JPS6261647A - Method for regenerating denitration catalyst - Google Patents

Method for regenerating denitration catalyst

Info

Publication number
JPS6261647A
JPS6261647A JP19934785A JP19934785A JPS6261647A JP S6261647 A JPS6261647 A JP S6261647A JP 19934785 A JP19934785 A JP 19934785A JP 19934785 A JP19934785 A JP 19934785A JP S6261647 A JPS6261647 A JP S6261647A
Authority
JP
Japan
Prior art keywords
catalyst
water
container
treatment
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.)
Pending
Application number
JP19934785A
Other languages
Japanese (ja)
Inventor
Yoshiaki Obayashi
良昭 尾林
Shigeaki Mitsuoka
光岡 薫明
Tsuneo Nagano
永野 常雄
Hideaki Aizawa
相沢 秀明
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.)
Ryomei Engineering Co Ltd
Mitsubishi Heavy Industries Ltd
Original Assignee
Ryomei Engineering Co Ltd
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 Ryomei Engineering Co Ltd, Mitsubishi Heavy Industries Ltd filed Critical Ryomei Engineering Co Ltd
Priority to JP19934785A priority Critical patent/JPS6261647A/en
Publication of JPS6261647A publication Critical patent/JPS6261647A/en
Pending legal-status Critical Current

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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

PURPOSE:To enhance the regeneration effect of the denitration catalyst for a garbage incinerator, by removing the surface of the part contacted with gas to be treated of an ammonia catalytic reducing denitration catalyst lowered in its catalytic activity by abrasion and subsequently washing the abraded surface with water. CONSTITUTION:A columnar containe 1 such as a drum, from which a lid 3 was removed, is packed with an ammonia catalytic reducing denitration pellet catalyst (containing 89wt% of TiO2 and 11wt% of V2O5 and having a diameter of 4-6mmphi) lowered in its activity so as to occupy 40-60% of the volume of said container 1 and the lid 3 is subsequently applied to the container 1. The container 1 is then rotated at 60rpm for about 60min to contact catalyst particles with each other to abrade the surfaces of said catalyst particles, and, after the abrading treatment, the catalyst particles are immersed in water 8 times by volume of the catalyst for about 60min while stirring is performed occasionally. If this method is adapted to the denitration catalyst for an urban garbage incinerator, the regeneration effect is markedly displayed.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は排煙脱硝装置に適用されているペレット状(粒
状1円柱状)触媒の再生方法に関する。
DETAILED DESCRIPTION OF THE INVENTION [Industrial Field of Application] The present invention relates to a method for regenerating a pellet-like (granular, cylindrical) catalyst applied to a flue gas denitrification device.

〔従来の技術〕[Conventional technology]

燃焼排ガス中の窒素酸化物の除去方法として、アンモニ
ア金還元剤に用い、触媒によって還元するアンモニア接
触還元方式が広く採用されている。
As a method for removing nitrogen oxides from combustion exhaust gas, an ammonia catalytic reduction method in which ammonia is used as a gold reducing agent and reduced by a catalyst is widely used.

これら窒素酸化物除去用のアンモニア接触還元脱硝触媒
(以下、脱硝触媒又は単に触媒と記す)は、燃焼排ガス
中での便用時に徐々に性能の低下をき九すため、高い脱
硝性能を維持するためには、触媒の交換または性能低下
した触媒の再生賦活が必要となる。
These ammonia catalytic reduction denitrification catalysts (hereinafter referred to as denitrification catalysts or simply catalysts) for removing nitrogen oxides maintain high denitrification performance because their performance gradually decreases when used in combustion exhaust gas. For this purpose, it is necessary to replace the catalyst or reactivate the catalyst whose performance has deteriorated.

しかし、性能低下した触媒を新触媒に交換することは触
媒が高価で、使用済触媒の廃棄にも費用t−要すことか
ら経済的に不利である。したがって、性能低下した触媒
は再生賦活させ再使用することが有利である。
However, replacing a catalyst whose performance has deteriorated with a new catalyst is economically disadvantageous because the catalyst is expensive and disposal of the used catalyst also costs t-. Therefore, it is advantageous to reactivate and reuse a catalyst whose performance has deteriorated.

