JPS63134057A - Production of catalyst for denitrification of flue gas - Google Patents

Production of catalyst for denitrification of flue gas

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Publication number
JPS63134057A
JPS63134057A JP61280856A JP28085686A JPS63134057A JP S63134057 A JPS63134057 A JP S63134057A JP 61280856 A JP61280856 A JP 61280856A JP 28085686 A JP28085686 A JP 28085686A JP S63134057 A JPS63134057 A JP S63134057A
Authority
JP
Japan
Prior art keywords
catalyst
denitrification
surface layer
reaction
supported
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
Application number
JP61280856A
Other languages
Japanese (ja)
Other versions
JPH0640957B2 (en
Inventor
Shigeru Nojima
繁 野島
Kozo Iida
耕三 飯田
Toru Seto
徹 瀬戸
Shigeaki Mitsuoka
光岡 薫明
Yoshiaki Obayashi
良昭 尾林
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
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Filing date
Publication date
Application filed by Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP61280856A priority Critical patent/JPH0640957B2/en
Publication of JPS63134057A publication Critical patent/JPS63134057A/en
Publication of JPH0640957B2 publication Critical patent/JPH0640957B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Abstract

PURPOSE:To improve denitrification activity and to permit suppression of said reaction as well by depositing a vanadium compd. which is an active metal component into a catalyst carrier surface layer at a high concn. within 200mum of the surface layer. CONSTITUTION:V2O5 which is a main active component is thinly and uniformly deposited, within 200mum from the catalyst surface layer, on the V2O5/TiO2 denitrification catalyst which reduces the NOx in the exhaust gas contg. NOx by adding ammonia to acid exhaust gas so as to provide the pollution-free gas. High concn. V2O5 is eventually incorporated within 200mum of the catalyst surface and the content in the bulk is correspondingly decreased. The initial activity of the denitrification reaction is thereby improved and the activity against catalyst poisoning is maintained as well, by which the durability is improved and the side reaction is suppressed.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は電力用大型ボイラ等の燃焼炉等から排ガス中の
窒素酸化物除去に適用される触媒の製造方法に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method for producing a catalyst that is applied to remove nitrogen oxides from exhaust gas from combustion furnaces such as large power boilers.

〔従来の技術〕[Conventional technology]

排ガス脱硝触媒としては、隈化チタンやアルミナなどを
担体として、それらにバナジウム、タングステン、鉄、
銅などの活性金Sを担持したものが知られている。しか
しこれらの触媒は従来、各種活性金属塩の水溶液あるい
は有機溶媒に溶解した溶液をペレット形状、ハニカム形
状に成型した担体に含浸あるいは混練する方法、または
粉末状の担体に溶液を含浸あるいは混練した後、ベレッ
ト形状、ハニカム形状に成型する方法によって製造され
ている。
As an exhaust gas denitrification catalyst, vanadium, tungsten, iron,
Those supporting activated gold S such as copper are known. However, these catalysts have conventionally been produced by impregnating or kneading a solution of various active metal salts dissolved in an aqueous or organic solvent into a pellet-shaped or honeycomb-shaped carrier, or by impregnating or kneading a solution into a powdered carrier. It is manufactured by molding into a pellet shape or a honeycomb shape.

とりわけ、17205−No、−T102系脱硝触媒は
排ガス中の脱硝作用(4NO+ 4Nl(3+02−+
 4N2+6H20) t−促進し、一方副反応である
SOxの酸化反応やアンモニアの分解反応等を抑制する
など、高性能な排煙脱硝触媒として使われている。通常
、担体に担持するv205′Ikは0.I wt%〜5
.Owt%wo、量は3 wt%〜20 wt%が広く
適用されている。ただし、v205  量を増加させる
ことにより脱硝活性が向上するが、Soxの酸化力も激
しくなるため上記担持範囲にv205  量が限定され
ている。
In particular, the 17205-No and -T102 denitrification catalysts have a denitration effect in exhaust gas (4NO+ 4Nl(3+02-+
4N2+6H20) It is used as a high-performance exhaust gas denitrification catalyst, promoting t- while suppressing side reactions such as SOx oxidation reaction and ammonia decomposition reaction. Usually, the v205'Ik supported on the carrier is 0. I wt%~5
.. Owt%wo, the amount is widely applied from 3 wt% to 20 wt%. However, although increasing the amount of v205 improves the denitrification activity, the oxidizing power of Sox also increases, so the amount of v205 is limited to the above supported range.

