JPH10235206A - Denitration catalyst, preparation thereof and denitration method - Google Patents

Denitration catalyst, preparation thereof and denitration method

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Publication number
JPH10235206A
JPH10235206A JP9354908A JP35490897A JPH10235206A JP H10235206 A JPH10235206 A JP H10235206A JP 9354908 A JP9354908 A JP 9354908A JP 35490897 A JP35490897 A JP 35490897A JP H10235206 A JPH10235206 A JP H10235206A
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JP
Japan
Prior art keywords
size distribution
pore
pore size
peak
oxide
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
JP9354908A
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Japanese (ja)
Other versions
JP3337634B2 (en
Inventor
Noboru Sugishima
昇 杉島
Atsushi Morita
敦 森田
Motonobu Kobayashi
基伸 小林
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Nippon Shokubai Co Ltd
Original Assignee
Nippon Shokubai Co Ltd
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  • Catalysts (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a denitration catalyst superior in removal efficiency of NOx , its preparing method and a denitration method using the denitration catalyst. SOLUTION: This denitration catalyst comprises titanium oxide as a first component, and vanadium oxide and/or tungsten oxide as a second component, and has fine pores consisting of at least two fine pore groups of the fine pores having the vertex of the peak of the pore size distribution in a range of 0.01 to 0.05μm and the fine pores having the vertex of the peak of the pore size distribution in a range of >=0.1 and <=0.8μm, and when peak intensity of the pore size distribution of the fine pore group having the vertex of the peak of the pore size distribution in a range of 0.01 to 0.05μm is defined as 1, the peak intensity in the pore size distribution of the fine pore group having the vertex of the peak of the pore size distribution in a range of >=0.1 and <=0.8μm is >=0.4.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は脱硝触媒、すなわち
窒素酸化物(NOx)除去用触媒、この触媒の調製に好
適な脱硝触媒の調製方法、およびこの脱硝触媒を用いて
排ガス中の窒素酸化物を還元除去する方法に関する。
The present invention relates to a denitration catalyst, that is, a catalyst for removing nitrogen oxides (NOx), a method for preparing a denitration catalyst suitable for preparing this catalyst, and nitrogen oxides contained in exhaust gas using the denitration catalyst. And a method for reducing and removing the same.

【0002】[0002]

【従来の技術】現在実用化されている排ガス中の窒素酸
化物除去方法としては、アンモニア、または尿素などの
固体還元剤を用いて排ガス中の窒素酸化物を脱硝触媒上
で接触還元し、無害な窒素と水とに分解する選択的触媒
還元(SCR)法が一般的である。近年、酸性雨に代表
されるように窒素酸化物による環境汚染が世界的に深刻
化するにともない、脱硝技術の高効率化が要求されてい
る。
2. Description of the Related Art As a method of removing nitrogen oxides from exhaust gas which has been put into practical use at present, nitrogen oxides in the exhaust gas are catalytically reduced on a denitration catalyst using a solid reducing agent such as ammonia or urea, and harmless. The selective catalytic reduction (SCR) method, which decomposes into nitrogen and water, is common. In recent years, as the environmental pollution caused by nitrogen oxides, as typified by acid rain, has become more serious worldwide, it has been required to improve the efficiency of the denitration technology.

【0003】しかしながら、排ガス中の窒素酸化物およ
び還元剤として用いられるアンモニアは一般に希薄であ
り、触媒上でのガス拡散などの問題から、従来の脱硝触
媒では高い窒素酸化物除去性能を得ることは困難であっ
た。
[0003] However, nitrogen oxides in exhaust gas and ammonia used as a reducing agent are generally lean, and it is difficult to obtain high nitrogen oxide removal performance with a conventional denitration catalyst due to problems such as gas diffusion on the catalyst. It was difficult.

【0004】例えば、特公平4−42327号および同
1−14808号各公報には、ゾル化メタチタン酸にバ
ナジウム、モリブデンなどの金属酸化物を添加、混合し
た後、焼成して酸化チタン焼成品を製造する方法が開示
されているが、これら方法によって得られる脱硝触媒は
その窒素酸化物除去性能が決して十分ではない。
[0004] For example, Japanese Patent Publication Nos. 4-42327 and 1-14088 disclose that a metal oxide such as vanadium or molybdenum is added to solated metatitanic acid, mixed, and then fired to obtain a fired titanium oxide product. Although production methods are disclosed, the denitration catalysts obtained by these methods never have sufficient nitrogen oxide removal performance.

【0005】また、特開昭63−185448号公報に
は、チタンとバナジウム、タングステン、モリブデンな
どの卑金属とを含み、2つのピークが存在する細孔径分
布を有する脱硝触媒が開示されているが、この脱硝触媒
もまた窒素酸化物除去性能が十分でなく、より高い窒素
酸化物除去性能を有する脱硝触媒の開発が強く望まれて
いる。
JP-A-63-185448 discloses a denitration catalyst containing titanium and a base metal such as vanadium, tungsten and molybdenum and having a pore size distribution having two peaks. This denitration catalyst also has insufficient nitrogen oxide removal performance, and there is a strong demand for the development of a denitration catalyst having higher nitrogen oxide removal performance.

【0006】[0006]

【発明が解決しようとする課題】本発明の目的は、窒素
酸化物除去性能(以下、「脱硝性能」という)に優れ、
排ガス中の窒素酸化物を還元除去するに好適な脱硝触
媒、この脱硝触媒の調製に好適な脱硝触媒の調製方法、
およびこの脱硝触媒を用いてアンモニアなどの還元性物
質の存在下に排ガス中の窒素酸化物を還元除去する方法
を提供することにある。
SUMMARY OF THE INVENTION An object of the present invention is to provide excellent nitrogen oxide removal performance (hereinafter referred to as "denitration performance").
A denitration catalyst suitable for reducing and removing nitrogen oxides in exhaust gas, a method for preparing a denitration catalyst suitable for preparing this denitration catalyst,
It is another object of the present invention to provide a method for reducing and removing nitrogen oxides in exhaust gas by using the denitration catalyst in the presence of a reducing substance such as ammonia.

【0007】[0007]

【課題を解決するための手段】本発明者らは、チタン酸
化物とバナジウム酸化物および/またはタングステン酸
化物とを含有する脱硝触媒のなかでも、特定の細孔径分
布を有するものが、極めて高い脱硝性能を有すること、
またこの脱硝触媒は、その調製時に特定の易分解性物質
を使用することにより効率よく調製できることを知り、
この知見に基づいて本発明を完成するに至った。
The present inventors have found that among the denitration catalysts containing titanium oxide and vanadium oxide and / or tungsten oxide, those having a specific pore size distribution are extremely high. Having denitration performance,
Also, knowing that this denitration catalyst can be efficiently prepared by using a specific easily decomposable substance during its preparation,
Based on this finding, the present invention has been completed.

