JPS5962329A - Catalyst regeneration method - Google Patents
Catalyst regeneration methodInfo
- Publication number
- JPS5962329A JPS5962329A JP57170934A JP17093482A JPS5962329A JP S5962329 A JPS5962329 A JP S5962329A JP 57170934 A JP57170934 A JP 57170934A JP 17093482 A JP17093482 A JP 17093482A JP S5962329 A JPS5962329 A JP S5962329A
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- water
- washing
- nozzle
- boiler
- 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
- 239000003054 catalyst Substances 0.000 title claims abstract description 35
- 238000011069 regeneration method Methods 0.000 title claims description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 38
- 238000005406 washing Methods 0.000 claims abstract description 30
- 238000001035 drying Methods 0.000 claims abstract description 5
- 238000000034 method Methods 0.000 claims description 15
- 238000010304 firing Methods 0.000 claims description 5
- 230000001172 regenerating effect Effects 0.000 claims description 4
- 230000008929 regeneration Effects 0.000 description 3
- 229910052783 alkali metal Inorganic materials 0.000 description 2
- 150000001340 alkali metals Chemical class 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000003921 oil Substances 0.000 description 2
- 231100000614 poison Toxicity 0.000 description 2
- 230000007096 poisonous effect Effects 0.000 description 2
- 229910000831 Steel Inorganic materials 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 239000008235 industrial water Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
- 125000000391 vinyl group Chemical group [H]C([*])=C([H])[H] 0.000 description 1
- 229920002554 vinyl polymer Polymers 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Abstract
Description
【発明の詳細な説明】
本発明は、横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1再生することのできる方
法VC関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method VC that can regenerate a denitrification catalyst installed in a cross-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 adhesion of various poisonous components, such as alkali metals, to the catalyst in the treatment of boiler exhaust gas using C heavy oil due to long-term use, 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、7
00〜800℃で焼成する方法(t¥f開昭50−15
3787号〕、水洗後100〜500°Cで焼成する方
法(特開昭50−153789号〕等がめり、いずれも
有効でる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。Conventionally proposed methods for regenerating this catalyst include 7.
Method of firing at 00 to 800℃ (t¥f
No. 3787], a method of firing at 100 to 500°C after washing with water (Japanese Unexamined Patent Publication No. 153789/1989), etc., and these methods are recognized to be effective, but in order to carry out these methods, a denitrification reaction is required. The denitrification catalyst must be removed from the equipment, 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、横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
より水洗し、次いで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脱硝触媒の再生方法
VC関するものである。That is, in the present invention, a denitrification catalyst installed in a cross-flow type denitrification reactor that has deteriorated over time is washed with water using a water washing device consisting of a permanent part and a temporary part, while it is still installed in the equipment, and then The present invention relates to a method VC for regenerating a denitrification catalyst, which is characterized by drying using a boiler heat source or exhaust gas during boiler firing.
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)(は本発明方法に係る横流れ型脱
硝反応装置の一例を示す図で、第1図(A)が断面図、
第1図(B)が第1図(A)のA矢視図、第2図(A)
、CB)は第1図(A)、C,B)中符号2で示す触媒
バック部の詳細図で、第2図(A)が断面図、第2図(
、B)が第2図(A)のA−A線矢視図である。FIGS. 1(A) and 1(B) are diagrams showing an example of a cross-flow type denitrification reactor according to the method of the present invention; FIG. 1(A) is a cross-sectional view;
Figure 1 (B) is a view from arrow A in Figure 1 (A), Figure 2 (A)
, CB) are detailed views of the catalyst back portion indicated by the reference numeral 2 in FIGS. 1(A), C, and B), and FIG.
, B) is a view taken along the line AA in FIG. 2(A).
第1図(A)、(B)および第2図(A)、(B)にお
いて、1は横流れ型脱硝反応【置本体、2は該装置1に
組込まれている型鋼製の触媒バックで、数十本〜数百本
の脱硝触媒15が充填されている。3〜14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、取入口10、排水用弁11および排水用
ホッパ12が常設部、フレキシブルホース4.4’給水
管7、ノズルへラダ8、ノズル9、水洗用入口ダクト1
6および水洗用出口ダクト14が仮設部でめる。なお、
水洗用入口、出口ダクト15゜14は、アルミ等の軽金
属製の枠にビニール等のフードを張ったもので、反応装
置1内での組立てが容易であり、これらのダク)13.