しかし、脱硝活性を向上させようとするとSOxの酸化
能が顕著となジ、さらに、ボイラー原料燃料種によって
は、排ガス中に砒素化合物等の触媒被毒物質が存在する
場合があり、触媒への堆積により、細孔の閉塞や触媒活
性点の消失が生じ、触媒活性が急速に低下する欠点があ
る。
However, when trying to improve the denitrification activity, the oxidation ability of SOx becomes significant.Furthermore, depending on the type of boiler feedstock fuel, catalyst poisoning substances such as arsenic compounds may be present in the exhaust gas, which may cause damage to the catalyst. The deposition causes the clogging of pores and the disappearance of catalytic active sites, which has the drawback of rapidly reducing the catalytic activity.

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

本発明は従来の排煙脱硝触媒の欠点を解消し脱硝反応の
初期活性を向上させ被毒物質が触媒に堆積後も触媒活性
を維持する耐久性を有し、Soxの酸化等の副反応を抑
制する排煙脱硝触媒を製造する方法を提供しようとする
ものである。
The present invention eliminates the drawbacks of conventional exhaust gas denitrification catalysts, improves the initial activity of the denitrification reaction, has the durability to maintain catalytic activity even after poisonous substances are deposited on the catalyst, and prevents side reactions such as Sox oxidation. The present invention aims to provide a method for manufacturing a flue gas denitrification catalyst that suppresses exhaust gas denitrification.

〔問題点を解決する念めの手段〕[A precautionary measure to resolve the problem]

本発明は、窒素酸化物を含有する排ガスにアンモニア全
添加して、排ガス中の窒素醸化物を還元無害化するVO
/TLO2系脱硝触媒の製造方法において、触媒担体表
面層に活性金属化合物であるバナジウム化合物を表面層
200趨以内に高濃度で担持することを特徴とする排煙
脱硝触媒の製造方法である。
The present invention is a VO system that completely adds ammonia to exhaust gas containing nitrogen oxides to reduce and render harmless nitrogen compounds in the exhaust gas.
/TLO2-based denitrification catalyst manufacturing method, which is characterized in that a vanadium compound, which is an active metal compound, is supported on the catalyst carrier surface layer at a high concentration within 200 nm of the surface layer.

本発明者らはv2o5−wo3−’r1o2糸触媒にて
脱硝反応(4NO+ 4NH3→4N2+6H20)と
802の酸化反応(2S02+02→2So5)ノ反応
速[−比較検討したところ、脱硝反応の方が段然、反応
が速いことを見い出し念。そして、ハニカム形状の触媒
では、脱硝反応は触媒表面層だけで十分反応が進行し、
一方、S02の酸化反応は触媒のバルク内部まで反応に
関与していることがわかった。
The present inventors compared the reaction rates of the denitrification reaction (4NO+ 4NH3 → 4N2 + 6H20) and the 802 oxidation reaction (2S02 + 02 → 2So5) using a v2o5-wo3-'r1o2 thread catalyst, and found that the denitrification reaction is significantly better. , I found that the reaction was fast. In addition, with a honeycomb-shaped catalyst, the denitrification reaction progresses sufficiently only in the catalyst surface layer.
On the other hand, it was found that the oxidation reaction of S02 involves the reaction even inside the bulk of the catalyst.

それゆえに、脱硝活性を向上させ、副反応を今までのま
まに抑えた触媒を調製するために触媒の表面層に主要な
活性成分であるv205  を薄く均一に担持させれば
良いことを見い出した。
Therefore, we discovered that in order to improve the denitrification activity and prepare a catalyst that suppresses side reactions, it is sufficient to uniformly support v205, the main active ingredient, on the surface layer of the catalyst. .

とりわけ、表面層200μm以内にv2o5’2高濃度
で担持することが好ましい。また表面層に均一に薄<v
205t−担持する手法としては気相蒸着法(CVO法
)を応用することができる。
In particular, it is preferable to support v2o5'2 at a high concentration within 200 μm of the surface layer. Also, the surface layer is uniformly thin <v
As a method for supporting 205t, a vapor phase evaporation method (CVO method) can be applied.

T工02担体とWoo/、  との反応は次のように進
行する。なお、担体表面の酸素は水素を結合しており、
酸性点の役割をする。
The reaction between the T-02 carrier and Woo/, proceeds as follows. Note that oxygen on the surface of the carrier is bonded to hydrogen,
Acts as an acidic point.

