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JPH07313839A - Moving bed for treating exhaust gas - Google Patents

Moving bed for treating exhaust gas

Info

Publication number
JPH07313839A
JPH07313839A JP6271858A JP27185894A JPH07313839A JP H07313839 A JPH07313839 A JP H07313839A JP 6271858 A JP6271858 A JP 6271858A JP 27185894 A JP27185894 A JP 27185894A JP H07313839 A JPH07313839 A JP H07313839A
Authority
JP
Japan
Prior art keywords
exhaust gas
moving bed
dust
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.)
Withdrawn
Application number
JP6271858A
Other languages
Japanese (ja)
Inventor
Yasuyuki Sensui
康幸 泉水
Hisatsugu Kitaguchi
久継 北口
Osamu Yamauchi
修 山内
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.)
Nippon Steel Corp
Original Assignee
Nippon Steel Corp
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 Nippon Steel Corp filed Critical Nippon Steel Corp
Priority to JP6271858A priority Critical patent/JPH07313839A/en
Publication of JPH07313839A publication Critical patent/JPH07313839A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

  • Treating Waste Gases (AREA)

Abstract

PURPOSE:To provide a device optimum for dust removal, desulfurization, denitrification and chlorine compound removal of exhaust gas contg. smoke dust, gaseous SO2, nitrogen oxides and chlorine compounds. CONSTITUTION:A carbon agent 2 of <=5mm average particle diameter is deposited on sintered ore 1 of 1mm-10mm diameter. Then, a moving bed 6 is packed with the deposited material. The spacific surface area of the carbon agent 2 measure by the BET method is preferably >=20m<2>/g.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、大量に排ガスを排出す
る産業分野、例えば焼結炉、ゴミ焼却炉、ボイラー等か
ら排出される大量の排ガスを脱硫、脱硝し、塩素化合物
を除去する排ガス処理用移動層に関する。
FIELD OF THE INVENTION The present invention relates to an industrial field in which a large amount of exhaust gas is discharged, for example, an exhaust gas for desulfurizing and denitrifying a large amount of exhaust gas discharged from a sintering furnace, a refuse incinerator, a boiler, etc. to remove chlorine compounds. It relates to a moving bed for processing.

【0002】[0002]

【従来の技術】例えば焼結炉、ゴミ焼却炉、ボイラーか
ら発生する排ガスには高い濃度の亜硫酸ガス(SO
2 )、窒素酸化物、微量の塩素化合物が含まれているの
で、大気汚染防止のため脱硫、脱硝、塩素化合物の除去
が必要である。
2. Description of the Related Art For example, exhaust gas generated from a sintering furnace, a refuse incinerator, or a boiler has a high concentration of sulfurous acid gas (SO
2 ), Nitrogen oxides and trace amounts of chlorine compounds are contained, so desulfurization, denitration and removal of chlorine compounds are necessary to prevent air pollution.

【0003】脱硫に関しては、石灰石膏法、水酸化マグ
ネシウム法、活性コークスへの吸着法が知られている。
脱硝に関しては、例えば5酸化バナジウム、活性コーク
スなどの触媒の存在下でのアンモニアによる選択還元脱
硝が知られている。塩素化合物除去に関しては、例え
ば、「機械工学便覧」、エンジニアリング編、C8環境
装置に記載されているように、600℃以上に加熱して
分解する方法、5酸化バナジウム触媒で酸化分解する方
法、活性コークスに吸着させ除去する方法が知られてい
る。
Regarding desulfurization, a lime gypsum method, a magnesium hydroxide method, and an adsorption method on activated coke are known.
Regarding denitration, for example, selective reduction denitration with ammonia in the presence of a catalyst such as vanadium pentoxide or activated coke is known. Regarding the removal of chlorine compounds, for example, as described in “Mechanical Engineering Handbook”, Engineering Edition, C8 environmental equipment, a method of decomposing by heating to 600 ° C. or higher, a method of oxidative decomposition with a vanadium oxide 5 catalyst, an activity A method of adsorbing and removing coke is known.