【0008】すなわち、本発明は、第一成分としてチタ
ン酸化物、第二成分としてバナジウム酸化物および/ま
たはタングステン酸化物を含有する脱硝触媒であって、
(1)0.01〜0.05μmの範囲に孔径分布のピー
クの頂点を有する細孔群と0.1μm以上0.8μm未
満の範囲に孔径分布のピークの頂点を有する細孔群との
少なくとも2つの細孔群からなる細孔を有し、かつ
(2)0.01〜0.05μmの範囲に孔径分布のピー
クの頂点を有する細孔群の孔径分布のピーク強度を1と
したとき、0.1μm以上0.8μm未満の範囲に孔径
分布のピークの頂点を有する細孔群の孔径分布のピーク
強度が0.4以上である、ことを特徴とする脱硝触媒で
ある。
That is, the present invention relates to a denitration catalyst containing titanium oxide as a first component and vanadium oxide and / or tungsten oxide as a second component,
(1) At least a group of pores having peaks of pore size distribution in the range of 0.01 to 0.05 μm and a group of pores having peaks of pore size distribution in the range of 0.1 μm to less than 0.8 μm. When the peak intensity of the pore size distribution of the pore group having pores composed of two pore groups and (2) having the peak of the peak of the pore size distribution in the range of 0.01 to 0.05 μm is defined as 1, A denitration catalyst characterized in that the peak intensity of the pore size distribution of a group of pores having a peak of the pore size distribution in the range of 0.1 μm or more and less than 0.8 μm is 0.4 or more.

【0009】また、本発明は、平均粒子径が5〜100
0μm、熱分解温度が100〜700℃、かつ分解時の
発熱量が50kcal/g以下である易分解性物質を触
媒前駆体に存在させ、これを焼成して除去することを特
徴とする脱硝触媒の調製方法である。
In the present invention, the average particle diameter is 5 to 100.
A denitration catalyst characterized in that an easily decomposable substance having a thermal decomposition temperature of 0 μm, a thermal decomposition temperature of 100 to 700 ° C., and a calorific value at the time of decomposition of 50 kcal / g or less is present in a catalyst precursor, which is calcined and removed. Preparation method of

【0010】また、本発明は、上記脱硝触媒に窒素酸化
物含有排ガスを接触させて窒素酸化物を還元除去する脱
硝方法である。
[0010] The present invention is also a denitration method for reducing and removing nitrogen oxides by bringing a nitrogen oxide-containing exhaust gas into contact with the denitration catalyst.

【0011】本発明の「孔径分布のピーク強度」とは、
図1に示すように、水銀圧入法による微分細孔容積分布
図において、微分細孔容積分布のピークの高さを意味す
る。また、「孔径分布のピーク半値幅」とは、図1に示
すように、ピーク強度の1/2の高さにおける微分細孔
容積分布ピーク幅を意味する。したがって、ピーク強度
が高く、ピーク半値幅が小さいほどシャープな微分細孔
容積分布であることが示される。
The “peak intensity of the pore size distribution” of the present invention means:
As shown in FIG. 1, in the differential pore volume distribution diagram by the mercury intrusion method, it means the peak height of the differential pore volume distribution. Further, as shown in FIG. 1, the “peak half width of the pore size distribution” means the peak width of the differential pore volume distribution at half the peak intensity. Therefore, the higher the peak intensity and the smaller the peak half width, the sharper the differential pore volume distribution is.

【0012】[0012]

【発明の実施の形態】本発明の脱硝触媒は第一成分とし
てチタン酸化物、第二成分としてバナジウム酸化物およ
び/またはタングステン酸化物を含有するものである。
第二成分の第一成分に対する割合(第二成分/第一成
分)は、通常、0.1〜25重量%であり、好ましくは
1〜15重量%である。特に、第二成分を脱硝触媒のB
ET法による単位表面積当り4.8×10-7〜2.2×
10-5mol/m2の割合で含有するものが好ましい。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The denitration catalyst of the present invention contains titanium oxide as a first component and vanadium oxide and / or tungsten oxide as a second component.
The ratio of the second component to the first component (second component / first component) is generally 0.1 to 25% by weight, preferably 1 to 15% by weight. In particular, the second component is a denitration catalyst B
4.8 × 10 -7 to 2.2 × per unit surface area by ET method
Those containing at a rate of 10 −5 mol / m 2 are preferred.

【0013】本発明の脱硝触媒の特徴は、(1)0.0
1〜0.05μmの範囲に孔径分布のピークの頂点を有
する細孔群(以下、「第一細孔群」という場合もある)
と0.1μm以上0.8μm未満の範囲に孔径分布のピ
ークの頂点を有する細孔群(以下、「第二細孔群」とい
う場合もある)との少なくとも2つの細孔群からなる細
孔を有し、かつ(2)0.01〜0.05μmの範囲に
孔径分布のピークの頂点を有する細孔群の孔径分布のピ
ーク強度を1としたとき、0.1μm以上0.8μm未
満の範囲に孔径分布のピークの頂点を有する細孔群の孔
径分布のピーク強度(以下、「ピーク強度比」という場
合もある)が0.4以上であることにある。
The characteristics of the denitration catalyst of the present invention are (1) 0.0
A group of pores having a peak of the peak of the pore size distribution in the range of 1 to 0.05 μm (hereinafter sometimes referred to as “first pore group”).
And a pore group having at least two pore groups of a pore group having a peak of a pore diameter distribution peak in a range of 0.1 μm or more and less than 0.8 μm (hereinafter, also referred to as “second pore group”). And (2) when the peak intensity of the pore size distribution of the pore group having the peak of the pore size distribution in the range of 0.01 to 0.05 μm is set to 1, the value is 0.1 μm or more and less than 0.8 μm. The peak intensity of the pore size distribution of the pore group having the peak of the peak of the pore size distribution in the range (hereinafter, also referred to as “peak intensity ratio”) is 0.4 or more.

【0014】すなわち、本発明の脱硝触媒は、図2〜4
に示すように、少なくとも0.01〜0.05μmおよ
び0.1μm以上0.8μm未満の範囲に各々一つづつ
実質的に独立した2つの孔径分布のピークを有し、しか
も第一細孔群のピーク強度に対する第二細孔群のピーク
強度が0.4以上というものである。本発明の脱硝触媒
は、上記要件(1)および(2)を満たす限り、孔径分
布ピークがショルダーを有するようなものであってもよ
いが、各細孔群の孔径分布が狭く、孔径が実質的に均一
なものが好ましい。
That is, the denitration catalyst of the present invention is shown in FIGS.
As shown in the figure, at least 0.01 to 0.05 μm and at least 0.1 μm to less than 0.8 μm each have two substantially independent pore size distribution peaks, and the first pore group The peak intensity of the second group of pores with respect to the peak intensity of No. is 0.4 or more. The denitration catalyst of the present invention may be one in which the pore size distribution peak has a shoulder as long as the above requirements (1) and (2) are satisfied, but the pore size distribution of each pore group is narrow and the pore size is substantially It is preferable that the particles are uniformly uniform.

【0015】第一および第二細孔群の孔径分布のピーク
の頂点がそれぞれ0.01〜0.05μmおよび0.1
μm以上0.8μm未満の範囲にない場合には、十分な
脱硝活性を得ることができない。また、第一および第二
細孔群の孔径分布のピークの頂点がそれぞれ0.01〜
0.05μmおよび0.1μm以上0.8μm未満の範
囲にあっても、上記要件(2)に規定するピーク強度比
が0.4より小さいと、目的とする十分高い脱硝性能を
有する脱硝触媒を得ることができない。なお、ピーク強
度比が高いほうが効果的であるが、高すぎると触媒強度
が低下することもあるので、その場合にはピーク強度比
を2以下とするのがよい。
The peaks of the pore size distribution peaks of the first and second pore groups are 0.01 to 0.05 μm and 0.1, respectively.
If it is not in the range of not less than μm and less than 0.8 μm, sufficient denitration activity cannot be obtained. Further, the peaks of the peaks of the pore size distribution of the first and second pore groups are each 0.01 to
If the peak intensity ratio defined in the above requirement (2) is smaller than 0.4 even in the range of 0.05 μm and 0.1 μm or more and less than 0.8 μm, the desired denitration catalyst having sufficiently high denitration performance can be obtained. I can't get it. The higher the peak intensity ratio, the more effective. However, if the peak intensity ratio is too high, the catalyst intensity may decrease. In this case, the peak intensity ratio is preferably set to 2 or less.

