JPS6347506B2 - - Google Patents

Info

Publication number
JPS6347506B2
JPS6347506B2 JP57173237A JP17323782A JPS6347506B2 JP S6347506 B2 JPS6347506 B2 JP S6347506B2 JP 57173237 A JP57173237 A JP 57173237A JP 17323782 A JP17323782 A JP 17323782A JP S6347506 B2 JPS6347506 B2 JP S6347506B2
Authority
JP
Japan
Prior art keywords
catalyst
water
denitrification
boiler
washing
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
JP57173237A
Other languages
Japanese (ja)
Other versions
JPS5962350A (en
Inventor
Yukio Nagaoka
Toshio Suzuki
Takafuru Kobayashi
Toku Fukuyama
Kohei Suyama
Kazuhiko Ito
Hideyuki Masaki
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 JP57173237A priority Critical patent/JPS5962350A/en
Publication of JPS5962350A publication Critical patent/JPS5962350A/en
Publication of JPS6347506B2 publication Critical patent/JPS6347506B2/ja
Granted legal-status Critical Current

Links

Description

【発明の詳細な説明】 本発明は、縦流れ型の脱硝反応装置に組込まれ
ている脱硝触媒を、装置に組込んだまま再生する
ことのできる方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for regenerating a denitrification catalyst installed in a vertical flow type denitrification reactor while it is still installed in the apparatus.

脱硝反応装置に組込まれている脱硝触媒の脱硝
性能は、経時的に劣化する。これは、長期の使用
に伴なつて各種の被毒成分、例えばC重油を使用
するボイラ排ガス処理におけるアルカリ金属類等
の触媒への付着、或いは排ガス中の有機物を含む
ダストの吸着によつて生じる。
The denitrification performance of the denitrification catalyst incorporated in the denitrification reactor deteriorates over time. This is caused by various poisonous components that occur over long-term use, such as adhesion of alkali metals to the catalyst in boiler exhaust gas treatment using C heavy oil, or adsorption of dust containing organic matter in the exhaust gas. .

脱硝性能が劣化した触媒は、実用効果を失うた
め、廃棄するか、もしくは経済的な再生の手段を
講じる必要がある。
Catalysts whose denitrification performance has deteriorated lose their practical effectiveness, so it is necessary to dispose of them or take measures for economical regeneration.

従来より提案されているこの触媒の再生法とし
ては、700〜800℃で焼成する方法(特開昭50−
153787号)、水洗後100〜500℃で焼成する方法
(特開昭50−153789号)等があり、いずれも有効
であることが認められているが、これらを行う為
には、脱硝反応装置から脱硝触媒を取り出さなけ
ればならず、工程的に非常に長時間が必要である
ばかりか、経済的にも不利である。
The method of regenerating this catalyst that has been proposed in the past is a method of firing at 700 to 800°C (Japanese Patent Application Laid-open No.
153787), and a method of calcination at 100 to 500℃ after washing with water (Japanese Patent Application Laid-Open No. 153789), both of which are recognized as effective, but in order to carry out these methods, a denitrification reaction device is required. The denitrification catalyst must be taken out from the tank, which not only requires a very long process time but is also economically disadvantageous.

本発明は、このような欠点を排除するためにな
されたもので、脱硝性能が劣化した触媒を脱硝反
応装置に組込んだままで再生する方法を提供する
ものである。
The present invention has been made to eliminate such drawbacks, and provides a method for regenerating a catalyst whose denitrification performance has deteriorated while it is still installed in a denitrification reactor.