【0004】これらの反応を行わせるために、例えば、
「排煙脱硫技術に関する調査研究」、社団法人日本産業
機械工業会に記載されているように、例えば水酸化マグ
ネシウムのような水溶液物質の場合は、スクラバーや液
を充填した容器中にガスを吹き込むバブリング法が、5
酸化バナジウム触媒を用いた脱硝あるいは塩素化合物除
去には固定層が、5mm以上に成型した活性コークスや
ゼオライトの場合は移動層あるいは固定層が、褐炭を軽
度に乾留して製造されるリグナイトコークスや消石灰な
ど粉状物質を用いる場合には乾式スクラバーあるいは循
環流動層が用いられている。
In order to carry out these reactions, for example,
As described in "Research on flue gas desulfurization technology", Japan Industrial Machinery Manufacturers Association, in the case of aqueous substances such as magnesium hydroxide, gas is blown into a container filled with a scrubber or liquid. The bubbling method is 5
For denitration using a vanadium oxide catalyst or removal of chlorine compounds, the fixed bed is a fixed bed, and in the case of activated coke or zeolite molded to a size of 5 mm or more, the moving bed or fixed bed is a lignite coke produced by lightly distilling brown coal. When using powdered substances such as slaked lime, dry scrubbers or circulating fluidized beds are used.

【0005】また、例えば、「機械工学便覧」、エンジ
ニアリング編、C8環境装置に記載されているように、
脱硝作用をもつ酸化金属系触媒をTiO2 等でできた担
体に担持させ、固定層として排ガス処理を行う方法も知
られている。
Further, for example, as described in "Mechanical Engineering Handbook", Engineering Edition, C8 Environmental Equipment,
There is also known a method in which a metal oxide catalyst having a denitration action is supported on a carrier made of TiO 2 or the like, and exhaust gas treatment is carried out as a fixed bed.

【0006】[0006]

【発明が解決しようとする課題】しかし、例えば水酸化
マグネシウム溶液のような液状の反応剤を用いる場合は
反応生成物質処理のための水処理設備が必要で、かつ水
処理設備を円滑に運転するために処理ガス中の煤塵濃度
を約100mg/Nm3 以下にする必要があり、水処理
設備の前段に除塵設備を設置することが不可欠であるの
で、設備費用が高価である。
However, when a liquid reactant such as a magnesium hydroxide solution is used, a water treatment facility for treating the reaction product is required and the water treatment facility can be operated smoothly. Therefore, the dust concentration in the treated gas needs to be about 100 mg / Nm 3 or less, and it is indispensable to install the dust removing equipment in the preceding stage of the water treatment equipment, so the equipment cost is high.

【0007】5酸化バナジウム触媒を用いた脱硝あるい
は塩素化合物除去を行う場合は、触媒機能を維持するた
めに前段で例えばアルカリなどの触媒機能を阻害する固
体物質を除去するため除塵する必要があり、前段に高性
能除塵機を設置する必要がある。さらに、例えば窒素酸
化物の還元剤としてアンモニアをガス中に吹き込むと、
触媒上で硫黄酸化物と化学反応し、硫安や酸性硫安を生
成して触媒機能が阻害されるので、硫黄酸化物を除去す
るために、前段に脱硫器を設置する必要もある。これら
に加えて、処理しようとするガスを300℃以上に加熱
する必要があるので、加熱装置の設置も必要である。こ
の結果、設備費用は非常に高価となる。
When denitration using a vanadium pentoxide catalyst or chlorine compound removal is performed, in order to maintain the catalytic function, it is necessary to remove dust in order to remove a solid substance that inhibits the catalytic function, such as alkali, in the preceding stage. It is necessary to install a high-performance dust remover in the previous stage. Further, for example, when ammonia is blown into the gas as a reducing agent for nitrogen oxides,
Since a chemical reaction with sulfur oxides on the catalyst produces ammonium sulfate or acidic ammonium sulfate to impair the catalytic function, it is also necessary to install a desulfurizer at the previous stage in order to remove the sulfur oxides. In addition to these, it is necessary to heat the gas to be treated to 300 ° C. or higher, so it is necessary to install a heating device. As a result, the equipment cost becomes very expensive.