14は、第2図(A)、CB) K示すように、触媒バ
ック2のフランジ部16にボルト17により取付けられ
る。In Fig. 1 (A), (B) and Fig. 2 (A), (B), 1 is the cross-flow type denitrification reaction [equipment body], and 2 is the catalyst bag made of shaped steel built into the device 1. , tens to hundreds of denitrification catalysts 15 are filled. 3 to 14 are parts related to the water washing device according to the method of the present invention, in which the main water supply pipe 3, the gate valve 5, the pressure gauge 6, the intake port 10, the drainage valve 11 and the drainage hopper 12 are permanent parts, and the flexible hose 4.4 'Water supply pipe 7, ladder to nozzle 8, nozzle 9, water washing inlet duct 1
6 and a water washing outlet duct 14 are installed in the temporary part. In addition,
The water washing inlet and outlet ducts 15 and 14 are made of a frame made of light metal such as aluminum and covered with a hood made of vinyl or the like, and are easy to assemble within the reactor 1.
14 is attached to the flange portion 16 of the catalyst bag 2 with bolts 17, as shown in FIGS. 2(A) and 2(CB)K.
上記の水洗装置は、水洗操作に先立って、先ず反応装置
内での仮設部の組立てを行う。すなわち、触媒バック2
の上流側(被処理ガスGの流れ方向に対する上流側〕約
600〜500imにノズルヘッダ8の位置を決め、ノ
ズル9が触媒に対して垂直になるようにし、ダクト16
゜14を上記のようにボルト17でフランジ部16VC
取付ける。次に、給水車y s vcフレキシブルホー
ス4全接続し、これを取入口10から反応装置1内へ挿
入して給水管7と接続し、また出口ダクト14をフレキ
シブルホース4′ニより排水用ホッパ12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, catalyst bag 2
The nozzle header 8 is positioned approximately 600 to 500 mm upstream of the flow direction of the gas to be treated (G) so that the nozzle 9 is perpendicular to the catalyst.
゜14 as above with bolt 17 to flange part 16VC
Install. Next, the water tank ysvc flexible hose 4 is fully connected, and this is inserted into the reactor 1 through the inlet 10 and connected to the water supply pipe 7, and the outlet duct 14 is connected to the drainage hopper through the flexible hose 4'. Connect with 12.
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!JJ弁5を徐々に開にし、圧力計6に
て水圧を2〜3に9/α2に調整し、ノズル9より噴唇
状水を触媒に噴射する。噴射された水は出ロダク1−1
4に集められ、フレキシブルホース4′と排水用ホッパ
12を経て、ライン18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楡物の濃度がほぼ零になる
までとする。Washing with water is a breeze! The JJ valve 5 is gradually opened, the water pressure is adjusted to 2 to 3 (9/α2) using the pressure gauge 6, and the nozzle 9 injects lip-shaped water onto the catalyst. The sprayed water comes out Rodak 1-1
4, and is extracted from a line 18 through a flexible hose 4' and a drainage hopper 12. The washing time is
This should be done until the concentration of pollutants such as alkali metals in the wastewater 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/1yn2程度の圧縮空気を導入し、触媒バック
2中に残存している水分を除去する。When this water washing operation is completed, the pressure 4~ from the water supply main 3
Compressed air of about 5 kg/1yn2 is introduced to remove moisture remaining in the catalyst bag 2.
しかる後、水洗用入口ダクト16および水洗用出口ダク
ト14をはずし、ノズルヘッダ8、ノズル9および給水
管7を第1図(AJ、(B)に示す触媒バック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ヘッ
ダ8の位置決め全行い、ノズル9を垂直にし、水洗用入
口、出ロダク)13.14(i7ボルトで取付け、上記
したようにして水洗操作と水分除去操作を行う。After that, the inlet duct 16 for washing and the outlet duct 14 for washing are removed, and the nozzle header 8, nozzle 9, and water supply pipe 7 are placed in the part of the catalyst bag 2 that has not been washed yet as shown in Fig. 1 (AJ, (B)). Transfer the nozzle header 8 to its original position as described above, set the nozzle 9 vertically, install the water washing inlet and outlet rods with the I7 bolts, and perform the water washing and water removal operations as described above.
