Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPS6316170B2 - - Google Patents
[go: Go Back, main page]

JPS6316170B2 - - Google Patents

Info

Publication number
JPS6316170B2
JPS6316170B2 JP57173952A JP17395282A JPS6316170B2 JP S6316170 B2 JPS6316170 B2 JP S6316170B2 JP 57173952 A JP57173952 A JP 57173952A JP 17395282 A JP17395282 A JP 17395282A JP S6316170 B2 JPS6316170 B2 JP S6316170B2
Authority
JP
Japan
Prior art keywords
catalyst
liquid
gas
washing
water
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
Application number
JP57173952A
Other languages
Japanese (ja)
Other versions
JPS5966352A (en
Inventor
Michasu Honda
Masao Hino
Tooru Seto
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 JP17395282A priority Critical patent/JPS5966352A/en
Publication of JPS5966352A publication Critical patent/JPS5966352A/en
Publication of JPS6316170B2 publication Critical patent/JPS6316170B2/ja
Granted legal-status Critical Current

Links

Landscapes

  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Description

【発明の詳細な説明】 本発明はガス処理装置などの横置型反応装置内
に充填された並行流式触媒が使用途中にダストの
付着堆積あるいは被毒成分の蓄積により性能低下
した時に、該触媒を充填したまゝで触媒の性能を
回復させる改良された賦活方法を提供せんとする
ものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention provides a solution for reducing the performance of a parallel flow catalyst packed in a horizontal reactor such as a gas treatment equipment due to dust adhesion or accumulation of poisonous components during use. The purpose of the present invention is to provide an improved activation method for restoring the performance of a catalyst while still being filled with the catalyst.

カリウム、ナトリウム、カルシウムなどのアル
カリまたはアルカリ土類金属は、脱硝触媒、燃焼
触媒など燃焼排ガスを対象にした触媒反応におい
て触媒活性を阻害する被毒物質のため、できるだ
けその含有量を低減させる必要がある。しかしな
がら最近では燃料事情の悪化から、ますますダス
ト量、ダスト組成の点で触媒に悪影響を与えるよ
うな排ガス源になつてきており、そこで使用され
る触媒に耐ダスト被毒性を要求されると共に、被
毒された触媒についての効果的な賦活方法が要求
される状況にある。
Alkali or alkaline earth metals such as potassium, sodium, and calcium are poisonous substances that inhibit catalytic activity in catalytic reactions targeting combustion exhaust gas, such as denitration catalysts and combustion catalysts, so it is necessary to reduce their content as much as possible. be. However, in recent years, due to worsening fuel conditions, dust has increasingly become a source of exhaust gas that has a negative impact on catalysts in terms of dust amount and dust composition, and the catalysts used there are required to be resistant to dust toxicity. There is a need for an effective activation method for poisoned catalysts.

本発明者らは既に触媒の賦活方法として数多く
の提案をしてきた。例えば水洗法(特願昭56〜
128831号)、粗粒アツシユによる触媒表面を強
制的に摩耗させる方法(特願昭57〜32988号)及
び粗粒粉体を多く含むスラリーを高圧ガス体下
で触媒表面に噴射し、仕上げ水洗を行う方法(特
願昭57〜61710号)などである。
The present inventors have already proposed numerous methods for activating catalysts. For example, the water washing method (patent application from 1984)
128831), a method of forcibly abrading the catalyst surface using coarse particle assemblies (Japanese Patent Application No. 57-32988), and a method in which a slurry containing a large amount of coarse particles is injected onto the catalyst surface under a high-pressure gas body, and a final washing with water is performed. (Patent Application No. 57-61710).

しかしながら、上述した提案方法は主として触
媒を竪置に配設した竪置型反応器に対するもので
あり、触媒を横置に配設した横置型反応器につい
て具体的には開示されていない。又、横置型反応
器に充填された触媒を浸漬水洗処理する程度で
は、液の流動がないため、触媒のガス通過孔内部
の被毒成分の溶出速度が遅く、さらに触媒が横置
きになつているために水洗液の液切りが完全にで
きない。
However, the above-mentioned proposed method is mainly for a vertical reactor in which a catalyst is arranged vertically, and there is no specific disclosure regarding a horizontal reactor in which a catalyst is arranged horizontally. In addition, when the catalyst packed in a horizontal reactor is immersed in water, there is no liquid flow, so the rate of elution of poisonous components inside the gas passage holes of the catalyst is slow, and the catalyst is placed horizontally. The washing liquid cannot be drained completely due to the presence of water.