【0008】5mm以上に成型した活性コークスやゼオ
ライトを用いた移動層あるいは固定層でガス処理を行う
方法は、乾式処理なので水処理設備が不要で、かつ、脱
硫、脱硝、塩素化合物の除去を同時に行うことができる
ので、設備的には安価である。しかし、移動層あるいは
固定層中をガスを円滑に通過させるために活性コークス
やゼオライトを5mm以上の粒度に成型する必要があ
り、成型のためのコストが高くなる。
The method of performing gas treatment in a moving bed or fixed bed using activated coke or zeolite molded to a size of 5 mm or more does not require water treatment equipment because it is a dry treatment, and desulfurization, denitration, and removal of chlorine compounds are carried out at the same time. Since it can be performed, it is inexpensive in terms of equipment. However, in order to allow the gas to smoothly pass through the moving bed or the fixed bed, it is necessary to mold active coke or zeolite to a particle size of 5 mm or more, which increases the cost for molding.

【0009】リグナイトコークスの様な安価ではあるが
反応器内のガス流速に適合した粒子径を持つ粉状の反応
剤を循環流動層、ドライスクラバー等の反応器に吹き込
む方法は、反応剤は移動層や固定層に用いる場合に比べ
安価であり、ドライスクラバーや循環流動層はガス中の
有害物質の除去反応を行わせる上で十分な時間を確保で
きる。しかし、例えばリグナイトコークスの様な粉状反
応剤の耐用時間とドライスクラバーや循環流動層のライ
ザー内のリグナイトコークスの滞留を比較すると、これ
らの反応器内の滞留時間は短い。従って、経済的に粉状
反応剤を使用するためには、ドライスクラバーや循環流
動層のライザーから排出される粉状反応剤を集塵機で回
収して再度使用すること、即ち粉状反応剤の循環使用が
不可欠である。しかし、ドライスクラバーや循環流動層
の入口煤塵濃度が高いと粉状反応剤と煤塵が混合してし
まうので、混合による粉状反応剤の希釈を防止するため
には入口ガスの煤塵濃度を50mg/Nm3 以下に除塵
する必要があり、前段に高度除塵器を設置しなければな
らない。また、反応剤回収用の除塵設備を後段にも設置
する必要があり、設備費用は高価になる。
A method such as an inexpensive method such as lignite coke in which a powdery reactant having a particle size adapted to the gas flow rate in the reactor is blown into a reactor such as a circulating fluidized bed or a dry scrubber is It is cheaper than when used for a moving bed or a fixed bed, and a dry scrubber or a circulating fluidized bed can secure a sufficient time for carrying out a reaction for removing harmful substances in a gas. However, when comparing the service life of powdered reactants such as lignite coke with the retention of lignite coke in the dry scrubber or circulating fluidized bed riser, the residence time in these reactors is short. Therefore, in order to use the powdery reactant economically, the powdery reactant discharged from the dry scrubber and the riser of the circulating fluidized bed should be collected by the dust collector and used again, that is, the circulation of the powdery reactant should be performed. Use is essential. However, if the inlet dust concentration of the dry scrubber or circulating fluidized bed is high, the powdery reactant and the dust are mixed, so in order to prevent the powdery reactant from being diluted by the mixing, the dust concentration of the inlet gas is 50 mg / It is necessary to remove dust to Nm 3 or less, and an advanced dust remover must be installed in the preceding stage. In addition, it is necessary to install dust removing equipment for collecting the reactant in the subsequent stage, and the equipment cost becomes high.

【0010】担体に触媒を担持させて固定層で排ガス処
理を行う方法は、触媒機能が劣化するたびに交換する必
要があるので、耐用時間が比較的短い粉状反応剤を用い
る場合は経済的ではない。
The method of supporting the catalyst on the carrier and treating the exhaust gas in the fixed bed needs to be replaced every time the catalyst function deteriorates. Therefore, it is economical when using a powdery reactant having a relatively short service life. is not.