この水洗の際、水洗用入口、出口ダクト16゜14は、
ノズル?からの噴霧状水が被毒物全件なって飛散し、既
に水況乞終了している触媒にかかり、該触媒全汚染する
ことから防止する作用をなす。During this water washing, the water washing inlet and outlet ducts 16°14 are
nozzle? This prevents the sprayed water from scattering all the poisonous substances and splashing onto the catalyst, which has already been watered, and contaminating the entire catalyst.
以上の操作を触媒バック2の全てについて行ない、水洗
が全て兄了したなら、水洗装j区の仮設部を取り除き、
ボイラの熱源、例えは蒸気式%式%)
風機(FDP)、空気予熱器(AH)からの熱風、又は
ボイラ焚上時の排カスを反応装置1の被処理ガスGの経
路を用いて流し乾燥させる。なお、ボイラ焚上時[は軽
油等の良質の燃料が用いられるため、該排カスによる触
媒の被毒は余り生じない。After performing the above operations on all of the catalyst bags 2 and washing them all, remove the temporary part of the washing section J.
The heat source of the boiler, for example, the steam type % type %), the hot air from the blower (FDP), the air preheater (AH), or the exhaust gas from the boiler firing is passed through the path of the gas to be treated G in the reactor 1. dry. In addition, since high-quality fuel such as light oil is used when the boiler is fired, the catalyst is not poisoned by the waste.
以上の操作態様に沿って、初期性能が88%であった脱
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%t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 was 88% was regenerated to 78%, and the performance was recovered at 87%t.
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 人口NoX100 ppm
入口BOX110 ppm
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 before and after the regeneration were as follows: Gas temperature: 385° C. Gas composition: Population: NoX: 100 ppm; Inlet box: 110 ppm; and the 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
乾燥条件
使用熱源:軽油を用いたボイラ契止時の120℃の排ガ
ス
時間:1時間
捷た、上記触媒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 of water: 10 times the apparent volume of the catalyst Water temperature: Room temperature Time = 1 hour Drying conditions Heat source used: Boiler using light oil Exhaust gas at 120°C when shutting down Time: 1 hour after washing the above catalyst The denitrification performance indicates the denitrification rate determined by the formula below.
入口NOx濃度
(ただし、NOx濃度は全て024襲換算値である。〕
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V?−要する時間は極めて短時間となり、経
済的にも有利である。Inlet NOx concentration (However, all NOx concentrations are 024 attack equivalent values.) As detailed above, according to the method of the present invention, it is possible to regenerate the denitrification catalyst while it is installed in the cross-flow type denitrification reactor. , Regeneration V?--The required time is extremely short, and it is economically advantageous.