すなわち本発明は、縦流れ型の脱硝反応装置に
組込まれている脱硝触媒であつて経時劣化したも
のを、該装置に組込んだままで常設部と仮設部と
から成る水洗装置により前記触媒の見かけ体積の
10倍の水量で水洗する工程、該水洗排水を前記反
応装置下部に常設された排水用ホツパ又は前記反
応装置下部のエアヒータ部より系外へ排出する工
程、水洗完了後に圧縮空気を導入して前記触媒中
に残存している水分を除去する工程、前記触媒を
ボイラ熱源又はボイラ焚上時の120℃以上の温度
の排ガスにより乾燥する工程からなる触媒の再生
法に関するものである。
In other words, the present invention cleans a denitration catalyst that has deteriorated over time and is installed in a vertical flow type denitrification reaction device by cleaning the appearance of the catalyst by using a water washing device consisting of a permanent part and a temporary part while the denitration catalyst is installed in the equipment. of volume
A step of washing with 10 times the amount of water, a step of discharging the washed water out of the system from a drainage hopper permanently installed at the bottom of the reaction device or an air heater section at the bottom of the reaction device, and a step of introducing compressed air after the washing is completed to The present invention relates to a method for regenerating a catalyst, which comprises a step of removing moisture remaining in the catalyst, and a step of drying the catalyst using a boiler heat source or exhaust gas at a temperature of 120° C. or higher when the boiler is fired.

以下、添付図面を参照して本発明方法を詳述す
る。
Hereinafter, the method of the present invention will be explained in detail with reference to the accompanying drawings.

第1図A,Bおよび第2図A,Bは本発明方法
に係る縦流れ型脱硝装置の例を示す図で、第1図
A,Bは被処理ガスGを装置上部から装置下部へ
流す下流れ方式のもの、第2図A,Bは被処理ガ
スGを装置下部から装置上部へ流す上流れ方式の
ものであり、各図のBは断面図、AはBのA―A
線矢視図である。
Figures 1A and B and Figures 2A and B are diagrams showing examples of vertical flow type denitrification equipment according to the method of the present invention, and Figures 1A and B flow the gas G to be treated from the upper part of the equipment to the lower part of the equipment. Figure 2 A and B are of the downstream type, and Figures 2A and B are of the upstream type in which the gas to be processed G flows from the bottom of the device to the top of the device.
It is a line arrow view.

第1図A,Bおよび第2図A,Bにおいて、1
は縦流れ型脱硝反応装置本体、2は該装置1に組
込まれている型鋼製の触媒パツクで、数十本〜数
百本の脱硝触媒が充填されている。3〜10が本発
明方法に係る水洗装置に関する部分で、給水本管
3、仕切弁5、圧力計6および取入口10が常設
部、フレキシブルホース4、給水管7、ノズルヘ
ツダ8およびノズル9が仮設部であり、11〜1
3が本発明方法に係る排水手段で、11は上記の
下流れ方式の反応装置1に常設された排水用ホツ
パ、12は上記の上流れ方式の反応装置1にもと
もと設置されているエアヒータ部をそのまま排水
用ホツパとして用いるもの、13は排水用弁であ
る。
In Figure 1 A, B and Figure 2 A, B, 1
2 is a vertical flow type denitrification reactor main body, and 2 is a shaped steel catalyst pack incorporated in the device 1, which is filled with several tens to hundreds of denitrification catalysts. 3 to 10 are parts related to the flushing device according to the method of the present invention, where the main water supply pipe 3, gate valve 5, pressure gauge 6, and intake port 10 are permanently installed, and the flexible hose 4, water supply pipe 7, nozzle header 8, and nozzle 9 are temporary parts. part, 11-1
3 is a drainage means according to the method of the present invention, 11 is a drainage hopper permanently installed in the above-mentioned downstream type reaction apparatus 1, and 12 is an air heater section originally installed in the above-mentioned upstream type reaction apparatus 1. The valve 13 is used as a drainage hopper as it is.

上記の水洗装置は、水洗操作に先立つて、先ず
反応装置内での仮設部の組立てを行う。すなわ
ち、触媒パツク2の上面(高さ約300〜500mm)に
ノズルヘツダ8の位置決めをし、ノズル9が触媒
に垂直になるようにセツトする。一方、給水本管
3にフレキシブルホース4を接続し、これを取入
口10から反応装置1内へ挿入して給水管7と接
続する。
In the above-mentioned water washing apparatus, a temporary part is first assembled within the reaction apparatus prior to the water washing operation. That is, the nozzle header 8 is positioned on the upper surface of the catalyst pack 2 (about 300 to 500 mm in height) and set so that the nozzle 9 is perpendicular to the catalyst. On the other hand, a flexible hose 4 is connected to the main water supply pipe 3, inserted into the reaction apparatus 1 through the inlet 10, and connected to the water supply pipe 7.