【0011】本発明の目的は、煤塵、亜流酸ガス、窒素
酸化物、及び塩素化合物を含む排ガスの除塵、脱硫、脱
硝、塩素化合物除去に最適な装置を提供することであ
る。
An object of the present invention is to provide an apparatus suitable for dust removal, desulfurization, denitration, and chlorine compound removal of exhaust gas containing soot dust, sulfurous acid gas, nitrogen oxides, and chlorine compounds.

【0012】[0012]

【課題を解決するための手段】本発明の要旨は、大気放
散排ガスを浄化する物質を充填した排ガス処理用移動層
において、平均粒子径5mm以下の炭剤を直径1mm以
上10mm以下の焼結鉱に担持させ、充填したことを特
徴とする排ガス処理用移動層である。前記炭剤のBET
法で測定した比表面積は20m2 /g以上であることが
好ましい。
Means for Solving the Problems The gist of the present invention is to provide a moving bed for treating exhaust gas, which is filled with a substance for purifying exhaust gas emitted into the atmosphere, by adding a carbonizing agent having an average particle diameter of 5 mm or less to a sintered ore having a diameter of 1 mm or more and 10 mm or less. It is a moving bed for treating exhaust gas, characterized in that it is carried on and filled with. BET of the charcoal agent
The specific surface area measured by the method is preferably 20 m 2 / g or more.

【0013】[0013]

【作用】例えば、亜硫酸ガス濃度150〜200ppm
で塩素化合物を微量含む排ガスを、ガス中の亜硫酸ガ
ス、塩素化合物を吸着する機能を有する細孔半径が1〜
10nmの細孔で比表面積が約100m2 /gの活性炭
剤で処理した場合、80%以上脱硫するためにはガスと
の接触時間即ち反応時間は0.5〜1.0秒必要であ
り、活性炭剤の脱硫能力が80%以下に低下するまでの
耐用時間は約20時間である。また、塩素化合物を80
%以上除去するためには反応時間は0.5〜1.0秒必
要であり、活性炭剤の塩素化合物除去能力が80%以下
に低下するまでの耐用時間は約120時間である。
[Function] For example, a sulfurous acid gas concentration of 150 to 200 ppm
The exhaust gas containing a small amount of chlorine compounds has a pore radius of 1 to 1 that has a function of adsorbing sulfur dioxide gas and chlorine compounds in the gas.
When treated with an activated carbon agent having a pore size of 10 nm and a specific surface area of about 100 m 2 / g, a contact time with a gas, that is, a reaction time is required to be 0.5 to 1.0 seconds in order to desulfurize by 80% or more, The service life until the desulfurization ability of the activated carbon agent decreases to 80% or less is about 20 hours. In addition, the chlorine compound is 80
% Or more, the reaction time is required to be 0.5 to 1.0 seconds, and the service life until the chlorine compound removing ability of the activated carbon agent decreases to 80% or less is about 120 hours.

【0014】排ガスの脱硫、脱硝、塩素化合物除去機能
を有する活性炭剤を、粒子径が大きい焼結鉱に担持させ
て充填した移動層は有害物質を除去し、かつ活性炭剤の
排ガス処理能力を十分に使い切ることができる。また、
高価な成型した活性炭剤を使用する必要が無いので、安
価な粉状の活性炭剤を使用することが可能である。加え
て、移動層が除塵能力を有するので前段、後段に除塵設
備を設置する必要がなく、設備費用が安価である。
A moving bed filled with an activated carbon agent having the functions of desulfurization, denitration and chlorine compound removal of exhaust gas by supporting it on a sintered ore having a large particle size removes harmful substances and has a sufficient exhaust gas treatment ability of the activated carbon agent. It can be used up. Also,
Since it is not necessary to use an expensive molded activated carbon agent, it is possible to use an inexpensive powdered activated carbon agent. In addition, since the moving bed has a dust removing capability, there is no need to install dust removing equipment at the front and rear stages, and the equipment cost is low.

