, 10 and 10' are powder feeding nozzles, 11
Is the collected ash.

燃焼排ガス発生源1で発生した水銀と酸性ガスを含む燃
焼排ガス中に、バグフイルタ3のガス流れ前方の排ガス
ダクト2から、粉体供給ノズル10によつて反応助剤と
水銀反応混合粉体を噴射する。反応助剤と水銀反応混合
粉体は混合サイロ6から、粉体定量供給機7によつて所
定量切出し、粉体輸送フアン8から送られる空気によつ
て粉体供給ノズル10へ輸送する。つぎに、反応助剤と
水銀反応混合粉体を供給したガス流れ後方の排ガスダク
ト2から、同様にして酸性ガス中和剤を排ガス中へ噴射
する。
The reaction aid and the mercury reaction mixed powder are injected into the combustion exhaust gas containing mercury and acid gas generated in the combustion exhaust gas generation source 1 from the exhaust gas duct 2 in front of the gas flow of the bag filter 3 by the powder supply nozzle 10. To do. A predetermined amount of the reaction aid and the mercury reaction mixed powder are cut out from the mixing silo 6 by the powder quantitative feeder 7 and are transported to the powder feeding nozzle 10 by the air sent from the powder transport fan 8. Next, the acidic gas neutralizing agent is similarly injected into the exhaust gas from the exhaust gas duct 2 behind the gas flow to which the reaction aid and the mercury reaction mixed powder have been supplied.

反応助剤と水銀反応混合粉体の噴射位置と酸性ガス中和
剤の噴射位置は、上記位置と前後しても支障ないが、本
説明位置の方が好ましい。
The injection positions of the reaction aid and the mercury reaction mixed powder and the injection position of the acid gas neutralizing agent may be before or after the above position, but the present description position is preferable.

排ガス中に噴射された水銀反応剤及び酸性ガス中和剤は
各々、排ガス中の水銀及び酸性ガスと迅速に反応し水銀
及び酸性ガスをガス側から粉体側へ固定する。
The mercury reactant and the acid gas neutralizer injected into the exhaust gas rapidly react with the mercury and the acid gas in the exhaust gas to fix the mercury and the acid gas from the gas side to the powder side.

水銀及び酸性ガスを固定した反応剤及び中和剤と未反応
の反応剤及び中和剤、燃焼ばいじんは後流に位置するバ
グフイルタ3上に捕集され、逆洗操作によつて払い落さ
れて系外へ排出される。
Reactants and neutralizers with fixed mercury and acid gas, unreacted reactants and neutralizers, and combustion dust are collected on the bag filter 3 located downstream and washed off by backwashing operation. It is discharged outside the system.

未反応の水銀反応剤及び酸性ガス中和剤が一緒にバグフ
イルタ3上にケーキ層を形成するので、その層を排ガス
が通過するとき更に水銀及び酸性ガスと反応剤及び中和
剤との固気反応が進行し、各々の除去率が高まる。水銀
及び酸性ガスが取り除かれた燃焼ガスは、排気フアン4
を経由して煙突5より排出される。
Since the unreacted mercury reactant and the acid gas neutralizer together form a cake layer on the bag filter 3, when the exhaust gas passes through the layer, the solid gas of the mercury and the acid gas with the reactant and the neutralizer is further added. The reaction proceeds and the removal rate of each increases. Combustion gas from which mercury and acid gas have been removed is exhaust fan 4
It is discharged from the chimney 5 via the.

第2図にバグフイルタ3布表面の粉体堆積層の概念図を
示す。
FIG. 2 shows a conceptual diagram of the powder deposit layer on the surface of the bag filter 3 cloth.