そのために横置型反応器に傾斜をもたせる方法
あるいは圧力下におけるスプレー水洗法などが考
えられるが、前者は装置が複雑になるなどの欠点
があり、後者はそれなりに上述した提案方法に示
したように効果があるが、特に横置型反応器の場
合、竪置型反応器に比し水洗水量及び賦活時間が
大きくなり過ぎる欠点があつた。
Possible methods for this purpose include a method of tilting the horizontal reactor or a spray washing method under pressure, but the former has disadvantages such as the complexity of the equipment, while the latter has some disadvantages as shown in the proposed method above. Although it is effective, especially in the case of a horizontal reactor, there is a drawback that the amount of water for washing and the activation time are too large compared to a vertical reactor.

そこで本発明者らは、横置型反応器における触
媒賦活に際して使用する水洗水量及び賦活時間を
大幅に減少せしめうる方法につき鋭意研究の結
果、本発明を完成するに到つた。
Therefore, the present inventors have completed the present invention as a result of extensive research into a method that can significantly reduce the amount of washing water and activation time used during catalyst activation in a horizontal reactor.

すなわち本発明は、並行流式触媒を充填した横
置型反応装置内の該触媒が性能低下した場合、該
触媒を該反応装置内に充填した状態で高圧気液混
相流を該触媒表面上に噴射させる触媒の賦活方法
である。
That is, the present invention provides a method for injecting a high-pressure gas-liquid multiphase flow onto the surface of the catalyst while the catalyst is packed in the reactor when the performance of the catalyst in a horizontal reactor filled with a parallel flow catalyst decreases. This is a method for activating a catalyst.

本発明における並行流式触媒とは、ガスと触媒
との接触が並行に行われる通常のものをいい、一
般にはハニカム触媒と板状触媒とがある。
The parallel flow type catalyst in the present invention refers to a conventional catalyst in which gas and catalyst are brought into contact in parallel, and generally includes a honeycomb catalyst and a plate-shaped catalyst.

本発明方法は、この並行流式触媒を横置したい
わゆる横置型反応装置の触媒賦活に適用した場合
に、特に顕著な効果がある。また性能低下した並
行流式触媒(以下、触媒)表面に噴射される高圧
気液混相流としては、空気と水、空気と鉱酸
(H2SO4、HCl)を含む洗浄液、空気とドレンを
多量に含む湿り蒸気及び炭酸ガス、その他のガス
と洗浄液などの洗浄媒体などの組合せが使用しう
る。以上の気液混相流の気体としては乾燥水蒸気
も使用しうる。本発明における気:液の比率は、
液1に対し気1〜20、気液混相流の圧力は、
2〜10Kg/cm2Gが適当である。
The method of the present invention is particularly effective when applied to catalyst activation in a so-called horizontal reactor in which the parallel flow catalyst is installed horizontally. In addition, the high-pressure gas-liquid multiphase flow injected onto the surface of a parallel flow catalyst (hereinafter referred to as catalyst) with degraded performance includes air and water, a cleaning solution containing air and mineral acid (H 2 SO 4 , HCl), and air and drain. Combinations such as large quantities of wet steam and carbon dioxide, other gases and cleaning media such as cleaning liquids can be used. Dry steam can also be used as the gas for the above gas-liquid multiphase flow. The gas:liquid ratio in the present invention is
The pressure of the gas-liquid multiphase flow is 1 to 20 gas to 1 liquid.
2 to 10 Kg/cm 2 G is appropriate.

本発明の高圧気液混相流は、触媒のガス通過孔
部の入口側、または出口側のいずれよりも噴射さ
せることができる。
The high-pressure gas-liquid multiphase flow of the present invention can be injected from either the inlet side or the outlet side of the gas passage hole portion of the catalyst.