【0015】平均粒子径が5mmを越える活性炭剤も移
動層用の充填物として使用できるが、平均粒子径が5m
mを越えるためには成型が必要で、製造コストが高くな
る。従って、平均粒子径が5mm以下の炭剤を使用す
る。
Activated carbon agents having an average particle size of more than 5 mm can be used as the packing for the moving bed, but the average particle size is 5 m.
In order to exceed m, molding is required, resulting in high manufacturing cost. Therefore, a carbonizing agent having an average particle diameter of 5 mm or less is used.

【0016】直径1mm以上10mm以下の焼結鉱に炭
剤を担持させる理由は、特願平4−337798号明細
書に記載されている様に、1〜10mmの焼結鉱は除塵
率が98%以上の高度の除塵能力を有し、多孔質で粉体
を付着させ担持する能力に優れているのに加え、排ガス
処理後に焼結原料として使用することが可能であるため
である。有害物質の除去機能物質を炭剤とした理由は、
炭剤は排ガス処理で機能を失った後に燃料として使用可
能なためである。
The reason why the carbonizing agent is supported on the sinter having a diameter of 1 mm or more and 10 mm or less is that, as described in Japanese Patent Application No. 4-337798, the sinter having a diameter of 1 to 10 mm has a dust removal rate of 98. This is because, in addition to having a high degree of dust removal capability of not less than%, being excellent in the ability to adhere and carry powders in a porous manner, it can be used as a sintering raw material after exhaust gas treatment. The reason for using the charcoal agent as a substance that removes harmful substances is
This is because the carbonizing agent can be used as a fuel after losing its function in exhaust gas treatment.

【0017】炭剤のBET法で測定した比表面積が20
2 /g以上であると好ましい理由は、硫黄酸化物、窒
素酸化物、塩素化合物の炭剤表面への吸着能力を確保す
るためである。
The specific surface area of the carbonizing agent measured by the BET method is 20.
The reason why it is preferably m 2 / g or more is to ensure the adsorption ability of sulfur oxides, nitrogen oxides, and chlorine compounds on the surface of the carbonizing agent.

【0018】なお、本発明では有害物質除去機能を有す
る物質として炭剤を採用したが、例えば、ゼオライト、
消石灰、酸化金属触媒などの有害物質除去機能物質を焼
結鉱に担持させることもできる。
In the present invention, a carbonizing agent is adopted as the substance having a harmful substance removing function.
It is also possible to support a substance having a function of removing harmful substances such as slaked lime and a metal oxide catalyst on the sinter.

【0019】[0019]

【実施例】本発明の実施例を図1及び図2を用いて説明
する。
Embodiments of the present invention will be described with reference to FIGS.