【0016】本発明の脱硝触媒においては、第二細孔群
の孔径分布が狭くシャープなものが好ましく、具体的に
は第二細孔群の孔径分布ピークの半値幅が0.3μm以
下のものが好ましい。上記半値幅を0.3μm以下、通
常0.01〜0.3μmとすることにより、脱硝性能が
向上し、触媒強度も高くなる。
In the denitration catalyst of the present invention, it is preferable that the pore size distribution of the second pore group is narrow and sharp. Specifically, the half-width of the pore size distribution peak of the second pore group is 0.3 μm or less. Is preferred. By setting the half width to 0.3 μm or less, usually 0.01 to 0.3 μm, the denitration performance is improved and the catalyst strength is also increased.

【0017】本発明の脱硝触媒の、水銀圧入法で測定し
た全細孔容積は、0.2〜0.6cc/gの範囲にある
のがよい。そして、第一細孔群が占める細孔容積は全細
孔容積の10〜60%、また第二細孔群が占める細孔容
積は全細孔容積の10〜60%の範囲にあるのがよい。
なお、第一および第二細孔群が占める細孔容積とは各孔
径範囲にある細孔が占める容積の合計量を意味する。
The total pore volume of the denitration catalyst of the present invention measured by a mercury intrusion method is preferably in the range of 0.2 to 0.6 cc / g. The pore volume occupied by the first pore group is in the range of 10 to 60% of the total pore volume, and the pore volume occupied by the second pore group is in the range of 10 to 60% of the total pore volume. Good.
The pore volume occupied by the first and second pore groups means the total amount of the volume occupied by pores in each pore diameter range.

【0018】本発明の脱硝触媒の平均粒子径は0.00
1〜100μm、好ましくは0.01〜100μmの範
囲にあるのがよい。また、本発明の脱硝触媒のBET法
による比表面積は30〜250m2/g、好ましくは4
0〜200m2/gの範囲にあるのがよい。
The average particle diameter of the denitration catalyst of the present invention is 0.00
It is good to be in the range of 1 to 100 μm, preferably 0.01 to 100 μm. The specific surface area of the denitration catalyst of the present invention measured by the BET method is 30 to 250 m 2 / g, preferably 4 to 250 m 2 / g.
It is preferably in the range of 0 to 200 m 2 / g.

【0019】本発明の脱硝触媒のなかでも、第一成分と
してチタン酸化物、第二成分としてバナジウム酸化物お
よび/またはタングステン酸化物を含有する脱硝触媒で
あって、(1)0.01〜0.05μmの範囲に孔径分
布のピークの頂点を有する細孔群と0.1μm以上0.
8μm未満の範囲に孔径分布のピークの頂点を有する細
孔群との少なくとも2つの細孔群からなる細孔を有し、
かつ(2)0.01〜0.05μmの範囲に孔径分布の
ピークの頂点を有する細孔群の孔径分布のピーク強度を
1としたとき、0.1μm以上0.8μm未満の範囲に
孔径分布のピークの頂点を有する細孔群の孔径分布のピ
ーク強度が0.4以上であり、さらに0.1μm以上
0.8μm未満の範囲に孔径分布のピークの頂点を有す
る細孔群の孔径分布のピーク半値幅が0.3μm以下、
水銀圧入法による全細孔容積が0.2〜0.6cc/
g、第一および第二細孔群が占める細孔容積がそれぞれ
全細孔容積の10〜60%および10〜60%、また第
二成分としてのバナジウム酸化物および/またはタング
ステン酸化物の第一成分としてのチタン酸化物に対する
割合(第二成分/第一成分)が0.1〜25重量%のも
のが好ましい。
Among the denitration catalysts of the present invention, a denitration catalyst containing titanium oxide as a first component and vanadium oxide and / or tungsten oxide as a second component, wherein (1) 0.01 to 0 A pore group having a peak of the peak of the pore size distribution in the range of 0.05 μm and 0.1 μm to 0.1 μm;
A pore group having at least two pore groups with a pore group having a peak of a pore diameter distribution peak in a range of less than 8 μm,
And (2) when the peak intensity of the pore size distribution of the pore group having a peak of the pore size distribution in the range of 0.01 to 0.05 μm is set to 1, the pore size distribution is in the range of 0.1 μm or more and less than 0.8 μm. The peak intensity of the pore size distribution of the pore group having the peak apex is 0.4 or more, and the pore size distribution of the pore group having the peak apex of the pore size distribution in the range of 0.1 μm or more and less than 0.8 μm. Peak half width is 0.3 μm or less,
The total pore volume by the mercury intrusion method is 0.2 to 0.6 cc /
g, the pore volume occupied by the first and second pore groups is 10 to 60% and 10 to 60%, respectively, of the total pore volume, and the first component of vanadium oxide and / or tungsten oxide as the second component is Preferably, the ratio (second component / first component) to titanium oxide as a component is 0.1 to 25% by weight.

【0020】特に、上記好適な脱硝触媒において、触媒
のBET法による単位表面積当りのバナジウム酸化物お
よび/またはタングステン酸化物のモル数が4.8×1
-7〜2.2×10-5mol/m2の割合であるものが
好ましい。
In particular, in the above preferred denitration catalyst, the number of moles of vanadium oxide and / or tungsten oxide per unit surface area of the catalyst determined by the BET method is 4.8 × 1.
Those having a ratio of 0 −7 to 2.2 × 10 −5 mol / m 2 are preferable.

【0021】本発明の脱硝触媒の形状については特に制
限はなく、板状、波板状、網状、ハニカム状、円柱状、
円筒状などの所望の形状で用いてもよく、またアルミ
ナ、シリカ、コーディライト、チタニア、ステンレス金
属などよりなる板状、波板状、網状、ハニカム状、円柱
状、円筒状などの所望の形状の担体に担持して使用して
もよい。
The shape of the denitration catalyst of the present invention is not particularly limited, and may be a plate, a corrugated plate, a net, a honeycomb, a column, or the like.
It may be used in a desired shape such as a cylindrical shape, or a desired shape such as a plate, a corrugated plate, a net, a honeycomb, a column, or a cylinder made of alumina, silica, cordierite, titania, stainless steel, or the like. May be supported on a carrier.

【0022】本発明の脱硝触媒の調製方法に制限はない
が、この種の触媒の調製時に一般に用いられる成型助剤
などのほかに、平均粒子径が5〜1000μm、熱分解
温度が100〜700℃、かつ分解時の発熱量が50k
cal/g以下である易分解性物質を触媒前駆体に存在
させ、これを焼成して除去する方法によって好適に調製
することができる。
The method for preparing the denitration catalyst of the present invention is not limited. In addition to a molding aid generally used for preparing this type of catalyst, it has an average particle size of 5 to 1000 μm and a thermal decomposition temperature of 100 to 700. ℃ and the calorific value during decomposition is 50k
It can be suitably prepared by a method in which a readily decomposable substance having a cal / g or less is present in the catalyst precursor, and this is calcined and removed.