ペレット触媒はLNG焚き排ガスや都市ごみ焼却炉用ボ
イラーに適用されており、発明者らは、後者の場合、触
媒表層へのシリカ、鉄、アルミニウム、カルシウム、マ
グネシウム、ナトリウム及びカリウム等の化合物の付着
と触媒内部へのナトリウム、カリウムなどのアルカリ成
分の触媒への蓄積が原因で性能が低下することをつきと
め九。通常の重油焚きボイラ排ガスに適用し、性能が低
下した触媒は水による洗浄(水洗処理)によって、触媒
に蓄積したす) IJウム及びカリウム等のアルカリ成
分を溶出することにより再生が可能である。しかし都市
ゴミ焼却用ボイラ排ガス中のダスト成分は通常の重油焚
きボイラ排ガス中の主成分(80〜? Ovtl )が
未燃カーボンであるのとは異なシ、81.Pa。
Pellet catalysts are applied to boilers for LNG-fired exhaust gas and municipal waste incinerators, and the inventors have found that in the latter case, compounds such as silica, iron, aluminum, calcium, magnesium, sodium, and potassium adhere to the catalyst surface. It was discovered that the performance deteriorated due to the accumulation of alkaline components such as sodium and potassium inside the catalyst. When applied to normal heavy oil-fired boiler exhaust gas, catalysts whose performance has deteriorated can be regenerated by washing with water (water washing treatment) to elute alkaline components such as IJum and potassium that have accumulated on the catalyst. However, the dust component in the exhaust gas from municipal waste incineration boilers is different from the main component (80~? Ovtl) in the exhaust gas from ordinary heavy oil-fired boilers, which is unburned carbon. Pa.

ムL、 OA、 Mg、 Zn、 Ma、 K  等の
元素が塩化物、硫酸塩、リン酸塩、陵化物などの形態で
存在してお9、これらの化合物の中には水にJllll
l性で触媒表面に固着している物質もあり、これt水洗
処理だけで除去するには多量の水金必要とし、かつ困難
である。以上のことから単に水洗処理だけでは満足の−
<回復率が得られない。ま九本洗処理に多量の水上使用
すれば、当然排水処理の問題をも起ってくる。
Elements such as MuL, OA, Mg, Zn, Ma, and K exist in the form of chlorides, sulfates, phosphates, and compounds9, and some of these compounds are
Some substances adhere to the surface of the catalyst due to their properties, and it is difficult and requires a large amount of water to remove them only by washing with water. For the above reasons, simply washing with water is not enough.
<Recovery rate cannot be obtained. If a large amount of water is used for water washing, problems with wastewater treatment will naturally arise.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

都市ゴミ焼却炉排ガスに適用した触媒の性能低下厘因は
通常の重油焚きボイラ排ガスに適用した触媒のようにナ
トリウム及びカリウム等のアルカリ成分の触媒への蓄積
のみでなく、触媒表面へ固着した水に難溶性の物質も関
与しているため、単に水洗するだけでは満足のいく回復
率は得られない。
The reason for the performance deterioration of catalysts applied to exhaust gas from municipal waste incinerators is not only the accumulation of alkaline components such as sodium and potassium on the catalyst, as in the case of catalysts applied to ordinary heavy oil-fired boiler exhaust gas, but also water adhering to the catalyst surface. Because poorly soluble substances are also involved, a satisfactory recovery rate cannot be obtained simply by washing with water.

本発明は、この種性能低下した脱硝触媒の満足のいく再
生方法を提供しようとするものである。
The present invention seeks to provide a satisfactory method for regenerating such degraded denitrification catalysts.

〔問題点を解決する九めの手段〕[Ninth way to solve the problem]

本発明は、性能低下をきたしたアンモニア接触還元脱硝
触媒の被処理ガスか接触する部分の表層を摩耗削除した
後、水洗することを特徴とする脱硝触媒の再生方法であ
る。
The present invention is a method for regenerating a denitrification catalyst, which is characterized in that the surface layer of the ammonia catalytic reduction denitrification catalyst that has deteriorated in performance is washed with water after abrasion is removed from the surface layer of the part of the catalyst that comes into contact with the gas to be treated.