【0020】排ガスの脱硫及び塩素化合物除去を目的と
して、図1に示すように、直径3mm以上5mm以下に
粒度調整した焼結鉱1に、細孔半径が1〜10nmの細
孔を有し、比表面積が約100m2 /gで平均粒径0.
5mmの活性炭の炭剤2の粉を20kg/tの割合で予
め混合し、担持させて充填した十字流型の移動層6で、
空間速度約5000h-1の条件で亜硫酸ガス濃度150
〜200ppmで塩素化合物を微量含む焼結炉の排ガス
5と接触させた。予め除塵しない場合は、入口排ガス5
の煤塵濃度は400〜800mg/Nm3 で変化してい
た。この場合、移動層6は排ガス5を除塵する機能をも
有するため、移動層6内に煤塵が堆積するので、目詰り
を発生させず円滑に運転するためには充填物の滞留時間
を約10時間以下とする必要がある。そこで、充填物の
滞留時間を煤塵による目詰りを発生させない限界の滞留
時間及び活性炭剤の耐用時間のうち小さい方の時間であ
る8時間として運転した結果、移動層6の排ガス清浄化
能力として脱硫率85%、塩素化合物除去率99%、除
塵率97%が得られた。
For the purpose of desulfurization of exhaust gas and removal of chlorine compounds, as shown in FIG. 1, a sintered ore 1 having a grain size adjusted to a diameter of 3 mm or more and 5 mm or less has pores having a pore radius of 1 to 10 nm, A specific surface area of about 100 m 2 / g and an average particle size of 0.
In the cross flow type moving bed 6 in which the powder of the charcoal agent 2 of 5 mm of activated carbon was premixed at a rate of 20 kg / t, and supported and filled,
Sulfurous acid gas concentration of 150 under the condition of space velocity of about 5000 h -1
It was brought into contact with the exhaust gas 5 of a sintering furnace containing a trace amount of chlorine compounds at ˜200 ppm. Inlet exhaust gas 5 if dust is not removed in advance
The soot and dust concentration of No. 3 varied from 400 to 800 mg / Nm 3 . In this case, since the moving bed 6 also has a function of removing the exhaust gas 5, soot is accumulated in the moving bed 6, so that the retention time of the packing is about 10 in order to smoothly operate without causing clogging. Must be less than or equal to time. Therefore, as a result of operating as the residence time of the packing, which is the shorter of the limit retention time that does not cause clogging due to soot dust and the service life of the activated carbon agent, which is the shorter time, desulfurization is performed as the exhaust gas cleaning capacity of the moving bed 6. A rate of 85%, a chlorine compound removal rate of 99%, and a dust removal rate of 97% were obtained.

【0021】次に、塩素化合物除去のみを目的として、
図2に示すように、2層構造にした十字流型の移動層6
を用いた。第1移動層8は直径3mm以上5mm以下に
粒度調整した焼結鉱を充填物とし、空間速度約7000
-1、滞留時間10時間の移動層である。除塵率は約9
7%で、出口の含塵濃度は35mg/Nm3 未満であ
る。第2移動層9は、平均粒径0.5mmの活性炭の炭
剤2の粉を直径3mm以上5mm以下に粒度調整した焼
結鉱1に20kg/tの割合で予め混合して担持させて
充填した移動層で、空間速度は約7000h-1である。
2層構造の移動層とした理由は、第1移動層8で予め除
塵すると第2移動層9は煤塵による目詰りを防止できる
ので、滞留時間を活性炭の炭剤2の耐用時間に近い約1
00時間として運転できるためである。試験の結果は、
除塵率99%、塩素化合物除去率85%であった。
Next, for the purpose of removing chlorine compounds only,
As shown in FIG. 2, a cross flow type moving layer 6 having a two-layer structure.
Was used. The first moving bed 8 is made of a sintered ore whose particle size is adjusted to have a diameter of 3 mm or more and 5 mm or less, and has a space velocity of about 7,000.
It is a moving bed with h −1 and a residence time of 10 hours. Dust removal rate is about 9
At 7%, the dust concentration at the outlet is less than 35 mg / Nm 3 . The second moving bed 9 is preliminarily mixed and loaded with a powder of activated carbonaceous agent 2 having an average particle diameter of 0.5 mm in a proportion of 20 kg / t in a sintered ore 1 having a diameter adjusted to 3 mm or more and 5 mm or less. In the moving bed, the space velocity is about 7000 h -1 .
The reason why the moving layer has a two-layer structure is that if the first moving layer 8 is preliminarily dedusted, the second moving layer 9 can prevent clogging due to soot and dust, so that the residence time is about 1 which is close to the service life of the carbonaceous agent 2 of activated carbon.
This is because it can be operated as 00 hours. The test results are
The dust removal rate was 99% and the chlorine compound removal rate was 85%.

【0022】炭剤を担持させる方法として予め焼結鉱と
混合する例を説明したが、例えば、移動層がガスに含ま
れる粉体を除去、保持する機能を利用し、移動層の前段
で排ガス中に粉状の炭剤を吹き込んでもよい。
As an example of the method of supporting the carbonizing agent, the method of mixing with the sintered ore in advance has been explained. For example, the moving bed utilizes the function of removing and holding the powder contained in the gas, and the exhaust gas is provided in the preceding stage of the moving bed. A powdery carbonaceous agent may be blown therein.