HC1−V−C1 この反応生成物中のC/  等は触媒被毒物質となる可
能性があるために焼成により除去するか、o     
   o                    o
HC1-V-C1 Since C/ etc. in this reaction product may become catalyst poisoning substances, they should be removed by calcination or o
o o
.

+l         It            
         II    賀加水分解により除去
する。
+l It
II. Remove by hydrolysis.

II                      1
CI!−1/−0/               H
O−V−OHこのように、表面層に担持されたv205
  は全て活性体としての機能を有し、その結果、少量
のv2o5’2表面層に薄く担持させるだけで十分な脱
硝活性を確保することができ、副反応の抑制も可能とじ
九。
II 1
CI! -1/-0/H
O-V-OH Thus, v205 supported on the surface layer
All have functions as activators, and as a result, sufficient denitrification activity can be ensured by simply supporting a small amount of v2o5'2 in a thin layer on the surface layer, and side reactions can also be suppressed.

〔作用〕[Effect]

本発明の気相担持法(CVO法)によってバナジウムを
ハニカム形状、ペレット形状の担体の表面層に200μ
1以内に高濃度で担持した触媒は従来の含浸法による担
体のバルク内部にまで担持した触媒に比べ、SOxの酸
化能はほとんど変わらなく低く抑えたままであるが、脱
硝作用は大幅に向上する。
By the gas phase loading method (CVO method) of the present invention, vanadium is applied to the surface layer of a honeycomb-shaped or pellet-shaped carrier with a thickness of 200 μm.
Compared to a catalyst supported in the bulk of the carrier by the conventional impregnation method, a catalyst supported at a high concentration within 1% has almost no change in SOx oxidation ability and remains low, but the denitrification effect is significantly improved.

本発明の触媒調製法ではタングステンの担持法は通常の
含浸法により行われ、パラタングステンアンそニウム水
溶液等を所定濃度に調節し担体を溶液中に浸漬した後乾
燥、焼成する。一方、気相担持するバナジウム化合物は
常温にて液体物質であるVOOI、 、 VCl2. 
VOBr3  また固体状態のVO/、、VC!、、V
OOJP2.VBr3  等が挙げられ、いずれも気相
状態にて担体に接触させてVを表面層に担持する。
In the catalyst preparation method of the present invention, tungsten is supported by a conventional impregnation method, in which an aqueous solution of paratungsten amsonium or the like is adjusted to a predetermined concentration, and the carrier is immersed in the solution, then dried and calcined. On the other hand, the vanadium compounds supported in the gas phase are VOOI, , VCl2., which are liquid substances at room temperature.
VOBr3 Also solid state VO/,,VC! ,,V
OOJP2. Examples include VBr3, and all of them are brought into contact with a carrier in a gas phase to support V on the surface layer.

担体は100Cないし800Cの範囲内の温度、好まし
くは150Cないし700Cの温度にて気相バナジウム
化合物を反応せしめ表面層にバナジウムを担持すること
が望ましい。
It is preferable that the carrier is reacted with a vapor phase vanadium compound at a temperature in the range of 100C to 800C, preferably 150C to 700C, so that vanadium is supported on the surface layer.

以下に本発明を実施例により詳しく説明する。The present invention will be explained in detail below using examples.

〔実施例1〕 T10 換算濃度15%のTz0804水溶液1500
.9t−20C以下に冷却し、15Xアンモニア水を徐
々に加えてずを8にして中和する。虫取する水散化チタ
ン沈殿物を濾過し、戸液に802−イオンが検出されな
くなるまで水洗する。乾燥後、500Cで3時間空気中
で焼成し、約200gの酸化チタン粉末を得之。
[Example 1] Tz0804 aqueous solution with T10 equivalent concentration of 15% 1500
.. Cool to below 9t-20C and neutralize by gradually adding 15X ammonia water to a concentration of 8. The water-dispersed titanium precipitate to be used for insect removal is filtered and washed with water until no 802- ions are detected in the solution. After drying, it was calcined in air at 500C for 3 hours to obtain about 200g of titanium oxide powder.

この酸化チタン80重量部に散性白土15重量部、グラ
ス7アイパ一5重量部を加え、水を加えて混線機によっ
てよく混合し念後、適当な水分とした後、ハニカム成型
機にて、穴の形状を正方形とし、目開き60m111壁
厚1.35flのハニカム状に成型した。乾燥後500
Cで3時間焼成し九。このハニカム担体を担体1とする
To 80 parts by weight of this titanium oxide, 15 parts by weight of dispersible clay and 5 parts by weight of Glass 7 IPA were added, and water was added and mixed thoroughly using a mixer to obtain an appropriate moisture content, and then using a honeycomb forming machine. The holes were square in shape and formed into a honeycomb shape with an opening of 60 m and a wall thickness of 1.35 fl. 500 after drying
Bake at C for 3 hours.9. This honeycomb carrier will be referred to as carrier 1.

