JPS5962350A - Regenerating method of catalyst - Google Patents
Regenerating method of catalystInfo
- Publication number
- JPS5962350A JPS5962350A JP57173237A JP17323782A JPS5962350A JP S5962350 A JPS5962350 A JP S5962350A JP 57173237 A JP57173237 A JP 57173237A JP 17323782 A JP17323782 A JP 17323782A JP S5962350 A JPS5962350 A JP S5962350A
- Authority
- JP
- Japan
- Prior art keywords
- catalysts
- denitration
- catalyst
- water
- 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.)
- Granted
Links
Abstract
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 device.
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、長期の使用に伴なって各種
の被挿成分、例えば(:重油?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?含むダストの吸着によって生じる。The denitrification performance of the denitrification catalyst built into the denitrification reactor is
Deteriorates over time. This occurs due to the adsorption of various components, such as heavy oil, alkali metals, etc. in the treatment of boiler exhaust gas, on the catalyst, or the adsorption of dust containing organic matter in the exhaust gas, due to long-term use.
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、7
00〜800℃で焼成する方法(特開昭50−1557
87号)、水洗後100〜5〔」0°Cで焼成する方法
(特開昭50−155789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、これら馨行う為には
一説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ふ、経済的
にも不利である。Conventionally proposed methods for regenerating this catalyst include 7.
Method of firing at 00 to 800°C (Japanese Patent Application Laid-Open No. 50-1557)
No. 87), a method of firing at 100 to 5°C after washing with water (Japanese Patent Application Laid-open No. 155789/1987), etc. Both methods are recognized as effective, but in order to perform these methods, One theory is that the denitrification catalyst must be removed from the nitrification reactor, which requires a very long process time and is economically disadvantageous.
本発明は、このような欠A’aj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乞脱硝反応装虹に
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 deficiency A'aj, and provides a method for regenerating a catalyst whose denitrification performance has deteriorated while it is still installed in a denitrification reaction device.
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って経時劣化したものケ、該装置に
組込んだままで常設部と仮設部から成る水洗装置により
水洗し、該水洗排水は上記反応装置下部に常設された排
水用ホッパ又は上記反応装置下部のエアヒータ部よp系
外へ排出し、水洗完了後に上記触媒馨ボイラ熱源又はボ
イラ焚上時の排ガスにより乾燥することを特徴とする触
媒の再生法に関するものである。In other words, the present invention provides a method for removing denitrification catalysts that have deteriorated over time and that have been incorporated into a vertical flow type denitrification reaction device, by washing them with water using a water washing device consisting of a permanent part and a temporary part, while still being installed in the equipment. The waste water is discharged to the outside of the p-system through a drainage hopper permanently installed at the bottom of the reactor or an air heater section at the bottom of the reactor, and after completion of water washing, it is dried by the catalytic boiler heat source or the exhaust gas when the boiler is fired. The present invention relates to a method for regenerating a catalyst.
以下、添付図面馨参照して本発明方法ケ詳述する。Hereinafter, the method of the present invention will be described in detail with reference to the accompanying drawings.
第1し1(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(春、(B)は被処理カス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CA−)、 (B)
け級処理ガスG7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。1 (A), (B) and 2 (A), (B) are diagrams showing examples of vertical flow type denitrification equipment according to the method of the present invention. A downstream method in which the waste G to be processed flows from the upper part of the apparatus to the lower part of the apparatus, Fig. 2 CA-), (B)
This is an upstream type processing gas that flows from the bottom of the G7 device to the top of the device. (B) in each figure is a cross-sectional view, and (A) is a
) is a view taken along the line A and -A.
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ックで、数十本〜数百本
の脱硝触媒が充填されている。5〜10が本発方法に係
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、フレキシブルポース
4、給水管7、ノズルヘッダ8およびノズル9か仮設部
であり、11〜13が本発明方法に係る排水手段で、1
1は上記の下流れ方式の反応装置1に常設された排水用
ホッパ、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?そのまま排水用ホッパ
として用いるもの、16は排水用弁である。In Fig. 1 (A), (B) and Fig. 2 (A), (B), 1 is the main body of the vertical flow type denitrification reactor, and 2 is the catalyst pack made of shaped steel built into the device 1. , dozens to hundreds of denitrification catalysts are packed. 5 to 10 are parts related to the flushing device according to the present method, in which the main water supply pipe 3, the gate valve 5, the pressure gauge 6 and the intake port 10 are the permanent part, the flexible port 4, the water supply pipe 7, the nozzle header 8 and the nozzle 9. It is a temporary part, 11 to 13 are drainage means according to the method of the present invention, and 1
Reference numeral 1 denotes a drainage hopper permanently installed in the downstream reaction apparatus 1, and 12 represents an air heater originally installed in the upstream reaction apparatus 1. 16 is a drainage valve which is used as a drainage hopper as it is.