本発明は石炭や石油を燃焼させた排ガスを触媒
に通過させ排ガス中の窒素酸化物を還元して無害
化除去する脱硝反応などに適用される触媒が、燃
焼排ガス中に含まれるカリウム、ナトリウム、カ
ルシウムなどのアルカリまたはアルカリ土類金属
及びアツシユの蓄積あるいは触媒細孔部の目詰り
などにより性能が低下した場合に、該触媒を再賦
活化するのに特に有効である。
The present invention provides a catalyst that is applied to a denitrification reaction in which exhaust gas from burning coal or oil is passed through a catalyst to reduce and detoxify nitrogen oxides in the exhaust gas. It is particularly effective for reactivating a catalyst when its performance has deteriorated due to accumulation of alkali or alkaline earth metals such as calcium and ash, or clogging of catalyst pores.

以下、本発明を添付図を参照しながら更に詳し
く説明する。
Hereinafter, the present invention will be explained in more detail with reference to the accompanying drawings.

第1図は、従来のスプレー水洗法に基づき触媒
が排ガス流に対し竪配置の場合と横配置の場合に
おける被毒物質の溶出率と水洗時間の関係を示す
グラフである。第1図の試験条件は水洗水量とし
て触媒1m2当り300/min、スプレーノズルは均
等扇形ノズル、水洗圧力は2Kg/cm2・Gで実施した
結果であり、図中aが触媒を竪配置、bが横配置
にした場合の結果である。
FIG. 1 is a graph showing the relationship between the elution rate of poisonous substances and the washing time when the catalyst is arranged vertically and horizontally with respect to the exhaust gas flow based on the conventional spray washing method. The test conditions in Figure 1 are as follows: The amount of washing water was 300/min per m2 of catalyst, the spray nozzle was a uniform fan-shaped nozzle, and the washing pressure was 2Kg/ cm2・G. b is the result when placed horizontally.

竪配置の場合、被毒物質の溶出が平衡に達する
迄の時間が約50分、その時の水洗水量が約15m3
あるのに対し、横配置の場合は平衡時間として約
180分、その時の水洗水量は約54m3も必要とした。
この結果、スプレー水洗法では明らかに触媒が竪
配置の場合の方が効果がよいことがわかる。この
差は横置の場合、触媒ガス通過孔部端面に衝突し
た水洗水の一部が既にその箇所で反応器下部に落
下してしまうためによるもので、竪置の場合は上
部より噴射した水洗水の大半が触媒ガス通過孔内
部を通過し水洗水のロスが少ないことによる洗浄
効果の効率の差である。
In the case of a vertical arrangement, it takes approximately 50 minutes for the elution of the poisonous substance to reach equilibrium, and the amount of water used for washing at that time is approximately 15 m3 , whereas in the case of a horizontal arrangement, the equilibrium time is approximately 50 minutes.
It took 180 minutes, and the amount of water needed for washing was approximately 54m3 .
The results clearly show that the spray washing method is more effective when the catalyst is arranged vertically. This difference is due to the fact that in the case of horizontal installation, some of the washing water that collides with the end face of the catalyst gas passage hole has already fallen to the bottom of the reactor at that point, whereas in the case of vertical installation, the washing water is sprayed from the top. The difference in cleaning efficiency is due to the fact that most of the water passes through the catalyst gas passage hole and there is little loss of washing water.

触媒が横置での水洗処理を行う場合には前述し
たロス分を補う必要がある。そこで従来法の噴射
圧力よりも若干高い圧力下で噴射すること及び水
洗水量を減少させ且つ被毒物質の溶出率も従来の
触媒が竪置の場合の水洗時と同程度に保持できな
いかについて検討を重ねた結果、高圧の気液混相
流を噴射すれば効果があるであろうと考え実験の
結果、下記の実験結果を得本発明の効果を確認し
た。
When the catalyst is washed with water in a horizontal position, it is necessary to compensate for the loss described above. Therefore, we investigated whether it would be possible to inject at a slightly higher pressure than the injection pressure of the conventional method, reduce the amount of water used for washing, and maintain the elution rate of poisonous substances at the same level as when washing with water when the conventional catalyst is placed vertically. As a result of repeated experiments, we thought that injecting a high-pressure gas-liquid multiphase flow would be effective, and as a result of experiments, we obtained the following experimental results and confirmed the effects of the present invention.