このハニカム担体1の飽和含水量を測定した後、WO5
の重量部で担体1に対して10 wt%担持されるよう
に、パラタングステンアンモニウム水溶液に担体1を浸
漬し、乾燥後500C,3時間焼成した。次に、このW
O3−T10□ 試料を400C一定の反応炉中に置き
、常温にて液体状バナジウム化合物であるvoat3に
N2  キャリア−ガスt−40i1j/分で吹き込み
、生じ念VOCI、蒸気を炉中に20分間供給した。さ
らに、反応炉から触媒を取り出し、空気中で50(Ic
、3時間焼成し、得られた触媒^の表面層200μm以
内のT205 担持量は0.95 wtXであり、バル
ク内部のV2O5担持量は0.32 wtXであった。
After measuring the saturated water content of this honeycomb carrier 1, WO5
The carrier 1 was immersed in an aqueous paratungsten ammonium solution so that 10 wt % of the paratungsten ammonium was supported on the carrier 1, and after drying, it was fired at 500 C for 3 hours. Next, this W
O3-T10□ The sample was placed in a reactor at a constant temperature of 400C, and N2 carrier gas was blown into the liquid vanadium compound voat3 at room temperature at a rate of t-40i1j/min. did. Furthermore, the catalyst was taken out from the reactor and 50 (Ic
The amount of T205 supported within 200 μm of the surface layer of the obtained catalyst^ was 0.95 wtX, and the amount of V2O5 supported inside the bulk was 0.32 wtX.

〔実施例2〕 V原料としてVOBr3i用いた他は実施例1と同様の
方法で触媒を調製し、触媒Bt−得た。触媒Bの表面層
200μm以内のV2O5担持量は1.01 wtXで
あジバルク内部のT205 担持量は0.38 Xであ
った。
[Example 2] A catalyst was prepared in the same manner as in Example 1 except that VOBr3i was used as the V raw material to obtain a catalyst Bt-. The amount of V2O5 supported within 200 μm of the surface layer of catalyst B was 1.01 wtX, and the amount of T205 supported inside the dibulk was 0.38 wtX.

〔実施例3〕 V原料としてvat2 原料を用い、実施例1と同様の
方法で触媒を調製し、触媒aを得念。触媒Cの表面層2
00μm以内のV2O5担持量は0.89 wtXであ
りバルク内部のT205  担持量は0.56 wtX
であった。
[Example 3] Using the VAT2 raw material as the V raw material, a catalyst was prepared in the same manner as in Example 1, and catalyst a was prepared. Surface layer 2 of catalyst C
The amount of V2O5 supported within 00 μm is 0.89 wtX, and the amount of T205 supported inside the bulk is 0.56 wtX.
Met.

〔実施例4〕 ”100/、をV原料に用い、実施例1で示し九voc
t、蒸気処理10分間、および30分間行へ各々触媒o
、mt−得た。触媒o、gの表面層200 μn以内の
V2O5担持量は0.55 wtX。
[Example 4] "100/" was used as the V raw material, and 9 voc as shown in Example 1
t, steam treatment for 10 minutes, and catalyst o for 30 minutes, respectively.
, mt-obtained. The amount of V2O5 supported within 200 μn of the surface layer of catalysts o and g is 0.55 wtX.

1.35 wtXであり、バルク内部のT205 担持
量は0.22 wtX、0.45 wtXであった。ま
た、実施例1で示したvoat、蒸気処理を、wo、−
’rio2試料を500C一定の反応炉中く置いて供給
し触媒Fを得た。この触媒2の表面層200μm以内の
V2O5担持量は1.21 wtXであり、バルク内部
のV2O5担持量は0.29 wtXであった。
The amount of T205 supported inside the bulk was 0.22 wtX and 0.45 wtX. In addition, the voat and steam treatment shown in Example 1, wo, -
Catalyst F was obtained by placing and feeding the 'rio2 sample into a reactor at a constant temperature of 500C. The amount of V2O5 supported within 200 μm of the surface layer of this catalyst 2 was 1.21 wtX, and the amount of V2O5 supported inside the bulk was 0.29 wtX.