上記の水洗装置は、水洗操作に先立って、先ず反Ic1
1装置内での仮設部の組立て乞行う。すなわち、触媒パ
ック2の上面(旨さ約500〜500mm)に′ノズル
ヘッダ8の位置決めをし、ノズル9が触媒に垂直になる
ようにセラ)−J’−る。−万、給水本管5にホレキシ
ブルホース4乞接続し、これ7a1′取入ロ10から反
応装置1内へ挿入して給水管7と接続する。The above-mentioned water washing device first performs the anti-Ic1 washing operation prior to the water washing operation.
Assembling temporary parts within one device. That is, the nozzle header 8 is positioned on the upper surface of the catalyst pack 2 (approximately 500 to 500 mm thick), and the nozzle header 8 is placed so that the nozzle 9 is perpendicular to the catalyst. - Connect 4 flexible hoses to the main water supply pipe 5, insert them into the reactor 1 through the intake hole 10, and connect them to the water supply pipe 7.
土肥の組立てが完了した後、水洗操作な行う。After completing the assembly of the soil fertilizer, perform the 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
圧ケ2〜s kg/eraに調整し、ノズル9よジ噴m
状水乞触媒に噴射する。噴射された水は、排水用ホッパ
11又はエアヒータ部12を経て排水用弁15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
の製置がほぼ零になるまでとする。In the water washing operation, gradually open the gate valve 5, adjust the water pressure to 2 to s kg/era with the pressure gauge 6, and spray from the nozzle 9.
Inject the water into the catalyst. The injected water passes through the drainage hopper 11 or the air heater section 12 and is extracted from the drainage valve 15. The washing time should be set until the amount of poisonous substances such as alkali metals in the wastewater is reduced to almost zero.
この水洗操作が終、了したなら、給水本管6から圧力4
〜5んg7’crl程度の圧縮仝気?導入し、触媒バッ
ク2中に残存している水分?除去する。When this water washing operation is completed, the pressure 4 from the water supply main 6 is
Compression air of ~5g7'crl? Moisture introduced and remaining in catalyst bag 2? Remove.
しかる後、ノズルへツタ−8、ノズル9および給水管7
ケ第1図(A)、(B)および第2図(A)、(匂に示
す触媒パック2の未だ水洗していない部分に移し、上記
したようにノズルへラダ8の位置決め?行い、ノズル?
乞垂直にし、上記したようにして水洗操作と水分除去操
作9行う。After that, connect the tube 8, nozzle 9 and water supply pipe 7 to the nozzle.
Transfer the catalyst pack 2 to the unwashed part shown in Figures 1 (A), (B) and Figure 2 (A), and position the rudder 8 to the nozzle as described above. ?
Hold it vertically and perform the water washing operation and water removal operation 9 as described above.
以上の操作乞触媒パック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、竹の仮設部ケ取り除ぎ、
ボイラの熱源−例えば蒸気式%式%
(FDP)、空気予熱器(AH)からの熱風、又はボイ
ラ焚十時の排ガスを反応装置1の被処理ガスGの経路な
用いて流し乾燥させる。なお、ボイラ焚上時には軽油等
の良質の燃料か用いられるため、該排カスによる触媒の
被thは余り生じない。After performing all of the above operations on Catalyst Pack 2 and washing with water, remove the temporary bamboo parts.
A heat source of the boiler, such as a steam type % type % (FDP), hot air from an air preheater (AH), or exhaust gas at the time of boiler firing, is used to flow through the path of the gas to be treated G in the reaction device 1 for drying. It should be noted that since high-quality fuel such as light oil is used when firing up the boiler, the catalyst is not exposed to much th by the exhaust scum.
以上の操作態様に沿って、初期性能が88係であった脱
硝触媒が78係まで低下したものについて再生ケ実施し
たところ、87係まで性能回後馨みることができた。In accordance with the above-mentioned operation mode, a denitrification catalyst whose initial performance was 88 units was regenerated to 78 units, and the catalyst was able to perform well after the performance reached 87 units.
なお、この時、栴生の前および後に流した被処理ガスの
性状は、
ガス温度 : 585”0
ガス組成 : 入口 −NOx 1100pp入口
SOx 110ppm
であり、水洗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 flowing before and after the Soo are as follows: Gas temperature: 585"0 Gas composition: Inlet - NOx 1100pp Inlet
SOx was 110 ppm, and the water washing conditions and drying conditions were as follows.
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
乾燥粂件
使用熱の=4!油乞用いたボイラ焚上時の1200の排
ガス
時間:1時間
また、上記の脱硝性能は下式によυ求められる脱硝率?