【0023】上記易分解性物質の代表例としては、アセ
タール樹脂、アクリル樹脂、メタクリル樹脂、フェノー
ル樹脂、ベンゾグアナミン樹脂、不飽和ポリエステル樹
脂などを挙げることができる。この添加量は、触媒前駆
体の0.1〜30重量%とするのがよい。多すぎると脱
硝触媒の機械的強度が低下する。上記易分解性物質の発
熱量が50kcal/gを超えると焼成時の発熱が大き
くなり、脱硝触媒の比表面積が小さくなるほか、活性成
分のシンタリングなどの原因となる。また、熱分解温度
が700℃を超えると触媒焼成後に未燃の易分解性物質
が残存することがある。
Representative examples of the easily decomposable substances include acetal resins, acrylic resins, methacrylic resins, phenolic resins, benzoguanamine resins, and unsaturated polyester resins. The amount added is preferably 0.1 to 30% by weight of the catalyst precursor. If the amount is too large, the mechanical strength of the denitration catalyst decreases. When the calorific value of the easily decomposable substance exceeds 50 kcal / g, the calorific value at the time of calcination increases, the specific surface area of the denitration catalyst decreases, and sintering of the active component is caused. If the thermal decomposition temperature exceeds 700 ° C., unburned easily decomposable substances may remain after the catalyst is calcined.

【0024】チタン酸化物の供給原料としては、酸化チ
タンのほか、焼成してチタン酸化物を生成するものであ
れば、無機および有機のいずれの化合物も使用すること
ができる。例えば、四塩化チタン、硫酸チタンなどの無
機チタン化合物およびシュウ酸チタン、テトライソプロ
ピルチタネートなどの有機チタン化合物を用いることが
できる。また、バナジウム酸化物およびタングステン酸
化物の供給原料としては、各々の酸化物のほかに、焼成
によって酸化物を生成するものであれば、無機および有
機のいずれの化合物も用いることができる。例えば、各
々の金属を含む水酸化物、アンモニウム塩、シュウ酸
塩、ハロゲン化物、硫酸塩、硝酸塩などを用いることが
できる。
As the supply material of the titanium oxide, any of inorganic and organic compounds can be used in addition to titanium oxide, as long as it produces a titanium oxide by firing. For example, inorganic titanium compounds such as titanium tetrachloride and titanium sulfate, and organic titanium compounds such as titanium oxalate and tetraisopropyl titanate can be used. In addition to the respective oxides, any of inorganic and organic compounds can be used as a raw material of the vanadium oxide and the tungsten oxide as long as the oxides are generated by firing. For example, a hydroxide, an ammonium salt, an oxalate, a halide, a sulfate, a nitrate, or the like containing each metal can be used.

【0025】以下、代表的な調製方法として、方法A〜
Cを挙げて説明するが、上記易分解性物質は、適当な時
期に添加して、焼成前の触媒前駆体に必要量存在するよ
うにすればよい。
Hereinafter, as typical preparation methods, methods A to
C will be described, but the easily decomposable substance may be added at an appropriate time so that a necessary amount of the catalyst precursor before calcination is present.

【0026】方法Aは、いわゆる共沈法といわれるもの
であり、可溶性チタン化合物、例えば四塩化チタンと可
溶性タングステン化合物、例えばメタタングステン酸ア
ンモニウムとを水に溶解して酸性のチタン−タングステ
ン含有水溶液とする。次に、この水溶液の温度を60℃
以下、好ましくは0〜50℃の範囲に保持しながら、ア
ンモニア水を最終pHが5〜8、好ましくは5以上で7
未満の範囲となるように添加して共沈させる。なお、タ
ングステン化合物の水溶液が塩基性の場合には、タング
ステン含有水溶液をアンモニア水と同時にチタン含有水
溶液に添加して沈澱させる。なお、上記最終pHとは沈
澱操作を終了した時点での沈澱物スラリーまたはゲルの
pHを意味する。
Method A is a so-called coprecipitation method in which a soluble titanium compound, for example, titanium tetrachloride and a soluble tungsten compound, for example, ammonium metatungstate are dissolved in water to form an acidic aqueous solution containing titanium and tungsten. I do. Next, the temperature of the aqueous solution was set to 60 ° C.
Hereinafter, while maintaining the temperature preferably in the range of 0 to 50 ° C., the final pH of the aqueous ammonia is 5 to 8, preferably 5 to 7,
And coprecipitate so as to be less than the range. When the aqueous solution of the tungsten compound is basic, the aqueous solution containing tungsten is added to the aqueous solution containing titanium at the same time as the aqueous ammonia to precipitate. The final pH means the pH of the precipitate slurry or gel at the time when the precipitation operation is completed.

【0027】上記沈澱操作における温度が60℃を超え
ると得られる脱硝触媒の活性が低下する。また、最終p
Hが5より低いと得られる脱硝触媒の活性は低下し、ま
た8を超えると脱硝触媒の活性は低下し、そのうえタン
グステンの再溶解も起こる。上記沈澱操作により得られ
たチタン−タングステン沈澱物は、沈澱物スラリーから
分離し、よく洗浄し、乾燥した後、焼成することにより
チタン−タングステン酸化物が得られる。上記分離、洗
浄、乾燥および焼成は、この種の酸化物の調製に一般的
に用いられている条件下で行うことができるが、酸化チ
タン/酸化タングステンの重量比が10/1〜3/1、
好ましくは20/1〜4/1のものを300〜700
℃、特に350〜600℃の範囲で加熱焼成すると耐久
性の優れたチタン−タングステン酸化物が得られる。
When the temperature in the above-mentioned precipitation operation exceeds 60 ° C., the activity of the denitration catalyst obtained decreases. Also, the final p
When H is lower than 5, the activity of the obtained denitration catalyst is reduced, and when it is more than 8, the activity of the denitration catalyst is reduced, and re-dissolution of tungsten also occurs. The titanium-tungsten precipitate obtained by the above-mentioned precipitation operation is separated from the precipitate slurry, washed well, dried, and then calcined to obtain a titanium-tungsten oxide. The above-mentioned separation, washing, drying and calcination can be performed under the conditions generally used for the preparation of this kind of oxide, and the weight ratio of titanium oxide / tungsten oxide is 10/1 to 3/1. ,
Preferably 20/1 to 4/1 is 300 to 700
When heated and baked at a temperature of 350C to 600C, a titanium-tungsten oxide having excellent durability can be obtained.

【0028】方法Bは、チタン酸化物にバナジウム酸化
物および/またはタングステン酸化物を担持させる方法
であり、例えばチタン酸化物の粉体またはスラリーにバ
ナジウムおよび/またはタングステンの塩類粉末または
その塩類の溶液を添加するか、あるいはチタン酸化物の
成形体にバナジウムおよび/またはタングステンの塩類
の溶液を含浸させて担持させることによりチタン−バナ
ジウムおよび/またはタングステン酸化物が得られる。
なお、焼成条件などは前記方法Aと同じである。
Method B is a method in which vanadium oxide and / or tungsten oxide is supported on titanium oxide. For example, a powder or slurry of vanadium and / or tungsten or a solution of salts of vanadium and / or tungsten is applied to a powder or slurry of titanium oxide. Or a titanium-vanadium and / or tungsten oxide can be obtained by impregnating a titanium oxide compact with a solution of vanadium and / or tungsten salts and supporting it.
The firing conditions and the like are the same as those in the method A.