第1図(A)、(B)は本発明方法に係る横流れ型の脱
硝反応装盾の一例を示す図で、第1図(A)が断面図、
第1図CB)が第1図(A)のA矢視図、PjfJ2図
(A)、(B)は第1図(A)、 (B)中、符号2で
示す触媒バック部の詳細図で、第2図(A)が断面図、
第2図<、B)が第2図(A)のA−A線矢視図である
。
復代理人 内 1) 明
後代理人 萩原亮−
天
(A)
第2図
(A)
(B)
5
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FIGS. 1(A) and 1(B) are diagrams showing an example of a cross-flow type denitrification reaction shield according to the method of the present invention, and FIG. 1(A) is a cross-sectional view;
Fig. 1 CB) is a view in the direction of arrow A in Fig. 1 (A), and PjfJ2 Figs. So, Figure 2 (A) is a cross-sectional view,
FIG. 2<, B) is a view taken along the line A--A in FIG. 2(A). Sub-Agents 1) Post-August Agent Ryo Hagiwara - Ten (A) Figure 2 (A) (B) 5 13-1624 Enjoji, Kasamatsu-cho, Hashima-gun, Gifu Prefecture ■Applicant Nippon Insulator Co., Ltd. Mizuho-ku, Nagoya City Sudacho 2-56
Claims (1)
生方法におりて、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水洗し、次いで
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
と全特徴とする触媒の再生方法。In a method for regenerating a denitrification catalyst incorporated in a cross-flow type denitrification reaction device, the catalyst is washed with water in a water washing device consisting of a permanent part and a temporary part while it is still installed in the device, and then the boiler heat source or boiler A catalyst regeneration method characterized by drying with exhaust gas during firing.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57170934A JPS5962329A (en) | 1982-10-01 | 1982-10-01 | Catalyst regeneration method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57170934A JPS5962329A (en) | 1982-10-01 | 1982-10-01 | Catalyst regeneration method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5962329A true JPS5962329A (en) | 1984-04-09 |
| JPH0148053B2 JPH0148053B2 (en) | 1989-10-17 |
Family
ID=15914070
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57170934A Granted JPS5962329A (en) | 1982-10-01 | 1982-10-01 | Catalyst regeneration method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5962329A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS61132036U (en) * | 1985-02-04 | 1986-08-18 | ||
| CN104707482A (en) * | 2015-03-19 | 2015-06-17 | 南京宇行环保科技有限公司 | Regeneration method of deactivated catalyst |
| CN105396627A (en) * | 2015-11-27 | 2016-03-16 | 南京威安新材料科技有限公司 | Cleaning device for denitration catalyst regeneration |
-
1982
- 1982-10-01 JP JP57170934A patent/JPS5962329A/en active Granted
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS61132036U (en) * | 1985-02-04 | 1986-08-18 | ||
| CN104707482A (en) * | 2015-03-19 | 2015-06-17 | 南京宇行环保科技有限公司 | Regeneration method of deactivated catalyst |
| CN105396627A (en) * | 2015-11-27 | 2016-03-16 | 南京威安新材料科技有限公司 | Cleaning device for denitration catalyst regeneration |
| CN105396627B (en) * | 2015-11-27 | 2018-05-22 | 安徽博蓝德环保科技发展有限公司 | Denitrating catalyst regeneration washing device |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0148053B2 (en) | 1989-10-17 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| JP2000514351A (en) | Method for cleaning and / or regenerating a totally or partially deactivated flue gas denitrification catalyst | |
| CN103977845B (en) | SCR catalyst regenerative system and method | |
| CN108568186A (en) | A kind of high temperature fume purification device | |
| JPS5962329A (en) | Catalyst regeneration method | |
| CN207056230U (en) | Electrostatic dry two level exhaust treatment system | |
| CN208493681U (en) | A kind of high temperature fume purification device | |
| JPS6347506B2 (en) | ||
| CN106215696A (en) | Coke oven flue gas SCR denitrification catalyst blockage prevention and blockage removal method and device | |
| JP3792290B2 (en) | Smoke exhaust treatment method and apparatus | |
| CN112807933B (en) | A kind of environmental protection purification equipment | |
| CN215996121U (en) | A purification device for waste gas in foundry industry | |
| CN217068371U (en) | Waste gas purification tower for smelting rare earth ore | |
| CN213968252U (en) | SBS coiled material pollutant processing apparatus | |
| CN210951363U (en) | Hot water denitration boiler | |
| WO1980000168A1 (en) | Device for purifying exhaust gas of diesel engine | |
| CN105935530A (en) | Steel belted reducing furnace tail gas recovering system | |
| CN221324519U (en) | High-efficient dust removal structure of garbage incinerator | |
| CN213078006U (en) | A waste incineration tail gas treatment device | |
| CN208852569U (en) | A kind of bag filter for rubbish exhaust-gas treatment | |
| CN108856079B (en) | Device for rapidly cleaning scale of smoke cooler | |
| CN210874836U (en) | A complete set of waste gas treatment device | |
| CN216537639U (en) | Full-automatic integrated waste gas treatment equipment | |
| CN217604708U (en) | Bag type dust removal device for treating flue gas of paint removal furnace | |
| CN106563339A (en) | Dry and wet dual-use flue gas purification equipment for organic flue gas | |
| CN120714431B (en) | Waste gas purification device for hot galvanizing production line |