上記の組立てが完了した後、水洗操作を行う。 After completing the above assembly, perform a water washing operation.

水洗操作は、仕切弁5を徐々に開にし、圧力計
6にて水圧を2〜3Kg/cm2に調整し、ノズル9よ
り、噴霧状水を触媒に噴射する。噴射水量は、水
洗を効果的に行い、かつ水洗排水を極力少なくす
るために、触媒の見かけ体積の10倍量とする。噴
射された水は、排水用ホツパ11又はエアヒータ
部12を経て排水用弁13から抜出される。水洗
時間は、排水中のアルカリ金属等の被毒物の濃度
がほぼ零になるまでとする。
In the water washing operation, the gate valve 5 is gradually opened, the water pressure is adjusted to 2 to 3 kg/cm 2 using the pressure gauge 6, and atomized water is injected from the nozzle 9 onto the catalyst. The amount of water injected is set to be 10 times the apparent volume of the catalyst in order to perform water washing effectively and to minimize washing wastewater. The injected water passes through the drainage hopper 11 or the air heater section 12 and is extracted from the drainage valve 13. The washing time should be set until the concentration of poisonous substances such as alkali metals in the waste water reaches almost zero.

この水洗操作が終了したなら、給水本管3から
圧力4〜5Kg/cm2程度の圧縮空気を導入し、触媒
パツク2中に残存している水分を除去する。この
水分除去操作は、触媒パツク2から水滴が落ちな
くなる程度迄、一般には5分以上、好ましくは10
分以上行なう。もし、この水分除去操作を行わず
に、後述のボイラ熱源からの熱風又はボイラ焚上
時の120℃以上の温度の排ガスにより触媒の乾燥
を行うと、触媒が破損する虞れがある。
When this water washing operation is completed, compressed air at a pressure of about 4 to 5 kg/cm 2 is introduced from the main water supply pipe 3 to remove moisture remaining in the catalyst pack 2. This water removal operation is generally carried out for 5 minutes or more, preferably 10 minutes or more, until water drops no longer fall from the catalyst pack 2.
Do this for more than a minute. If the catalyst is dried using hot air from a boiler heat source (described later) or exhaust gas having a temperature of 120° C. or higher when the boiler is fired without performing this moisture removal operation, there is a risk that the catalyst will be damaged.

しかる後、ノズルヘツダー8、ノズル9および
給水管7を第1図A,Bおよび第2図A,Bに示
す触媒パツク2の未だ水洗していない部分に移
し、上記したようにノズルヘツダ8の位置決めを
行い、ノズル9を垂直にし、上記したようにして
水洗操作と水分除去操作を行う。
Thereafter, the nozzle header 8, nozzle 9, and water supply pipe 7 are moved to the parts of the catalyst pack 2 that have not been washed yet as shown in FIGS. 1A and B and 2A and B, and the nozzle header 8 is positioned as described above. Then, the nozzle 9 is made vertical, and the water washing operation and water removal operation are performed as described above.