【0029】方法Cは、予めタングステン酸化物を担持
したチタン酸化物、またはチタン酸化物とタングステン
酸化物との均密混合物にバナジウム酸化物および/また
はタングステン酸化物を担持する方法である。具体的に
は、前記方法Aと同様にして調製した共沈チタン−タン
グステン酸化物粉体またはスラリーにバナジウム酸化物
および/またはタングステン酸化物の塩類粉末またはそ
の塩類の溶液を添加する方法や、硫酸チタンや四塩化チ
タンなどの溶液を熱加水分解して得られるチタン酸化物
ゾルにタングステンの塩類の溶液を加えた後、アンモニ
ア水を加えて沈澱させることによって得られるチタン−
タングステン酸化物粉体またはスラリーにバナジウム酸
化物および/またはタングステン酸化物の塩類粉末また
はその塩類の溶液を添加する方法、あるいはこれらの方
法によって得られるチタン−タングステン酸化物の成形
体にバナジウムおよび/またはタングステンの塩類の溶
液を含浸させる方法などが挙げられる。なお、焼成条件
などは前記方法Aと同じである。
Method C is a method in which vanadium oxide and / or tungsten oxide is supported on titanium oxide which has previously supported tungsten oxide, or on a dense mixture of titanium oxide and tungsten oxide. Specifically, a method of adding a salt powder of vanadium oxide and / or tungsten oxide or a solution of the salt thereof to a coprecipitated titanium-tungsten oxide powder or slurry prepared in the same manner as the above method A, A solution of a salt of tungsten is added to a titanium oxide sol obtained by thermally hydrolyzing a solution of titanium, titanium tetrachloride, or the like, and then titanium water obtained by precipitation by adding aqueous ammonia.
A method of adding vanadium oxide and / or a salt powder of a tungsten oxide or a solution of a salt thereof to a tungsten oxide powder or a slurry, or vanadium and / or a vanadium and / or a titanium-tungsten oxide formed body obtained by these methods. A method of impregnating with a solution of a salt of tungsten is exemplified. The firing conditions and the like are the same as those in the method A.

【0030】上記方法Cによって得られる脱硝触媒は脱
硝性能に優れている。その理由は明らかではないが、チ
タン酸化物上に分散したタングステン酸化物が窒素酸化
物の分解に寄与し、さらに他の活性種の活性を向上させ
るためであると考えられる。この点からもタングステン
酸化物を担持したチタン酸化物は、タングステン酸化物
が高分散したチタン酸化物とタングステン酸化物の均密
混合物であることが触媒活性が高くなり好ましい。ここ
でいうチタン酸化物とタングステン酸化物との均密混合
物とは、チタン酸化物とタングステン酸化物とが高度に
混合された結果、チタン酸化物とタングステン酸化物と
のX線回折ではタングステン酸化物に由来するピークが
実質的に認められないことが特徴である。
The denitration catalyst obtained by the above method C has excellent denitration performance. Although the reason is not clear, it is considered that the tungsten oxide dispersed on the titanium oxide contributes to the decomposition of the nitrogen oxide and further improves the activity of other active species. From this viewpoint, it is preferable that the titanium oxide supporting the tungsten oxide is an intimate mixture of the titanium oxide and the tungsten oxide in which the tungsten oxide is highly dispersed because the catalytic activity is high. The dense mixture of titanium oxide and tungsten oxide as used herein means that the titanium oxide and tungsten oxide are highly mixed, and the titanium oxide and tungsten oxide are tungsten oxide in the X-ray diffraction. Is characterized in that a peak derived from is substantially not observed.

【0031】上記方法A〜Cのなかでも、方法Cが好適
に用いられる。すなわち、タングステン酸化物をチタン
酸化物に担持した後、バナジウム酸化物および/または
タングステン酸化物を担持する方法、およびチタン酸化
物とタングステン酸化物との均密混合物を調製した後、
この混合物にバナジウム酸化物および/またはタングス
テン酸化物を担持する方法が好適に用いられる。
Of the above methods A to C, method C is preferably used. That is, after supporting tungsten oxide on titanium oxide, a method for supporting vanadium oxide and / or tungsten oxide, and after preparing an intimate mixture of titanium oxide and tungsten oxide,
A method of supporting vanadium oxide and / or tungsten oxide on this mixture is preferably used.

【0032】本発明の脱硝触媒は、ボイラ、加熱炉、ガ
スタービン、ディーゼルエンジンおよび各種工業プロセ
スから排出される窒素酸化物の分解活性に優れ、これら
窒素酸化物を含む排ガスの処理に好適に用いられる。
The denitration catalyst of the present invention has excellent activity for decomposing nitrogen oxides discharged from boilers, heating furnaces, gas turbines, diesel engines and various industrial processes, and is suitably used for treating exhaust gases containing these nitrogen oxides. Can be

【0033】本発明の脱硝方法は、本発明の脱硝触媒を
アンモニアなどの還元剤の存在下に排ガスと接触させ、
排ガス中の窒素酸化物を還元除去することからなる。こ
の際の条件などについては、特に制限はなく、この種の
反応に一般的に用いられている条件下に実施することが
できる。具体的には、排ガスの種類、性状、要求される
窒素酸化物の分解率などを考慮して適宜決定すればよ
い。
The denitration method of the present invention comprises contacting the denitration catalyst of the present invention with exhaust gas in the presence of a reducing agent such as ammonia.
It consists of reducing and removing nitrogen oxides in the exhaust gas. The conditions at this time are not particularly limited, and the reaction can be carried out under conditions generally used for this type of reaction. Specifically, it may be appropriately determined in consideration of the type and properties of the exhaust gas, the required nitrogen oxide decomposition rate, and the like.

【0034】なお、排ガスの空間速度は、通常、100
〜100000Hr-1であり、好ましくは200〜50
000Hr-1(STP)である。100Hr-1未満で
は、処理装置が大きくなりすぎ非効率となり、一方10
0000Hr-1を超えると、分解効率が低下する。
The space velocity of the exhaust gas is usually 100
100100,000 Hr −1 , preferably 200 to 50
000 Hr -1 (STP). If it is less than 100 Hr −1 , the processing equipment becomes too large and inefficient, while
If it exceeds 0000Hr −1 , the decomposition efficiency is reduced.

【0035】[0035]

【実施例】以下、実施例を挙げて本発明を更に具体的に
説明する。
EXAMPLES Hereinafter, the present invention will be described more specifically with reference to examples.

【0036】実施例1 市販の酸化チタン粉体(DT−51(商品名)、ローヌ
・プーラン社製)20kgにメタバナジン酸アンモニウ
ム1.4kg、シュウ酸1.7kgおよびモノエタノー
ルアミン0.4kgを水5L(リットル)に溶解させた
溶液を加え、さらにフェノール樹脂(ベルパール(商品
名)、カネボウ(株)製)1kgと成形助剤としてのデ
ンプン0.5kgとを加えて混合し、ニーダーで混練り
した後、押出成形機で外形80mm角、目開き4.0m
m、肉厚1.0mm、長さ500mmのハニカム状に成
形した。次いで、80℃で乾燥した後、450℃で5時
間空気雰囲気下で焼成して触媒Aを得た。
Example 1 1.4 kg of ammonium metavanadate, 1.7 kg of oxalic acid and 0.4 kg of monoethanolamine were added to 20 kg of commercially available titanium oxide powder (DT-51 (trade name), manufactured by Rhone Poulin) in water. A solution dissolved in 5 L (liter) was added, and 1 kg of a phenolic resin (Bellpearl (trade name), manufactured by Kanebo Co., Ltd.) and 0.5 kg of starch as a molding aid were added, mixed, and kneaded with a kneader. After that, the outer shape is 80 mm square and the aperture is 4.0 m with an extrusion molding machine.
m, a thickness of 1.0 mm, and a length of 500 mm. Next, after drying at 80 ° C., it was calcined at 450 ° C. for 5 hours in an air atmosphere to obtain a catalyst A.