〔比較例1〕 実施例1と同様の手法で調製し九No3−Tie2試料
にメタバナジン駿アンモニウム水溶液ヲ含浸、乾燥50
0C,3時間焼成することにより、バルク内部のV2O
5担持量は0.4 wtX、  0.8wtX、2.O
wtXll 0 wtXの触媒a、b、o。
[Comparative Example 1] A sample of No. 3-Tie 2 prepared in the same manner as in Example 1 was impregnated with an aqueous ammonium solution of metavanazine and dried for 50 minutes.
By firing at 0C for 3 hours, V2O inside the bulk is removed.
5 The supported amount is 0.4 wtX, 0.8 wtX, 2. O
wtXll 0 wtX catalysts a, b, o.

dを得た。これらの触媒a% b、c、(1は200μ
1以内の表面層のV2O5担持量がバルク内部と同一で
あった。
I got d. These catalysts a% b, c, (1 is 200μ
The amount of V2O5 supported on the surface layer within 1 was the same as that inside the bulk.

〔比較例2〕 実施例1と同様の手法で調製したNo3−TIO2試料
を室温の反応炉に置いて、VOC/、 ’e N2  
キャリアーガスにより2ぶ7分で5分間吹き込んだ。そ
の後、触媒を反応炉から取出して空気中で500C,3
時間焼成した。得られ念触媒eのバルク内部及び200
μm以内の表面層V2O5担持量はともに0.95 w
tXであった。
[Comparative Example 2] A No3-TIO2 sample prepared in the same manner as in Example 1 was placed in a reactor at room temperature, and VOC/, 'e N2
The carrier gas was blown for 5 minutes at 2 to 7 minutes. After that, the catalyst was taken out from the reactor and heated at 500C, 3
Baked for an hour. The bulk interior of the obtained psychocatalyst e and 200
The amount of V2O5 supported on the surface layer within μm is both 0.95 w.
It was tX.

実施例1〜4で得た触媒に、B、O,O,K。B, O, O, K to the catalysts obtained in Examples 1 to 4.

Fと比較例1.2で得た触媒aSbSc、a。F and the catalyst aSbSc, a obtained in Comparative Example 1.2.

of表1に示す条件にて脱硝性能試験を行り九初期活性
及び5000時間使用後の試験結果を表2に示した。
A denitrification performance test was conducted under the conditions shown in Table 1, and the initial activity and test results after 5000 hours of use are shown in Table 2.

触媒活性試験 さらに、各調製触媒^、B、O,Dl ESFa、bS
 c、el、aに対して触媒の被毒物質である砒素酸化
物蒸気を含むガスを表3に示す条件にて5000時間処
理し、その処理後の触媒活性を測定し念。触媒活性試験
は表1の条件で行い、試験結果を表4に示す。
Catalytic activity test Furthermore, each prepared catalyst ^, B, O, Dl ESFa, bS
C, el, and a were treated with a gas containing arsenic oxide vapor, which is a catalyst poisoning substance, for 5000 hours under the conditions shown in Table 3, and the catalytic activity after the treatment was measured. The catalyst activity test was conducted under the conditions shown in Table 1, and the test results are shown in Table 4.

担体上に担持されたv205量のラインプロファイルを
求める之めに、触媒Oと触媒すの壁厚1.35mのハニ
カムについてX線マイクロアナライザーによ5vの分布
状態を分析した。その分布曲線を第1図に示す。横軸は
ハニカムの厚さ方向を示し、縦軸はVの含有量である。
In order to obtain the line profile of the amount of v205 supported on the carrier, the distribution state of 5v was analyzed using an X-ray microanalyzer for the catalyst O and the honeycomb with a wall thickness of 1.35 m. The distribution curve is shown in FIG. The horizontal axis indicates the thickness direction of the honeycomb, and the vertical axis indicates the V content.

(!L)は触媒CについてVの分布状態を示したもの、
200μm以内の表面層にv205が多量に結合してい
ることがわかる。一方、(b)は触媒すについてのもの
で、表面層とバルク内部でv205  の含有量に変化
がないことがわかる。
(!L) shows the distribution state of V for catalyst C,
It can be seen that a large amount of v205 is bound to the surface layer within 200 μm. On the other hand, (b) is for the catalyst, and it can be seen that there is no change in the content of v205 between the surface layer and the inside of the bulk.

表1、表3の結果から明らかなように気相担持法(cv
o法)により、v205t−触媒担体の表面層に均一に
薄く担持し念触媒(触媒A、B。
As is clear from the results in Tables 1 and 3, the gas phase loading method (cv
A thin catalyst (catalysts A and B) was uniformly and thinly supported on the surface layer of the v205t-catalyst carrier using the method.

