JPH09323039A - Method for catalytically reducing nitrogen oxide - Google Patents

Method for catalytically reducing nitrogen oxide

Info

Publication number
JPH09323039A
JPH09323039A JP8143997A JP14399796A JPH09323039A JP H09323039 A JPH09323039 A JP H09323039A JP 8143997 A JP8143997 A JP 8143997A JP 14399796 A JP14399796 A JP 14399796A JP H09323039 A JPH09323039 A JP H09323039A
Authority
JP
Japan
Prior art keywords
catalyst
exhaust gas
nitrogen
oxide
nitrogen oxides
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
JP8143997A
Other languages
Japanese (ja)
Other versions
JP3791968B2 (en
Inventor
Tadao Nakatsuji
忠夫 仲辻
Ritsu Yasukawa
律 安川
Keiichi Tabata
啓一 田畑
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.)
Sakai Chemical Industry Co Ltd
Japan Petroleum Energy Center JPEC
Original Assignee
Petroleum Energy Center PEC
Sakai Chemical Industry Co 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 Petroleum Energy Center PEC, Sakai Chemical Industry Co Ltd filed Critical Petroleum Energy Center PEC
Priority to JP14399796A priority Critical patent/JP3791968B2/en
Publication of JPH09323039A publication Critical patent/JPH09323039A/en
Application granted granted Critical
Publication of JP3791968B2 publication Critical patent/JP3791968B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for catalytically reducing the NOx in an exhaust gas stably and efficiently with hydrocarbons as a reducing agent even in coexistence of oxygen, SOx and moisture at a low temp. without using a large amt. of the reducing agent. SOLUTION: The NOx contained in an exhaust gas is catalytically reduced in the presence of a catalyst with hydrocarbons as a reducing agent. In this case, the exhaust gas is brought into contact with an NOx oxidizing catalyst to oxidize the nitrogen monoxide (NO) contained in the exhaust gas to nitrogen dioxide (NO2 ) in the first stage. Hydrocarbons are added to such an exgaust gas, and the exhaust gas is brought into contact with an NOx reducing catalyst selected from metallic rhodium and rhodium oxide to reduce the NOx to nitrogen in the second stage.

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、炭化水素を還元剤
として用いる窒素酸化物の接触還元方法に関し、詳しく
は、工場、自動車等から排出される排ガスの中に含まれ
る有害な窒素酸化物を安定して高い除去率にて還元除去
することができる窒素酸化物の接触還元方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for catalytic reduction of nitrogen oxides using hydrocarbons as a reducing agent, and more specifically, it removes harmful nitrogen oxides contained in exhaust gas discharged from factories, automobiles and the like. The present invention relates to a method for catalytic reduction of nitrogen oxides, which enables stable reduction and removal at a high removal rate.

【0002】[0002]

【従来の技術】従来、排ガス中に含まれる窒素酸化物
は、窒素酸化物を酸化した後、アルカリに吸収させる方
法や、アンモニア、水素、一酸化炭素、炭化水素等の還
元剤を用いて、窒素に変換する方法等によって除去され
ている。
2. Description of the Related Art Conventionally, nitrogen oxides contained in exhaust gas are obtained by oxidizing the nitrogen oxides and then absorbing them into an alkali, or by using a reducing agent such as ammonia, hydrogen, carbon monoxide, or a hydrocarbon. It has been removed by a method of converting to nitrogen.

【0003】しかしながら、前者の方法によれば、生成
するアルカリ廃液を処理して、公害の発生を防止する方
策が必要である。他方、後者の方法によれば、還元剤と
してアンモニアを用いるときは、これが排ガス中の硫黄
酸化物と反応して塩類を生成し、その結果、触媒の還元
活性が低下する問題がある。また、水素、一酸化炭素、
炭化水素等を還元剤として用いる場合でも、これらが低
濃度に存在する窒素酸化物よりも高濃度に存在する酸素
と反応するので、窒素酸化物を低減するためには、多量
の還元剤を必要とするという問題がある。
However, according to the former method, it is necessary to treat the produced alkaline waste liquid to prevent pollution. On the other hand, according to the latter method, when ammonia is used as the reducing agent, it reacts with the sulfur oxide in the exhaust gas to form salts, and as a result, the reduction activity of the catalyst is reduced. Also, hydrogen, carbon monoxide,
Even when using hydrocarbons and the like as reducing agents, a large amount of reducing agent is required to reduce nitrogen oxides because they react with oxygen present in higher concentrations than nitrogen oxides present in low concentrations. There is a problem that