【0037】上記フェノール樹脂は、平均粒子径20μ
m、熱分解温度450℃、分解時の発熱量8kcal/
gであった。
The phenol resin has an average particle size of 20 μm.
m, thermal decomposition temperature 450 ° C, calorific value during decomposition 8 kcal /
g.

【0038】触媒Aの組成は、V25:TiO2=5:
95(重量比)であった。触媒Aの細孔径分布を水銀圧
入式ポロシメーターにより測定したところ、ピーク強度
比は0.77であり、第二細孔群の孔径分布のピーク半
値幅は0.13μmであった。全細孔容積は0.35c
c/gであり、第一および第二細孔群の細孔容積はそれ
ぞれ全細孔容積の44%および48%であった。また、
BET表面積は68m2/gであり、バナジウム酸化物
(V25)の、触媒の単位表面積当りの含有量は3.8
×10-6mol/m2であった。触媒Aの細孔径分布を
図2に示した。
The composition of the catalyst A is V 2 O 5 : TiO 2 = 5:
95 (weight ratio). When the pore size distribution of the catalyst A was measured by a mercury intrusion porosimeter, the peak intensity ratio was 0.77, and the peak half width of the pore size distribution of the second pore group was 0.13 μm. The total pore volume is 0.35c
c / g, and the pore volumes of the first and second pore groups were 44% and 48% of the total pore volume, respectively. Also,
The BET surface area was 68 m 2 / g, and the content of vanadium oxide (V 2 O 5 ) per unit surface area of the catalyst was 3.8.
× 10 −6 mol / m 2 . The pore size distribution of catalyst A is shown in FIG.

【0039】実施例2 硫酸法による酸化チタンの製造工程より得られる硫酸チ
タン溶液(二酸化チタンとして100g/L)180L
を100℃に加熱し、得られたチタン酸化物ゾルにパラ
タングステン酸アンモニウムの10%メチルアミン水溶
液(三酸化タングステンとして400g/L)5Lを添
加した。これを攪拌しながらアンモニア水をpHが8と
なるまで加え、さらにそのままに放置して2時間熟成し
た。このようにして得られたチタン−タングステン沈澱
物スラリーをろ過し、得られたチタン−タングステン沈
澱物を水洗した後、100℃で12時間乾燥し、さらに
500℃の温度で3時間焼成し、チタン−タングステン
酸化物粉体(酸化チタン/酸化タングステン=90/1
0(重量比))を得た。なお、この酸化物のX線回折に
よれば、タングステン酸化物に由来するピークは認めら
れなかった。
Example 2 180 L of a titanium sulfate solution (100 g / L as titanium dioxide) obtained from a process for producing titanium oxide by a sulfuric acid method
Was heated to 100 ° C., and 5 L of a 10% aqueous solution of ammonium paratungstate in methylamine (400 g / L as tungsten trioxide) was added to the obtained titanium oxide sol. While stirring, ammonia water was added until the pH became 8, and the mixture was left to stand and aged for 2 hours. The titanium-tungsten precipitate slurry thus obtained was filtered, and the obtained titanium-tungsten precipitate was washed with water, dried at 100 ° C. for 12 hours, and calcined at a temperature of 500 ° C. for 3 hours to obtain a titanium-tungsten precipitate. -Tungsten oxide powder (titanium oxide / tungsten oxide = 90/1)
0 (weight ratio)). According to X-ray diffraction of this oxide, no peak derived from tungsten oxide was observed.

【0040】このチタン−タングステン酸化物粉体20
kgにメタバナジン酸アンモニウム1.4kg、シュウ
酸1.7kgおよびモノエタノールアミン0.4kgを
水5Lに溶解させた溶液を加え、さらにフェノール樹脂
(ベルパール(商品名)、カネボウ(株)製)1kgと
成形助剤としてのデンプン0.5kgを加えて混合しニ
ーダーで混練りした後、押出成形機で外形80mm角、
目開き4.0mm、肉厚1.0mm、長さ500mmの
ハニカム状に成形した。次いで、80℃乾燥した後、4
50℃で5時間空気雰囲気下で焼成して触媒Bを得た。
This titanium-tungsten oxide powder 20
A solution prepared by dissolving 1.4 kg of ammonium metavanadate, 1.7 kg of oxalic acid and 0.4 kg of monoethanolamine in 5 L of water was added to the resulting solution, and 1 kg of a phenol resin (Bellpearl (trade name), manufactured by Kanebo Co., Ltd.) was added. 0.5 kg of starch as a molding aid was added, mixed and kneaded with a kneader, and then extruded with an extruder to an outer shape of 80 mm square.
It was formed into a honeycomb shape having an aperture of 4.0 mm, a wall thickness of 1.0 mm, and a length of 500 mm. Next, after drying at 80 ° C., 4
It was calcined at 50 ° C. for 5 hours in an air atmosphere to obtain a catalyst B.

【0041】触媒Bの組成は、V25:WO3:TiO2
=5:10:85(重量比)であった。触媒Bの細孔径
分布を水銀圧入式ポロシメーターにより測定したとこ
ろ、ピーク強度比は1.05であり、第二細孔群の孔径
分布のピーク半値幅は0.20μmであった。全細孔容
積は0.49cc/gであり、第一および第二細孔群の
細孔容積はそれぞれ全細孔容積の43%および51%で
あった。また、触媒BのBET表面積は71m2/gで
あり、バナジウム酸化物およびタングステン酸化物(W
3)の、触媒の単位表面積当りの含有量はそれぞれ
3.7×10-6mol/m2および5.7×10-6mo
l/m2であった。触媒Bの細孔径分布を図3に示し
た。
The composition of the catalyst B is V 2 O 5 : WO 3 : TiO 2
= 5: 10: 85 (weight ratio). When the pore size distribution of the catalyst B was measured by a mercury intrusion porosimeter, the peak intensity ratio was 1.05, and the peak half width of the pore size distribution of the second pore group was 0.20 μm. The total pore volume was 0.49 cc / g, and the pore volumes of the first and second pore groups were 43% and 51% of the total pore volume, respectively. The BET surface area of the catalyst B was 71 m 2 / g, and vanadium oxide and tungsten oxide (W
The content of O 3 ) per unit surface area of the catalyst was 3.7 × 10 −6 mol / m 2 and 5.7 × 10 −6 mo, respectively.
1 / m 2 . The pore size distribution of catalyst B is shown in FIG.