第2図はその実験における被毒物質の溶出率と
水洗時間の関係を示すグラフである。実験条件は
触媒1m2当り、水洗水量100/min、空気約1.3
m3/minの気液混相流を5Kg/cm2Gの圧力で均等扇
形ノズルを噴射する条件で行つた。その結果、被
毒物質の溶出率が平衡に達するまでの時間は第2
図に示すように約1時間でその時の水洗水量は6
m3で使用空気量は約80m3であつた。
FIG. 2 is a graph showing the relationship between the elution rate of poisonous substances and the washing time in the experiment. The experimental conditions were: 1 m 2 of catalyst, 100/min of washing water, and approximately 1.3 ml of air.
A gas-liquid multiphase flow of m 3 /min was applied at a pressure of 5 Kg/cm 2 G using a uniform fan-shaped nozzle. As a result, the time it takes for the elution rate of the poisonous substance to reach equilibrium is the second
As shown in the figure, the amount of water used for washing was 6 in about 1 hour.
The amount of air used was approximately 80m3 .

この結果、本発明方法によれば触媒が横置され
ている横置型反応器内に充填されている触媒も、
竪置型反応器に充填された触媒の賦活と同程度の
水洗水量及び時間で賦活しうることが確認され
た。
As a result, according to the method of the present invention, the catalyst packed in the horizontal reactor in which the catalyst is placed horizontally also
It was confirmed that the catalyst can be activated with the same amount of washing water and the same amount of time as the activation of the catalyst packed in a vertical reactor.

なお第2図は空気と水の気液混相流の噴射につ
いてのデータであるが空気と鉱酸(H2SO4
HCl)を含む洗浄液、空気と多量のドレンを含む
湿り蒸気及び炭酸ガス、その他のガスと洗浄液と
からなる気液混相流でも、ほゞ同様な結果が得ら
れた。なお上記組合せの気液混相流に更に水蒸気
を混入させるとその効果は一段と上昇した。
Figure 2 shows data regarding the injection of a gas-liquid multiphase flow of air and water, but air and mineral acids (H 2 SO 4 ,
Almost similar results were obtained with a gas-liquid multiphase flow consisting of a cleaning liquid containing HCl), wet steam containing air and a large amount of condensate, carbon dioxide gas, other gases, and the cleaning liquid. Furthermore, when water vapor was further mixed into the gas-liquid multiphase flow of the above combination, the effect further increased.

気液混相流に混入する蒸気は、凝縮して液とな
り、この場合、洗浄液の温度が上ることにより被
毒成分の溶解効果が若干良くなる。実験によれ
ば、被毒物の溶出率は液温が常温(20℃)から20
℃上ると約10%上り、40℃上ると約15%上昇す
る。添加する蒸気量は、蒸気及び液の温度によつ
て異り、特に蒸気の温度は利用源によつて相当大
幅に代るため上、下限は限定し難いが、噴射前の
液温を20℃〜60℃とする量の蒸気を添加すると良
い。又、乾燥蒸気を利用して洗浄液を噴射させる
ことも可能であるが、この場合には蒸気を気と考
えなければならない。この場合の添加量上、下限
は標準状態において液1に対して1〜20が適
当である。
The vapor mixed in the gas-liquid multiphase flow condenses into a liquid, and in this case, as the temperature of the cleaning liquid increases, the effect of dissolving the poisonous component becomes slightly better. According to experiments, the elution rate of poisonous substances increases from room temperature (20℃) to 20℃.
It increases by about 10% when the temperature rises by ℃, and by about 15% when the temperature rises by 40℃. The amount of steam to be added varies depending on the temperature of the steam and liquid, and in particular, the temperature of steam varies considerably depending on the source of use, so it is difficult to set upper and lower limits, but the liquid temperature before injection is 20℃. It is recommended to add enough steam to bring the temperature to ~60°C. It is also possible to spray the cleaning liquid using dry steam, but in this case the steam must be considered as air. In terms of the amount added in this case, the appropriate lower limit is 1 to 20 per liquid 1 under standard conditions.

以下、本発明の一実施態様例のフローを第3図
に示す。
The flow of one embodiment of the present invention is shown in FIG. 3 below.