〔作用〕[Effect]

本発明は性能低下し几ペレット状脱硝触媒のごく表面を
摩耗させ、表面に固着し次シリカ、鉄、アルミニウム、
カルシウム、マグネシウム、ナトリウム、カリウム等の
ダスト成分を除去し14)、新たな触媒面を露出させる
ことにニジ、触媒の水洗効果を高めるものである。
In the present invention, the performance deteriorates and the very surface of the pellet-like denitrification catalyst is worn out, and then silica, iron, aluminum, etc.
It removes dust components such as calcium, magnesium, sodium, and potassium (14) and exposes a new catalyst surface, thereby increasing the effectiveness of washing the catalyst with water.

発明者らは触媒に蓄積する成分の化合物の形11 F1
a 10x e ICt Ss Os e M a 0
4 K O4Ca COs及びOa 804であること
がX線回折分析より確認され、これらは触媒の極表面に
集中していることをつきとめ九。
The inventors discovered the compound form 11 F1 of the component that accumulates in the catalyst.
a 10x e ICt Ss Os e M a 0
4K O4Ca COs and Oa 804 were confirmed by X-ray diffraction analysis, and they were found to be concentrated on the extreme surface of the catalyst9.

これらの表面付着物を摩耗処理によって除去し、そのあ
と水洗処理金施こすことで一層大きな回復率が得られる
A greater recovery rate can be obtained by removing these surface deposits by abrasion treatment and then applying water washing treatment.

また摩耗処理の後、水洗処理を施こすことで排水処理1
檻も軽減できるという特徴もある。
In addition, after the abrasion treatment, water washing treatment is performed to perform wastewater treatment 1.
Another feature is that cages can be reduced.

〔実施例〕〔Example〕

初期のMox除去除去板下、脱硝軍と記す)810sの
ペレット状脱硝触媒を都市ごみ焼却炉排ガス中で約11
000時間充填させ九ところ、脱硝′Sが310−まで
低下し九。
Under the initial Mox removal removal plate, 810s of pelleted denitrification catalyst (described as denitrification force) was used in the exhaust gas of a municipal waste incinerator.
After 9,000 hours of filling, the denitrification value decreased to 310-.

性能低下した同触媒を下記に示す2つの方法でそれぞれ
摩耗処理と水洗処理を行ない性能評価し九。ま九単に水
洗処理だけの性能評価本行なった。
The same catalyst with degraded performance was subjected to abrasion treatment and water washing treatment using the two methods shown below, respectively, and its performance was evaluated. We conducted a performance evaluation using only water washing treatment.

なお、本触媒の岨成はrio!89 vt%%−へ11
 Wt4jで触媒直径は4〜6謹φである。
Furthermore, the author of this catalyst is rio! 89 vt%%-to11
In Wt4j, the catalyst diameter is 4 to 6 mm.

摩耗処理は下記の方法で行なった。Wear treatment was carried out in the following manner.

(1)  第1図に示すように、ドラム缶等の円柱状の
容器1に性能低下したペレット触媒2を容器1のふた3
″Ikとって4〜6分目光填し、ふた3をした後、その
容器1を回転させ触媒間の接触により触媒表面全摩耗さ
せる。回転数は60 rpmで60分回転させた。
(1) As shown in FIG.
After taking ``Ik'' and filling with light for 4 to 6 minutes, and closing the lid 3, the container 1 was rotated to completely abrade the catalyst surface by contact between the catalysts.The rotation speed was 60 rpm and the container was rotated for 60 minutes.

この摩耗処理の後、触媒容量の8倍量の水に触媒金時々
攪拌しながら、60分間浸漬し九〇 (2)  第2図に示すように、円柱状容器9、そのふ
た4および円柱状の網5からなる容器に、ペレット触媒
7を円柱状の網5に4〜6分目充填し、網5のふた6を
し、さらにそれを円柱状容器9に入れる。
After this abrasion treatment, the catalyst gold was immersed in water of 8 times the volume of the catalyst for 60 minutes with occasional stirring. A container consisting of a cylindrical mesh 5 is filled with pellet catalyst 7 for 4 to 6 minutes, the lid 6 of the mesh 5 is put on, and the pellet is placed in a cylindrical container 9.