【0042】実施例3 水80Lに四塩化チタン(TiCl4)12.8kgを
氷冷かつ撹拌下に徐々に添加して溶解し、この水溶液に
メタタングステン酸アンモニウム水溶液(酸化タングス
テンとして50重量%含有)1.2kgを加えた。得ら
れた水溶液を温度約30℃に保持しつつ、よく撹拌しな
がら、アンモニア水をpHが6となるまで加え、さらに
そのまま放置して2時間熟成した。このようにして得ら
れたチタン−タングステン沈澱物スラリーをろ過し、得
られたチタン−タングステン沈澱を水洗して、150℃
で乾燥した後、600℃で5時間焼成した酸化チタン/
酸化タングステン=90/10(重量比)のチタン−タ
ングステン酸化物を得た。このようにして得られた共沈
チタン−タングステン酸化物粉体20kgにメタバナジ
ン酸アンモニウム1.4kg、シュウ酸1.7kgおよ
びモノエタノールアミン0.4kgを水5Lに溶解させ
た溶液を加え、さらにフェノール樹脂(ベルパール(商
品名)、カネボウ(株)製)1kgと成形助剤としての
デンプン0.5kgとを加えて混合しニーダーで混練り
した後、押出成形機で外形80mm角、目開き4.0m
m、肉厚1.0mm、長さ500mmのハニカム状に成
形した。次いで、80℃で乾燥した後、450℃で5時
間空気雰囲気下で焼成して触媒Cを得た。
Example 3 12.8 kg of titanium tetrachloride (TiCl 4 ) was gradually added to 80 L of water under ice-cooling and stirring to dissolve, and an aqueous solution of ammonium metatungstate (containing 50% by weight as tungsten oxide) was added to the aqueous solution. ) 1.2 kg. While keeping the obtained aqueous solution at a temperature of about 30 ° C., ammonia water was added thereto until the pH reached 6, with sufficient stirring, and the mixture was left to ripen for 2 hours. The titanium-tungsten precipitate slurry thus obtained was filtered, and the obtained titanium-tungsten precipitate was washed with water and heated at 150 ° C.
And then calcined at 600 ° C for 5 hours.
A titanium-tungsten oxide having a tungsten oxide content of 90/10 (weight ratio) was obtained. A solution prepared by dissolving 1.4 kg of ammonium metavanadate, 1.7 kg of oxalic acid and 0.4 kg of monoethanolamine in 5 L of water was added to 20 kg of the coprecipitated titanium-tungsten oxide powder thus obtained. 3. Add 1 kg of resin (Bellpearl (trade name), manufactured by Kanebo Co., Ltd.) and 0.5 kg of starch as a molding aid, mix and knead with a kneader, and then use an extruder to form an outer shape of 80 mm square and 4 openings. 0m
m, a thickness of 1.0 mm, and a length of 500 mm. Next, after drying at 80 ° C., it was calcined at 450 ° C. for 5 hours in an air atmosphere to obtain a catalyst C.

【0043】触媒Cの組成は、V25:WO3:TiO2
=5:10:85(重量比)であった。触媒Cの細孔径
分布を水銀圧入式ポロシメーターにより測定したとこ
ろ、ピーク強度比は0.59であり、第二細孔群の孔径
分布のピーク半値幅は0.29μmであった。全細孔容
積は0.37cc/gであり、第一および第二細孔群の
細孔容積はそれぞれ全細孔容積の57%および37%で
あった。また、BET表面積は78m2/gであり、バ
ナジウム酸化物およびタングステン酸化物の、触媒の単
位表面積当りの含有量はそれぞれ3.3×10-6mol
/m2および5.2×10-6mol/m2であった。触媒
Cの細孔径分布を図4に示した。
The composition of the catalyst C is V 2 O 5 : WO 3 : TiO 2
= 5: 10: 85 (weight ratio). When the pore size distribution of the catalyst C was measured by a mercury intrusion porosimeter, the peak intensity ratio was 0.59, and the peak half width of the pore size distribution of the second pore group was 0.29 μm. The total pore volume was 0.37 cc / g, and the pore volumes of the first and second pore groups were 57% and 37% of the total pore volume, respectively. The BET surface area was 78 m 2 / g, and the content of vanadium oxide and tungsten oxide per unit surface area of the catalyst was 3.3 × 10 −6 mol.
/ M 2 and 5.2 × 10 −6 mol / m 2 . FIG. 4 shows the pore size distribution of the catalyst C.

【0044】比較例1 実施例2で用いたチタン−タングステン酸化物粉体をさ
らに気流粉砕機で粉砕し、混練りの際にフェノール樹脂
を加えず、成形機の前段に脱気層を設置して練り物中の
空気を除去したこと以外は実施例2に準じて外形80m
m角、目開き4.0mm、肉厚1.0mm、長さ500
mmのハニカム状触媒Dを調製した。
Comparative Example 1 The titanium-tungsten oxide powder used in Example 2 was further pulverized by an air current pulverizer, a phenol resin was not added at the time of kneading, and a deaeration layer was provided in the former stage of the molding machine. Except that the air in the kneaded material was removed, the outer shape was 80 m according to Example 2.
m square, aperture 4.0 mm, wall thickness 1.0 mm, length 500
mm of a honeycomb catalyst D was prepared.

【0045】触媒Dの細孔径分布を水銀圧入式ポロシメ
ーターにより測定したところ、0.01〜0.05μm
の範囲の孔径を有する第一細孔群のみが認められ、0.
1μm以上0.8μm未満の範囲の孔径を有す第二細孔
群は存在しなかった。触媒Dの全細孔容積は0.25c
c/gであった。また、BET表面積は65m2/gで
あり、バナジウム酸化物およびタングステン酸化物の、
触媒の単位表面積当りの含有量はそれぞれ4.0×10
-6mol/m2および6.3×10-6mol/m2であっ
た。触媒Dの細孔径分布を図5に示した。
When the pore size distribution of the catalyst D was measured by a mercury intrusion porosimeter, it was 0.01 to 0.05 μm.
Only the first group of pores having a pore size in the range
There was no second pore group having a pore diameter in the range of 1 μm or more and less than 0.8 μm. The total pore volume of catalyst D is 0.25c
c / g. The BET surface area is 65 m 2 / g, and the vanadium oxide and the tungsten oxide
The content per unit surface area of the catalyst was 4.0 × 10 4
-6 mol / m 2 and 6.3 × 10 -6 mol / m 2 . The pore size distribution of catalyst D is shown in FIG.

【0046】実施例4 実施例1〜3および比較例1で得られた触媒A〜Dを用
いて下記条件下で脱硝活性試験を行った。
Example 4 Using the catalysts A to D obtained in Examples 1 to 3 and Comparative Example 1, a denitration activity test was carried out under the following conditions.

【0047】試験条件 NOx:70ppm、NH3:70ppm、O2:13
%、H2O:7%、N2:バランス ガス温度:190〜330℃、空間速度(STP):1
0000〜20000Hr-1 そして、脱硝率を下記式にしたがって求めた。
Test conditions NOx: 70 ppm, NH 3 : 70 ppm, O 2 : 13
%, H 2 O: 7%, N 2 : balance Gas temperature: 190 to 330 ° C., space velocity (STP): 1
0000 to 20000 Hr -1 and the denitration rate were determined according to the following equation.

【0048】脱硝率(%)=[(反応器入口NOx濃
度)−(反応器出口NOx濃度)]÷(反応器入口NO
x濃度)×100 ガス温度と脱硝率との関係を表1に示した(空間速度:
16000Hr-1)。
Denitration rate (%) = [(reactor inlet NOx concentration) − (reactor outlet NOx concentration)] ÷ (reactor inlet NO
x concentration) × 100 The relationship between gas temperature and denitration rate is shown in Table 1 (space velocity:
16000Hr- 1 ).