第3図中、1が水洗液供給ライン、2が空気、
3が蒸気供給ラインを示す。使用条件に応じて各
供給ラインを開にし横置型反応器内の触媒ガス上
流側、又は下流側より噴射する。なお水洗後の廃
液は9のホツパーを経て常設の廃水ビツトへ導け
ばよい。4が反応器内の触媒のガス通過孔部に対
向して取付けられた噴射ノズルを示す。5が横置
型反応器本体、6が脱硝触媒、7がダクト、8が
ガス流れ方向を示す。
In Figure 3, 1 is the washing liquid supply line, 2 is air,
3 indicates the steam supply line. Depending on the usage conditions, each supply line is opened and the catalyst gas is injected from the upstream or downstream side of the horizontal reactor. The waste liquid after washing with water may be led to a permanently installed waste water bit via the hopper 9. 4 indicates an injection nozzle installed opposite the gas passage hole of the catalyst in the reactor. 5 is a horizontal reactor main body, 6 is a denitrification catalyst, 7 is a duct, and 8 is a gas flow direction.

以上の如く本発明は、空気と水等の組合せによ
る加圧混相流下で触媒表面部に噴射し再生を行う
もので以下の効果を奏する。
As described above, the present invention performs regeneration by injecting a pressurized multiphase flow of a combination of air, water, etc. onto the catalyst surface, and has the following effects.

(1) 横配置の長い触媒に液単相スプレを施すと、
噴霧ノズルに近い部分では、ガス通過口を囲む
全壁面に一様に液滴が当り全面が均一に濡れる
が、触媒の端末部に至るにつれ次第に上面に達
する液滴は減少し下面の液膜が厚くなる。この
ため、後端部上面の触媒洗浄が不充分となる。
これを防ぐには噴射圧力の上昇と水量の増加を
計ることが必要であるが、これでは余分の洗浄
液を使用することになる。気液混相流であれば
小水滴となり触媒孔(ガス通過口)内部に至る
まで均一にスプレを施すことができる。このた
め、洗浄液の使用量が減少できる。
(1) When a liquid single-phase spray is applied to a long horizontally arranged catalyst,
In the area close to the spray nozzle, the droplets hit the entire wall surrounding the gas passage port uniformly, and the entire surface is evenly wetted, but as it reaches the end of the catalyst, the number of droplets that reach the top surface gradually decreases, and a liquid film on the bottom surface is formed. It gets thicker. For this reason, the catalyst cleaning of the upper surface of the rear end portion becomes insufficient.
To prevent this, it is necessary to increase the injection pressure and the amount of water, but this would require the use of extra cleaning fluid. If it is a gas-liquid multiphase flow, the water becomes small droplets and can be sprayed uniformly all the way to the inside of the catalyst hole (gas passage port). Therefore, the amount of cleaning liquid used can be reduced.

(2) 液単相スプレで噴射圧力を上げると触媒面へ
の衡撃力が増し触媒破損の恐れがある。又、動
力の増大も相当な値となる。気液混相流では、
液単相の場合に比し、液滴の粒子が小さいため
噴射圧を相当上げても触媒に対する衡撃力は余
り増大しない。このため噴射圧を充分に高くし
て細かい液滴を遠くまで均一に飛ばすことが出
来る。又、動力の増加も比較的少ない。
(2) Increasing the injection pressure with single-phase liquid spray increases the impact force on the catalyst surface, which may damage the catalyst. Furthermore, the increase in power is also considerable. In gas-liquid multiphase flow,
Compared to the case of single-phase liquid, the particles of the liquid droplets are smaller, so even if the injection pressure is increased considerably, the impact force on the catalyst does not increase much. Therefore, the injection pressure can be set sufficiently high to uniformly spray fine droplets over a long distance. Also, the increase in power is relatively small.

なお、本発明方法は特に僅かな間隔をおいて複
数個のユニツト触媒を重ねて触媒パツクを形成せ
しめたものゝように、各ユニツト触媒間に噴射ノ
ズルを設置することができない横置型反応器に適
用するのに適している。
The method of the present invention is particularly suitable for horizontal reactors in which injection nozzles cannot be installed between each unit catalyst, such as those in which a plurality of unit catalysts are stacked at small intervals to form a catalyst pack. suitable for applying.