前記同様、これ1回転させ触媒を摩耗させるが、円柱状
の網5には浮かし盤8が付いており摩耗した触媒粉は触
媒間に残ることなく、後処理が便利なようにしである。
As before, the catalyst is rotated once to wear it out, but the cylindrical net 5 is equipped with a floating plate 8 so that the worn catalyst powder does not remain between the catalysts, making post-treatment convenient.

これも回転数6゜rpmで60分回転させた後、上記(
1)と同条件の水洗処理を施こした。
This was also rotated for 60 minutes at a rotation speed of 6° rpm, and then the above (
A water washing treatment was performed under the same conditions as in 1).

水洗処理だけの触媒は水洗→評価の工程を3回繰り返し
た。その水洗条件は上記同様である。
For catalysts that were only washed with water, the process of water washing and evaluation was repeated three times. The washing conditions are the same as above.

以上、そn−t’;rtの触媒の性Ut評価し、処理前
の性能と比較した・ 触媒評価にあたっては実機での触媒充填条件と同じ温度
、ガス組成上つくれる小型触媒評価装置上使用し九〇 その条件を表−1に示す。
As described above, we evaluated the performance of the catalyst at n-t';rt and compared it with the performance before treatment.In order to evaluate the catalyst, we used it on a small catalyst evaluation device that can be made at the same temperature and gas composition as the catalyst filling conditions in the actual device. 90 The conditions are shown in Table-1.

表  −1 触媒評価結果は表−2に示すが、ここで回復本とは新触
媒の脱硝幕:FI7  再生処理後の脱硝幕:R?、再
生処理前の脱硝幕t)+7とすると((RワーUη)/
CF+7−11117))X1GoC引で表わされるも
のとする。
Table 1 Catalyst evaluation results are shown in Table 2. Here, the recovered catalyst refers to the denitrification curtain of the new catalyst: FI7 The denitration curtain after regeneration treatment: R? , if the denitrification curtain t)+7 before the regeneration process, then ((R wa Uη)/
CF+7-11117))

表  −2 水洗II&塩のみの再生では、1回目の水洗後圓復幕が
3翫5チで、以下2回目の水洗後は、閂atos%3E
m目で同s’host示シタ。
Table-2 In the case of water washing II & salt only regeneration, after the first water washing, the round return is 3 and 5 chi, and after the second water washing, the bolt is atos%3E.
The same s'host is shown on the mth page.

lE1図及び第2図01!器による摩耗処理の後それぞ
れ水洗処理を施こすと回復率5cLo*、5tost示
した。
Figure lE1 and Figure 2 01! After the abrasion treatment with the equipment, water washing treatment was performed, and the recovery rate was 5cLo* and 5tost.

こO結果により摩耗処理は、2@の水洗による性wAl
r!l復能力に匹敵、又はそれ以上の効果があり、そO
分回復処理工程中排水処理工程tS楓で暑ることが立証
された。
Based on this result, wear treatment was performed by washing with water at 2
r! It has an effect equal to or greater than the ability to restore
During the minute recovery treatment process, the wastewater treatment process was proven to be hot in the tS maple.

なお、第1図の処理、第2図の処理で触媒表層の摩耗は
触媒重量、触媒密度等から計算してそれぞれ40 pm
、 70μmであった。
In addition, the abrasion of the catalyst surface layer in the process shown in Figure 1 and the process shown in Figure 2 is 40 pm, calculated from the catalyst weight, catalyst density, etc.
, 70 μm.

〔発明の効果〕〔Effect of the invention〕

性能の低下し之ペレット触媒の水洗再生を施こすにあた
っては、まず摩耗処理を行ない、水洗処理を実施した方
が再生効果が大きい。
When regenerating a pellet catalyst whose performance has deteriorated by washing with water, the regeneration effect will be greater if the abrasion treatment is first performed and then the water washing treatment is performed.