排ガス中に噴射した水銀反応剤、酸性ガス中和剤、反応
助剤及び燃焼ばいじんは第2図に示すように、3布12
表面に逐次堆積していく。図中G1は排ガス、13は反応
助剤からなるプレコート層、14は堆積層、15は水銀
反応剤、16は酸性ガス中和剤、17は反応助剤の存在
を示す。
As shown in FIG. 2, the mercury reactant, the acid gas neutralizer, the reaction aid, and the combustion dust injected into the exhaust gas are 3 cloths 12 pieces.
Sequentially deposit on the surface. In the figure, G 1 is exhaust gas, 13 is a precoat layer made of a reaction aid, 14 is a deposition layer, 15 is a mercury reaction agent, 16 is an acid gas neutralizing agent, and 17 is the presence of the reaction aid.

ここで酸性ガス中和剤としては、消石灰、炭酸カルシウ
ム、酸化カルシウム、水酸化マグネシウム、炭酸マグネ
シウム、酸化マグネシウムなどのアルカリ中和剤が挙げ
られる。
Examples of the acid gas neutralizing agent include alkali neutralizing agents such as slaked lime, calcium carbonate, calcium oxide, magnesium hydroxide, magnesium carbonate and magnesium oxide.

水銀反応剤としては、S,FeS,ZnS,CaS,CuSが挙げられ
る。
Examples of the mercury reactant include S, FeS, ZnS, CaS and CuS.

反応助剤としては、ゼオライト、アルミナ、ケイソウ
土、パーライト、活性白土、カオリン、長石等の粉末の
中から選ばれた1種もしくは2種以上の混合粉末を使用
する。
As the reaction aid, one or more mixed powders selected from powders of zeolite, alumina, diatomaceous earth, perlite, activated clay, kaolin, feldspar, etc. are used.

<実施例> 都市ごみ焼却炉から排出される水銀とHClの除去を下記
条件にて行なつた。条件: 焼却量:150T/日 排ガス量:30,000Nm3/h Hg濃度:0.3mg/Nm3 HCl濃度:700ppm ガス温度:200〜230℃要領: 反応助剤と水銀反応剤の混合粉体を50kg/h{混合
比:反応助剤/水銀反応剤(重量比)1〜50}吹き込
んだ。反応助剤としてはパーライト、水銀反応剤として
は粒度200〜300メツシユのZnS粉末を使用した。混合
粉体噴射後、0秒から2〜3秒後に混合粉体を吹き込ん
だ後流で消石灰粉末100kg/h吹き込み、水銀とHCl
(酸性ガス)を除去した。結果: 上記試験の結果、排ガス中の水銀は最高76%、HClは
98.6%で除去できた。
<Example> The mercury and HCl discharged from the municipal waste incinerator were removed under the following conditions. Conditions: Incineration amount: 150 T / day Exhaust gas amount: 30,000 Nm 3 / h Hg concentration: 0.3 mg / Nm 3 HCl concentration: 700 ppm Gas temperature: 200 to 230 ° C. Procedure: 50 kg of mixed powder of reaction aid and mercury reactant / H {mixing ratio: reaction aid / mercury reactant (weight ratio) 1 to 50}. Perlite was used as the reaction aid, and ZnS powder with a particle size of 200 to 300 mesh was used as the mercury reaction agent. After spraying the mixed powder, 0 to 2-3 seconds later, the mixed powder was blown in, and 100 kg / h of slaked lime powder was blown in the wake, and mercury and HCl were blown.
(Acid gas) was removed. Results: As a result of the above test, mercury in the exhaust gas could be removed at a maximum of 76% and HCl at 98.6%.

〔発明の効果〕〔The invention's effect〕

・本発明によつて、燃焼排ガス中の水銀と酸性ガスを乾
式で且つ同時に処理することができる。
-According to the present invention, mercury and acid gas in combustion exhaust gas can be treated dry and simultaneously.

・集じんと反応促進を兼ねたバグフイルターを用いるこ
とによつて、高い除去率を達成できる。
-A high removal rate can be achieved by using a bag filter that also collects dust and accelerates the reaction.

・水銀反応剤と反応助剤を混合噴射することによつて、
設備の簡素化と、水銀反応剤の排ガス中への噴射時の分
散性を高めることができる。
・ By mixing and injecting the mercury reactant and the reaction aid,
It is possible to simplify the equipment and improve the dispersibility when the mercury reactant is injected into the exhaust gas.