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

第1図は従来のスプレー水洗法に基づき触媒が
排ガス流に対し竪配置の場合と横配置の場合にお
ける被毒物質の溶出率と水洗時間の関係を示すグ
ラフ、第2図は本発明方法による被毒物質の溶出
率と水洗時間の関係を示すグラフ、第3図は本発
明方法の一実施態様例のフローを示す図である。
Fig. 1 is a graph showing the relationship between the elution rate of poisonous substances and the washing time when the catalyst is arranged vertically and horizontally relative to the exhaust gas flow based on the conventional spray washing method, and Fig. 2 is based on the method of the present invention. FIG. 3 is a graph showing the relationship between the elution rate of poisonous substances and the washing time, and FIG. 3 is a diagram showing the flow of an embodiment of the method of the present invention.

Claims (1)

【特許請求の範囲】[Claims] 1 並行流式触媒を充填した横置型反応装置内の
前記触媒が性能低下した場合、該触媒を前記反応
装置内に充填した状態で高圧気液混相流を該触媒
表面上に噴射させることを特徴とする触媒の賦活
方法。
1. When the performance of the catalyst in a horizontal reaction device filled with a parallel flow catalyst deteriorates, a high-pressure gas-liquid multiphase flow is injected onto the surface of the catalyst while the catalyst is packed in the reaction device. A method for activating a catalyst.
JP17395282A 1982-10-05 1982-10-05 Activation of catalyst Granted JPS5966352A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP17395282A JPS5966352A (en) 1982-10-05 1982-10-05 Activation of catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP17395282A JPS5966352A (en) 1982-10-05 1982-10-05 Activation of catalyst

Publications (2)

Publication Number Publication Date
JPS5966352A JPS5966352A (en) 1984-04-14
JPS6316170B2 true JPS6316170B2 (en) 1988-04-07

Family

ID=15970096

Family Applications (1)

Application Number Title Priority Date Filing Date
JP17395282A Granted JPS5966352A (en) 1982-10-05 1982-10-05 Activation of catalyst

Country Status (1)

Country Link
JP (1) JPS5966352A (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TW436332B (en) * 1996-08-19 2001-05-28 Siemens Ag Process and equipment for cleaning of contaminated object
JP7103729B2 (en) * 2017-09-21 2022-07-20 一般財団法人電力中央研究所 Impurity remover regeneration system

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5649629B2 (en) * 1973-03-05 1981-11-24
JPS5230789A (en) * 1975-09-05 1977-03-08 Nippon Kagaku Sangyo Kk Method for washing catalyst and its equipment

Also Published As

Publication number Publication date
JPS5966352A (en) 1984-04-14

Similar Documents

Publication Publication Date Title
JP5070100B2 (en) Desulfurization decarburization equipment
JPS6048147A (en) Activating method of catalyst
CN103801193B (en) A method for regenerating a solid amine CO2 capture bed
KR101608720B1 (en) Exhaust gas purification system
JPS6316170B2 (en)
JPS5830345A (en) Catalyst activation method
US5601702A (en) Removal of acidic halides from gas streams
US4036593A (en) Apparatus for purification of exhaust gases
CN206793340U (en) A serial flue gas comprehensive treatment system and an integral flue gas comprehensive treatment system
KR102183057B1 (en) Exhaust gas treatment apparatus
JP2007319832A (en) Exhaust gas treatment method and exhaust gas treatment device
JPH11300163A (en) Bag filter-type dust collector and its method
JPS6347506B2 (en)
CN109908718A (en) A low-temperature SCR denitration and catalyst online protection regeneration system for coke oven flue gas
JPS5949847A (en) Activating method of denitration catalyst
JPS58189043A (en) Activation of catalyst
JPS5817843A (en) Activating method for catalyst
JPH07100329A (en) Flue gas desulfurizing method
JPS54136572A (en) Treating method for combustion exhaust gas
JPH11276841A (en) Submerged regeneration equipment in wet desulfurization
KR102542611B1 (en) A gas pretreatment apparatus
EP0894023B1 (en) Apparatus for removal of hydrogen sulfide
SU1749501A1 (en) Catalytic neutralizer for internal combustion engine exhaust gas cleaning
JPH0773658B2 (en) Exhaust gas desulfurization method
CN208097746U (en) A kind of high salt concentration acid mist waste gas treatment equipment