これを都市ごみ焼却炉用脱硝触媒に適用すると効果が顕
著に表われた・ また水洗の際の排水処理工程も軽減できる。
When this was applied to a denitrification catalyst for municipal waste incinerators, the effect was noticeable. It also reduced the wastewater treatment process during washing.

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

第1図及び第2図は、本発明の摩耗処理に使用した容器
を示す図である。 復代理人  内 1)  明 復代理人  萩 原 亮 − 復代理人  安 西 篤 夫 第1図
FIGS. 1 and 2 are diagrams showing a container used for the abrasion treatment of the present invention. Sub-Agents 1) Meifuku Agent Ryo Hagiwara - Sub-Agent Atsuo Anzai Figure 1

Claims (1)

【特許請求の範囲】[Claims] 性能低下をきたしたアンモニア接触還元脱硝触媒の被処
理ガスが接触する部分の表層を摩耗削除した後、水洗す
ることを特徴とする脱硝触媒の再生方法。
A method for regenerating a denitrification catalyst, which comprises abrading and removing the surface layer of the part of the ammonia catalytic reduction denitrification catalyst that comes into contact with the gas to be treated, which has deteriorated in performance, and then washing the catalyst with water.
JP19934785A 1985-09-11 1985-09-11 Method for regenerating denitration catalyst Pending JPS6261647A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP19934785A JPS6261647A (en) 1985-09-11 1985-09-11 Method for regenerating denitration catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP19934785A JPS6261647A (en) 1985-09-11 1985-09-11 Method for regenerating denitration catalyst

Publications (1)

Publication Number Publication Date
JPS6261647A true JPS6261647A (en) 1987-03-18

Family

ID=16406253

Family Applications (1)

Application Number Title Priority Date Filing Date
JP19934785A Pending JPS6261647A (en) 1985-09-11 1985-09-11 Method for regenerating denitration catalyst

Country Status (1)

Country Link
JP (1) JPS6261647A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04117277U (en) * 1991-03-29 1992-10-20 アイシン精機株式会社 Retaining structure for strainer structure installed in fluid passage
KR20040042667A (en) * 2002-11-15 2004-05-20 유정근 Method for recycling waste de-NOx catalyst
WO2006084872A2 (en) * 2005-02-09 2006-08-17 Basf Aktiengesellschaft Method for regenerating inert carrier material of deactivated oxidation catalysts and corresponding device
JP4704352B2 (en) * 2004-10-06 2011-06-15 理恵 臼井 Flyer
JP2011161373A (en) * 2010-02-09 2011-08-25 Chugoku Electric Power Co Inc:The Method for regenerating denitration catalyst
KR20190082259A (en) 2016-12-15 2019-07-09 미츠비시 히타치 파워 시스템즈 가부시키가이샤 Method for regenerating used denitration catalyst

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04117277U (en) * 1991-03-29 1992-10-20 アイシン精機株式会社 Retaining structure for strainer structure installed in fluid passage
JP2570567Y2 (en) * 1991-03-29 1998-05-06 アイシン精機株式会社 Structure for holding a strainer structure disposed in a fluid passage
KR20040042667A (en) * 2002-11-15 2004-05-20 유정근 Method for recycling waste de-NOx catalyst
JP4704352B2 (en) * 2004-10-06 2011-06-15 理恵 臼井 Flyer
WO2006084872A2 (en) * 2005-02-09 2006-08-17 Basf Aktiengesellschaft Method for regenerating inert carrier material of deactivated oxidation catalysts and corresponding device
WO2006084872A3 (en) * 2005-02-09 2006-12-07 Basf Ag Method for regenerating inert carrier material of deactivated oxidation catalysts and corresponding device
JP2011161373A (en) * 2010-02-09 2011-08-25 Chugoku Electric Power Co Inc:The Method for regenerating denitration catalyst
KR20190082259A (en) 2016-12-15 2019-07-09 미츠비시 히타치 파워 시스템즈 가부시키가이샤 Method for regenerating used denitration catalyst

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