0、D、ElF)は含浸法による従来法触媒(触媒a1
 b、c%d、e)に比べて明らかに初期活性が向上し
、A’a 20 s等の被毒物質堆積後においても脱硝
活性が維持でき、耐久性の向上を図ることができ、さら
に、Soxの酸化等の副反応を抑制した状態で脱硝反応
を行うことができることが明白となった。
0, D, ElF) are conventional catalysts (catalyst a1
Compared to b, c% d, e), the initial activity is clearly improved, the denitrification activity can be maintained even after the deposition of poisonous substances such as A'a 20 s, and the durability can be improved. It has become clear that the denitrification reaction can be carried out while suppressing side reactions such as oxidation of Sox.

〔発明の効果〕〔Effect of the invention〕

本発明は上記構成を採用することによp1触媒表面20
0μm以内に高濃度のv205を含有し、バルク内部の
含有Jl全低下させることにより、脱硝反応の初期活性
を向上させ、触媒被毒に対しても活性を維持し、耐久性
を向上させるとともに、副反応を抑制することを可能に
した。
By adopting the above configuration, the present invention provides p1 catalyst surface 20
By containing a high concentration of V205 within 0 μm and completely reducing the Jl content inside the bulk, it improves the initial activity of the denitrification reaction, maintains activity against catalyst poisoning, and improves durability. This made it possible to suppress side reactions.

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

第1図(al (blはハニカム触媒の断面方向におけ
るv205  含有量の分布状態を示した図で、(a)
は触媒Cについて+1))は触媒すについてのものであ
る。 表  1 表  2
Figure 1 (al) is a diagram showing the distribution of v205 content in the cross-sectional direction of the honeycomb catalyst; (a)
is for catalyst C +1)) is for catalyst S. Table 1 Table 2

Claims (1)

【特許請求の範囲】[Claims] 窒素酸化物を含有する排ガスにアンモニアを添加して、
排ガス中の窒素酸化物を還元無害化するV_2O_5/
TiO_2系脱硝触媒の製造方法において、触媒担体表
面層に活性金属化合物であるバナジウム化合物を表面層
200μm以内に高濃度で担持することを特徴とする排
煙脱硝触媒の製造方法。
By adding ammonia to exhaust gas containing nitrogen oxides,
V_2O_5/ which reduces nitrogen oxides in exhaust gas and makes them harmless
A method for producing a TiO_2-based denitrification catalyst, characterized in that a vanadium compound, which is an active metal compound, is supported on the catalyst carrier surface layer at a high concentration within 200 μm of the surface layer.
JP61280856A 1986-11-27 1986-11-27 Method for producing flue gas denitration catalyst Expired - Fee Related JPH0640957B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61280856A JPH0640957B2 (en) 1986-11-27 1986-11-27 Method for producing flue gas denitration catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61280856A JPH0640957B2 (en) 1986-11-27 1986-11-27 Method for producing flue gas denitration catalyst

Publications (2)

Publication Number Publication Date
JPS63134057A true JPS63134057A (en) 1988-06-06
JPH0640957B2 JPH0640957B2 (en) 1994-06-01

Family

ID=17630929

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61280856A Expired - Fee Related JPH0640957B2 (en) 1986-11-27 1986-11-27 Method for producing flue gas denitration catalyst

Country Status (1)

Country Link
JP (1) JPH0640957B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7256155B2 (en) 2003-03-14 2007-08-14 Mitsubishi Heavy Industries, Ltd. Flue gas denitration catalyst and preparation process thereof

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56168835A (en) * 1980-05-31 1981-12-25 Mitsubishi Petrochem Co Ltd Denitrating catalyst and denitrating method
JPS6372342A (en) * 1986-09-13 1988-04-02 Sakai Chem Ind Co Ltd Catalyst for removing nitrogen oxide

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56168835A (en) * 1980-05-31 1981-12-25 Mitsubishi Petrochem Co Ltd Denitrating catalyst and denitrating method
JPS6372342A (en) * 1986-09-13 1988-04-02 Sakai Chem Ind Co Ltd Catalyst for removing nitrogen oxide

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7256155B2 (en) 2003-03-14 2007-08-14 Mitsubishi Heavy Industries, Ltd. Flue gas denitration catalyst and preparation process thereof

Also Published As

Publication number Publication date
JPH0640957B2 (en) 1994-06-01

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