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

第1図は、本発明の一実施態様を説明するための図であ
り、第2図は、本発明によるバグフイルター3布の表面
堆積層の概念図を示すものである。
FIG. 1 is a diagram for explaining one embodiment of the present invention, and FIG. 2 is a conceptual diagram of a surface deposition layer of a bag filter 3 cloth according to the present invention.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 洞口 光弘 神奈川県横浜市中区錦町12番地 三菱重工 業株式会社横浜製作所内 (72)発明者 殿村 丈二 神奈川県横浜市中区錦町12番地 三菱重工 業株式会社横浜製作所内 (56)参考文献 特開 昭62−186925(JP,A) ─────────────────────────────────────────────────── --- Continuation of the front page (72) Inventor Mitsuhiro Doroguchi 12 Nishiki-cho, Naka-ku, Yokohama-shi, Kanagawa Mitsubishi Heavy Industries, Ltd.Yokohama Works (72) Inventor Jouji Tonomura 12 Nishiki-cho, Naka-ku, Yokohama, Japan Mitsubishi Heavy Industries Yokohama Works Co., Ltd. (56) Reference JP-A-62-186925 (JP, A)

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】燃焼排ガスの煙道中に、反応助剤と水銀反
応剤の混合粉末を噴射して排ガス中の水銀を粉体側へ固
定するとともに、酸性ガス中和剤粉末を噴射して排ガス
中の酸性ガスを除去し、噴射後方にバグフイルターを設
けて排ガス中より燃焼ばいじんと一緒に系外へ排出する
ことを特徴とする燃焼排ガス中の水銀及び酸性ガス除去
方法。
1. A mixed powder of a reaction aid and a mercury reactant is injected into a flue of a combustion exhaust gas to fix mercury in the exhaust gas to the powder side, and an acidic gas neutralizer powder is injected to the exhaust gas. A method for removing mercury and acid gas in combustion exhaust gas, characterized in that the acid gas therein is removed, and a bag filter is provided behind the injection to discharge the gas together with the combustion dust from the exhaust gas to the outside of the system.
JP61059426A 1986-03-19 1986-03-19 Method for removing mercury and acid gas in combustion exhaust gas Expired - Lifetime JPH0661424B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61059426A JPH0661424B2 (en) 1986-03-19 1986-03-19 Method for removing mercury and acid gas in combustion exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61059426A JPH0661424B2 (en) 1986-03-19 1986-03-19 Method for removing mercury and acid gas in combustion exhaust gas

Publications (2)

Publication Number Publication Date
JPS62216630A JPS62216630A (en) 1987-09-24
JPH0661424B2 true JPH0661424B2 (en) 1994-08-17

Family

ID=13112923

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61059426A Expired - Lifetime JPH0661424B2 (en) 1986-03-19 1986-03-19 Method for removing mercury and acid gas in combustion exhaust gas

Country Status (1)

Country Link
JP (1) JPH0661424B2 (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5306475A (en) * 1987-05-18 1994-04-26 Ftu Gmbh Technische Entwicklung Und Forschung Im Umweltschutz Reactive calcium hydroxides
JPH04330917A (en) * 1991-05-01 1992-11-18 Kubota Corp Dust collecting method of waste gas
CA2114331C (en) * 1993-06-10 2000-03-28 Bernard J. Lerner Removal of mercury and cadmium and their compounds from incinerator flue gases
DE19542065C2 (en) * 1995-11-13 1997-10-23 Steag Ag Method and device for cleaning combustion gases from combustion plants
DE19824237B4 (en) * 1998-05-29 2004-12-30 Walhalla-Kalk Entwicklungs- Und Vertriebsgesellschaft Mbh Exhaust gas cleaning reagents, their manufacture and their use
US8420561B2 (en) * 2009-06-16 2013-04-16 Amcol International Corporation Flue gas scrubbing

Also Published As

Publication number Publication date
JPS62216630A (en) 1987-09-24

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