【0049】[0049]

【表1】 [Table 1]

【0050】また、空間速度と脱硝率との関係を表2に
示した(ガス温度:230℃)。
Table 2 shows the relationship between the space velocity and the denitration rate (gas temperature: 230 ° C.).

【0051】[0051]

【表2】 [Table 2]

【0052】実施例5 実施例2で得られた触媒Bを用いて下記条件下で脱硝活
性試験を行った。
Example 5 A denitration activity test was carried out using the catalyst B obtained in Example 2 under the following conditions.

【0053】試験条件 NOx:200ppm、NH3:200ppm、SO2
800ppm、O2:12%、H2O:10%、N2:バ
ランス ガス温度:380℃、空間速度:5000Hr-1 脱硝率を実施例4と同様にして求めたところ99%であ
った。
Test conditions NOx: 200 ppm, NH 3 : 200 ppm, SO 2 :
800 ppm, O 2 : 12%, H 2 O: 10%, N 2 : balance Gas temperature: 380 ° C., Space velocity: 5000 Hr −1 The denitration ratio was determined in the same manner as in Example 4, and it was 99%.

【0054】[0054]

【発明の効果】本発明の脱硝触媒は脱硝性能に優れ、特
に窒素酸化物の希薄な各種の排ガスを処理して窒素酸化
物を還元除去するに好適に用いられる。
The denitration catalyst of the present invention has excellent denitration performance, and is particularly preferably used for treating various exhaust gases having a low nitrogen oxide content to reduce and remove the nitrogen oxide.

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

【図1】孔径分布のピーク強度とピーク半値幅を示す説
明図である。
FIG. 1 is an explanatory diagram showing a peak intensity and a peak half width of a pore size distribution.

【図2】実施例1で得られた触媒Aの細孔径分布を示
す。
FIG. 2 shows the pore size distribution of catalyst A obtained in Example 1.

【図3】実施例2で得られた触媒Bの細孔径分布を示
す。
FIG. 3 shows a pore size distribution of catalyst B obtained in Example 2.

【図4】実施例3で得られた触媒Cの細孔径分布を示
す。
FIG. 4 shows the pore size distribution of catalyst C obtained in Example 3.

【図5】比較例1で得られた触媒Dの細孔径分布を示
す。
FIG. 5 shows the pore size distribution of catalyst D obtained in Comparative Example 1.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 第一成分としてチタン酸化物、第二成分
としてバナジウム酸化物および/またはタングステン酸
化物を含有する脱硝触媒であって、(1)0.01〜
0.05μmの範囲に孔径分布のピークの頂点を有する
細孔群と0.1μm以上0.8μm未満の範囲に孔径分
布のピークの頂点を有する細孔群との少なくとも2つの
細孔群からなる細孔を有し、かつ(2)0.01〜0.
05μmの範囲に孔径分布のピークの頂点を有する細孔
群の孔径分布のピーク強度を1としたとき、0.1μm
以上0.8μm未満の範囲に孔径分布のピークの頂点を
有する細孔群の孔径分布のピーク強度が0.4以上であ
る、ことを特徴とする脱硝触媒。
1. A denitration catalyst containing titanium oxide as a first component and vanadium oxide and / or tungsten oxide as a second component, wherein (1) 0.01 to
Consisting of at least two pore groups: a pore group having a peak of the pore size distribution in the range of 0.05 μm and a pore group having the peak of the pore size distribution in the range of 0.1 μm to less than 0.8 μm. (2) 0.01-0.
When the peak intensity of the pore size distribution of the pore group having the peak of the pore size distribution in the range of 05 μm is set to 1, 0.1 μm
A denitration catalyst, wherein the peak intensity of the pore size distribution of a group of pores having a peak of the pore size distribution in the range of not more than 0.8 μm is 0.4 or more.
【請求項2】 0.1μm以上0.8μm未満の範囲に
孔径分布のピークの頂点を有する細孔群の孔径分布のピ
ーク半値幅が0.3μm以下である請求項1記載の脱硝
触媒。
2. The denitration catalyst according to claim 1, wherein the peak half width of the pore size distribution of the pore group having a peak of the pore size distribution in the range of 0.1 μm or more and less than 0.8 μm is 0.3 μm or less.
【請求項3】 触媒の単位表面積当りのバナジウム酸化
物および/またはタングステン酸化物のモル数が4.8
×10-7〜2.2×10-5mol/m2である請求項1
または2記載の脱硝触媒。
3. The catalyst according to claim 1, wherein the number of moles of vanadium oxide and / or tungsten oxide per unit surface area of the catalyst is 4.8.
× 10 -7 to 2.2 claim 1 wherein × 10 -5 mol / m 2
Or the denitration catalyst according to 2.
【請求項4】 平均粒子径が5〜1000μm、熱分解
温度が100〜700℃、かつ分解時の発熱量が50k
cal/g以下である易分解性物質を触媒前駆体に存在
させ、これを焼成して除去することを特徴とする脱硝触
媒の調製方法。
4. An average particle size of 5 to 1000 μm, a thermal decomposition temperature of 100 to 700 ° C., and a calorific value during decomposition of 50 k.
A method for preparing a denitration catalyst, characterized in that a readily decomposable substance having a cal / g or less is present in a catalyst precursor, and this is calcined and removed.
【請求項5】 請求項1の脱硝触媒に窒素酸化物含有排
ガスを接触させて窒素酸化物を還元除去する脱硝方法。
5. A denitration method for reducing and removing nitrogen oxides by contacting a nitrogen oxide-containing exhaust gas with the denitration catalyst according to claim 1.
JP35490897A 1996-12-27 1997-12-24 Denitration catalyst, its preparation method, and denitration method Expired - Fee Related JP3337634B2 (en)

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US7150861B2 (en) 2001-09-28 2006-12-19 Nippon Shokubai Co., Ltd. Catalyst for purification of exhaust gases and process for purification of exhaust gases
US7740819B2 (en) 2002-02-26 2010-06-22 Nippon Shokubai Co., Ltd. Process for purification of exhaust gases and catalyst used for purification of exhaust gases in this process
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US6855304B2 (en) 1999-06-25 2005-02-15 Nippon Shokubai Co., Ltd. Catalyst and process for removing organohalogen compounds
KR20030006598A (en) * 2001-07-13 2003-01-23 주식회사 나노 Titanium Dioxide Powder For Selective Catalytic Reduction Support For Removing NOx Compounds And Method Of Preparing Thereof
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WO2003009938A1 (en) * 2001-07-25 2003-02-06 Ngk Insulators,Ltd. Honeycomb structural body for exhaust emission control and honeycomb catalyst body for exhaust emission control
US7150861B2 (en) 2001-09-28 2006-12-19 Nippon Shokubai Co., Ltd. Catalyst for purification of exhaust gases and process for purification of exhaust gases
US7740819B2 (en) 2002-02-26 2010-06-22 Nippon Shokubai Co., Ltd. Process for purification of exhaust gases and catalyst used for purification of exhaust gases in this process
JP2013173147A (en) * 2005-02-16 2013-09-05 Basf Catalysts Llc Ammonia oxidation catalyst for the coal fired utilities
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WO2017170425A1 (en) * 2016-03-31 2017-10-05 イビデン 株式会社 Honeycomb catalyst and manufacturing method for honeycomb catalyst

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