以上の操作を触媒パツク2の全てについて行な
い、水洗が全て完了したなら、水洗装置の仮設部
を取り除き、ボイラの熱源、例えば蒸気式空気予
熱器(SAH)、通風機(FAN)、押込通風機
(FDF)、空気予熱器(AH)からの熱風、又はボ
イラ焚上時の120℃以上の温度の排ガスを反応装
置1の被処理ガスGの経路を用いて流し乾燥させ
る。上記のボイラ焚上時の排ガスとして、120℃
以上の温度のものを使用するのは、触媒に付着し
ている水分を蒸発・飛散させるのに120℃以上の
温度が必要だからである(なお、上記のボイラ熱
源からの熱風は一般に120℃以上の温度となつて
いる)。なお、ボイラ焚上時には軽油等の良質の
燃料が用いられるため、該排ガスによる触媒の被
毒は余り生じないばかりか、該排ガス中に微量含
まれるSOxが触媒に付着し、このSOxの助触媒効
果により再生触媒の性能を新品触媒と略同等にま
で回復させる。
After performing the above operations on all catalyst packs 2 and washing with water is complete, remove the temporary part of the water washing device and remove the heat source of the boiler, such as the steam air preheater (SAH), fan (FAN), forced draft fan, etc. (FDF), hot air from the air preheater (AH), or exhaust gas at a temperature of 120° C. or higher when the boiler is fired is passed through the path of the gas to be treated G in the reaction device 1 for drying. As the exhaust gas when firing the above boiler, 120℃
The reason for using a temperature higher than 120℃ is that a temperature of 120℃ or higher is required to evaporate and scatter the water adhering to the catalyst (the hot air from the boiler heat source mentioned above is generally 120℃ or higher temperature). Furthermore, since high-quality fuel such as diesel oil is used when firing the boiler, the catalyst is not poisoned by the exhaust gas much, and a small amount of SOx contained in the exhaust gas adheres to the catalyst, causing the SOx to become a co-catalyst. The effect restores the performance of the regenerated catalyst to almost the same level as a new catalyst.

以上の操作態様に沿つて、初期性能が88%であ
つた脱硝触媒が78%まで低下したものについて再
生を実施したところ、87%まで性能回復をみるこ
とができた。
In accordance with the above operation mode, a denitrification catalyst whose initial performance had dropped to 78% was regenerated, and the performance was recovered to 87%.

なお、この時、再生の前および後に流した被処
理ガスの性状は、 ガス温度 :385℃ ガス組成 :入口 NOx 100ppm 入口 SOx 110ppm であり、水洗条件、水分除去条件および乾燥条件
は次の通りとした。
At this time, the properties of the gas to be treated before and after regeneration were as follows: Gas temperature: 385°C Gas composition: Inlet NOx 100ppm Inlet SOx 110ppm, and the water washing conditions, water removal conditions, and drying conditions were as follows. did.

水洗条件 水 質 : 工業用水 水 量 : 触媒の見かけ体積の10倍 水 温 : 常 温 時 間 : 1時間 水分除去条件 使用空気 : 4.5Kg/cm2の圧縮空気 時 間 : 7分 乾燥条件 使用熱源 :軽油を用いたボイラ焚上時の
120℃の排ガス 時 間 :1時間 また、上記の脱硝性能は下式により求められる
脱硝率を示したものである。
Washing conditions Water quality: Industrial water Amount: Water 10 times the apparent volume of the catalyst Temperature: Room temperature Time: 1 hour Moisture removal conditions Air used: 4.5 Kg/ cm2 compressed air Time: 7 minutes Drying conditions Heat source used : When firing a boiler using light oil
Exhaust gas at 120°C Time: 1 hour In addition, the above denitrification performance indicates the denitrification rate determined by the formula below.

脱硝率=入口NOx濃度−出口NOx濃度/入口NOx濃度 (ただし、NOx濃度は全てO24%換算値である) 以上詳述したように、本発明方法によれば、脱
硝触媒を横流れ型脱硝反応装置に組込んだままで
再生することができ、再生に要する時間は極めて
短時間となり、経済的にも極めて有利である。
Denitration rate = inlet NOx concentration - outlet NOx concentration / inlet NOx concentration (however, all NOx concentrations are O 2 4% equivalent values) As detailed above, according to the method of the present invention, the denitrification catalyst is It can be regenerated while being installed in the reactor, the time required for regeneration is extremely short, and it is extremely advantageous economically.