【0023】[0023]

【発明の効果】本発明によれば、安価な設備で煤塵及び
有害物質を含む排ガスからの煤塵、有害物質の高度除去
が可能となる。
According to the present invention, it is possible to highly remove soot and harmful substances from exhaust gas containing soot and harmful substances with inexpensive equipment.

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

【図1】本発明の排ガス処理用移動層の実施例を示す図
である。
FIG. 1 is a diagram showing an example of a moving layer for treating exhaust gas of the present invention.

【図2】本発明の排ガス処理用移動層の実施例を示す図
である。
FIG. 2 is a diagram showing an example of a moving layer for treating exhaust gas of the present invention.

【符号の説明】[Explanation of symbols]

1 焼結鉱 2 炭剤 3 混合機 4 搬送経路 5 排ガス 6 移動層 7 清浄排ガス 8 第1移動層 9 第2移動層 10 搬送経路 DESCRIPTION OF SYMBOLS 1 Sintered ore 2 Charcoal agent 3 Mixer 4 Transport path 5 Exhaust gas 6 Moving bed 7 Clean exhaust gas 8 1st moving bed 9 2nd moving bed 10 Transfer path

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01D 53/68 B01D 53/34 134 A ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location B01D 53/68 B01D 53/34 134 A

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 大気放散排ガスを浄化する物質を充填し
た排ガス処理用移動層において、平均粒子径5mm以下
の炭剤を直径1mm以上10mm以下の焼結鉱に担持さ
せ、充填したことを特徴とする排ガス処理用移動層。
1. A moving bed for treating exhaust gas, which is filled with a substance for purifying exhaust gas emitted into the atmosphere, characterized in that a carbonizing agent having an average particle diameter of 5 mm or less is carried and filled in a sinter having a diameter of 1 mm to 10 mm. A moving bed for exhaust gas treatment.
【請求項2】 前記炭剤のBET法で測定した比表面積
が20m2 /g以上であることを特徴とする請求項1記
載の排ガス処理用移動層。
2. The moving bed for treating exhaust gas according to claim 1, wherein the carbonaceous agent has a specific surface area of 20 m 2 / g or more as measured by the BET method.
JP6271858A 1994-04-01 1994-10-12 Moving bed for treating exhaust gas Withdrawn JPH07313839A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6271858A JPH07313839A (en) 1994-04-01 1994-10-12 Moving bed for treating exhaust gas

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP8532094 1994-04-01
JP6-85320 1994-04-01
JP6271858A JPH07313839A (en) 1994-04-01 1994-10-12 Moving bed for treating exhaust gas

Publications (1)

Publication Number Publication Date
JPH07313839A true JPH07313839A (en) 1995-12-05

Family

ID=26426339

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6271858A Withdrawn JPH07313839A (en) 1994-04-01 1994-10-12 Moving bed for treating exhaust gas

Country Status (1)

Country Link
JP (1) JPH07313839A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108922645A (en) * 2018-08-23 2018-11-30 中国原子能科学研究院 The adjusting preparation facilities of 2AF feed liquid in nuclear fuel aftertreatment technology process
CN111715070A (en) * 2020-05-25 2020-09-29 北京中航泰达环保科技股份有限公司 Ultra-clean discharge system and method for desulfurization and denitrification treatment of boiler flue gas
JP2020186416A (en) * 2019-05-09 2020-11-19 日本製鉄株式会社 Sintered soot dust management method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108922645A (en) * 2018-08-23 2018-11-30 中国原子能科学研究院 The adjusting preparation facilities of 2AF feed liquid in nuclear fuel aftertreatment technology process
JP2020186416A (en) * 2019-05-09 2020-11-19 日本製鉄株式会社 Sintered soot dust management method
CN111715070A (en) * 2020-05-25 2020-09-29 北京中航泰达环保科技股份有限公司 Ultra-clean discharge system and method for desulfurization and denitrification treatment of boiler flue gas

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