示したものである。Washing conditions Water quality: Industrial water Quantity: 10 times the apparent volume of the catalyst Water temperature: Room temperature Time = 1 hour Heat used for drying cake = 4! 1200 exhaust gas time when firing a boiler using oil: 1 hour Also, is the above denitrification performance the denitrification rate calculated by the formula below?
This is what is shown.
入口NOx磯度
0ただし、NOx濃厩装置て024係換算値である)以
上詳述したように、本発明方法によれば、脱硝触媒?横
流れ型脱硝反応装置に組込んだままでB生することがで
き、再生に要する時間は極めて短詩「IJlとなり、経
済的にも極めて有オリである。(However, the inlet NOx level is 0. However, the value is converted to 024 coefficient for the NOx concentration device.) As detailed above, according to the method of the present invention, the denitrification catalyst? It is possible to perform B-generation while being installed in a cross-flow type denitrification reactor, and the time required for regeneration is extremely short, making it extremely economical.
第1図(ん、(B)および&42図1(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Iノ′r面図、囚は(B)のA−A
線矢視復代理人 内 1) 明後
代理人 萩 原 亮 −(A)
(A)
岐阜県羽島郡笠松町円城寺1624
番地の13
■出 願 人 日本碍子株式会社
名古屋市瑞穂区須田町2番56号Figures 1 (B) and &42 Figures 1 (A) and 1 (B) are diagrams showing an example of a vertical flow type denitrification reactor according to the method of the present invention, and (B) in each figure is R view, the figure is A-A in (B)
1) Post-Morning Agent Ryo Hagiwara - (A) (A) 13-1624 Enjoji, Kasamatsu-cho, Hashima-gun, Gifu Prefecture ■Applicant Nippon Insulator Co., Ltd. 2, Suda-cho, Mizuho-ku, Nagoya City No. 56
Claims (1)
生法において、該触媒乞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水洗し、該水洗排
水は前記反応装置下部に常設さねた排水用ホッパ又は前
記反応装置下部σノエ了ヒータ部よp系外へ排出し、水
洗完了後に前記触媒ぞボイラ熱源又はボイラ焚上時の排
ガスにより乾燥することケ特徴とする触媒の再生法。In a method for regenerating a denitrification catalyst incorporated in a vertical flow type denitrification reaction device, the catalyst is washed with water using a water washing device consisting of a permanent part and a temporary part while the catalyst is installed in the device, and the washing wastewater is used for the reaction. It is characterized by discharging the water out of the p-system through a drainage hopper permanently installed at the bottom of the device or the heater section at the bottom of the reaction device, and drying it with the catalyst boiler heat source or the exhaust gas when the boiler is fired after completion of water washing. A method for regenerating catalysts.
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 true JPS5962350A (en) | 1984-04-09 |
JPS6347506B2 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 (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0824973A3 (en) * | 1996-08-19 | 1998-12-02 | Siemens Aktiengesellschaft | Method and installation for cleaning a contaminated object |
WO2004000461A1 (en) * | 2002-06-21 | 2003-12-31 | The Chugoku Electric Power Co.,Inc. | METHOD OF REGENERATING NOx REMOVAL CATALYST |
JP2014168775A (en) * | 2013-03-01 | 2014-09-18 | Wl Gore Andd Associates Gmbh | Fiber fabric filter system, regeneration method of fiber fabric filter and regeneration device of the same |
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 |
Families Citing this family (1)
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 |
Citations (3)
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 |
-
1982
- 1982-10-04 JP JP57173237A patent/JPS5962350A/en active Granted
Patent Citations (3)
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 (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0824973A3 (en) * | 1996-08-19 | 1998-12-02 | Siemens Aktiengesellschaft | Method and installation for cleaning a contaminated object |
WO2004000461A1 (en) * | 2002-06-21 | 2003-12-31 | The Chugoku Electric Power Co.,Inc. | METHOD OF REGENERATING NOx REMOVAL CATALYST |
JP2005199108A (en) * | 2002-06-21 | 2005-07-28 | Chugoku Electric Power Co Inc:The | Method for regenerating denitration catalyst |
JP4578048B2 (en) * | 2002-06-21 | 2010-11-10 | 中国電力株式会社 | Denitration catalyst regeneration method |
US8980779B2 (en) | 2002-06-21 | 2015-03-17 | The Chugoku Electric Power Co., Inc. | Method of regenerating NOx removal catalyst |
JP2014168775A (en) * | 2013-03-01 | 2014-09-18 | Wl Gore Andd Associates Gmbh | Fiber fabric filter system, regeneration method of fiber fabric filter and regeneration device of the same |
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 |
Also Published As
Publication number | Publication date |
---|---|
JPS6347506B2 (en) | 1988-09-22 |
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