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

第1図A,Bおよび第2図A,Bは本発明方法
に係る縦流れ型の脱硝反応装置の例を示す図で、
各図のBは断面図、AはBのA―A線矢視図であ
る。
1A and 2B and 2A and 2B are diagrams showing examples of vertical flow type denitrification reactors according to the method of the present invention,
In each figure, B is a sectional view, and A is a view of B taken along the line AA.

Claims (1)

【特許請求の範囲】[Claims] 1 縦流れ型の脱硝反応装置に組込まれている脱
硝触媒の再生法において、該触媒を前記装置に組
込んだまま、常設部と仮設部とから成る水洗装置
により前記触媒の見かけ体積の10倍の水量で水洗
する工程、該水洗排水を前記反応装置下部に常設
された排水用ホツパ又は前記反応装置下部のエア
ヒータ部より系外へ排出する工程、水洗完了後に
圧縮空気を導入して前記触媒中に残存している水
分を除去する工程、前記触媒をボイラ熱源又はボ
イラ焚上時の120℃以上の温度の排ガスにより乾
燥する工程からなる触媒の再生法。
1. In a method for regenerating a denitrification catalyst installed in a vertical flow type denitrification reactor, the catalyst is removed by 10 times the apparent volume of the catalyst using a water washing device consisting of a permanent part and a temporary part while the catalyst is installed in the equipment. a step of discharging the washed wastewater out of the system from a drainage hopper permanently installed at the bottom of the reaction device or an air heater section at the bottom of the reaction device; and a step of introducing compressed air into the catalyst after the washing is completed. A method for regenerating a catalyst comprising the steps of: removing moisture remaining in the catalyst; and drying the catalyst using a boiler heat source or exhaust gas at a temperature of 120° C. or higher when the boiler is fired.
JP57173237A 1982-10-04 1982-10-04 Regenerating method of catalyst Granted JPS5962350A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57173237A JPS5962350A (en) 1982-10-04 1982-10-04 Regenerating method of catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57173237A JPS5962350A (en) 1982-10-04 1982-10-04 Regenerating method of catalyst

Publications (2)

Publication Number Publication Date
JPS5962350A JPS5962350A (en) 1984-04-09
JPS6347506B2 true JPS6347506B2 (en) 1988-09-22

Family

ID=15956690

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57173237A Granted JPS5962350A (en) 1982-10-04 1982-10-04 Regenerating method of catalyst

Country Status (1)

Country Link
JP (1) JPS5962350A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103127823A (en) * 2013-02-22 2013-06-05 邹炎 Modular flue gas cleaning device with in-situ regeneration function, and regeneration method

Families Citing this family (4)

* 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
JP4578048B2 (en) * 2002-06-21 2010-11-10 中国電力株式会社 Denitration catalyst regeneration method
DK2772293T3 (en) * 2013-03-01 2020-08-24 Gore & Ass Substance filter system and method for regenerating a substance filter
CN106215696A (en) * 2016-09-22 2016-12-14 中冶焦耐(大连)工程技术有限公司 Flue gases of cock oven SCR denitration is anti-blocking, Method of blockage removal and device

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5228460A (en) * 1975-08-29 1977-03-03 Kobe Steel Ltd Catalytic reaction apparatus
JPS5230789A (en) * 1975-09-05 1977-03-08 Nippon Kagaku Sangyo Kk Method for washing catalyst and its equipment
JPS5637053A (en) * 1979-09-03 1981-04-10 Kawasaki Heavy Ind Ltd Regenerating treatment of denitrificating catalyst

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5228460A (en) * 1975-08-29 1977-03-03 Kobe Steel Ltd Catalytic reaction apparatus
JPS5230789A (en) * 1975-09-05 1977-03-08 Nippon Kagaku Sangyo Kk Method for washing catalyst and its equipment
JPS5637053A (en) * 1979-09-03 1981-04-10 Kawasaki Heavy Ind Ltd Regenerating treatment of denitrificating catalyst

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103127823A (en) * 2013-02-22 2013-06-05 邹炎 Modular flue gas cleaning device with in-situ regeneration function, and regeneration method

Also Published As

Publication number Publication date
JPS5962350A (en) 1984-04-09

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