【0004】このため、最近では、還元剤の不存在下に
窒素酸化物を触媒にて直接分解する方法も提案されてい
るが、しかし、従来、知られているそのような触媒は、
窒素酸化物の分解活性が低いために、実用に供し難いと
いう問題がある。
[0004] For this reason, recently, a method of directly decomposing nitrogen oxides with a catalyst in the absence of a reducing agent has been proposed. However, such a conventionally known catalyst has been proposed.
There is a problem that it is difficult to put into practical use due to low decomposition activity of nitrogen oxides.

【0005】また、炭化水素や含酸素化合物を還元剤と
して用いる新たな窒素酸化物接触還元用触媒として、H
型ゼオライトやCuイオン交換ZSM−5等が提案され
ており、なかでも、H型ZSM−5(SiO2 /Al2
3 モル比=30〜40)が最適であるとされている。
しかしながら、このようなH型ZSM−5でも、未だ十
分な還元活性を有するものとはいい難く、特に、ガス中
に水分が含まれるとき、ゼオライト構造体中のアルミニ
ウムが脱アルミニウムして、性能が急激に低下するの
で、一層高い還元活性を有し、更に、ガスが水分を含有
する場合にも、すぐれた耐久性を有する窒素酸化物接触
還元用触媒が要望されている。
Further, as a new catalyst for catalytic reduction of nitrogen oxides using a hydrocarbon or an oxygen-containing compound as a reducing agent, H
Zeolite and Cu ion exchange ZSM-5 have been proposed. Among them, H-type ZSM-5 (SiO 2 / Al 2
O 3 molar ratio = 30 to 40) is considered to be optimal.
However, even with such H-type ZSM-5, it is still difficult to say that the H-type ZSM-5 has a sufficient reducing activity. In particular, when moisture is contained in the gas, the aluminum in the zeolite structure is dealuminated and the performance is reduced. There is a demand for a catalyst for catalytic reduction of nitrogen oxides which has a higher reduction activity because of a rapid decrease and has excellent durability even when the gas contains moisture.

【0006】[0006]

【発明が解決しようとする課題】そこで、銀又は銀酸化
物を無機酸化物に担持させてなる触媒も提案されている
が、そのような触媒は、酸化活性が高く、窒素酸化物に
対する選択反応性が低いために、窒素酸化物の除去率が
低い。また、触媒が窒素酸化物の分解活性を有する温度
域が高いので、排ガス中の窒素酸化物を有効に分解する
には、排ガスを予め加熱することが必要であって、実用
化には問題がある。更に、銀又は銀酸化物を無機酸化物
に担持させてなる触媒は、硫黄酸化物の共存下での触媒
活性の劣化が著しいという問題もある(特開平5−31
7647号公報)。そのうえ、従来の窒素酸化物接触還
元用触媒は、一般に、耐熱性が十分ではなく、用途によ
っては、一層の耐熱性が強く要望されている。
Accordingly, a catalyst comprising silver or silver oxide supported on an inorganic oxide has been proposed. However, such a catalyst has a high oxidation activity and a selective reaction to nitrogen oxide. The removal rate of nitrogen oxides is low because of low properties. Further, since the temperature range in which the catalyst has a decomposition activity of nitrogen oxides is high, it is necessary to preheat the exhaust gas in order to effectively decompose the nitrogen oxides in the exhaust gas, which poses a problem in practical use. is there. Further, the catalyst in which silver or silver oxide is supported on an inorganic oxide has a problem that the catalytic activity is significantly deteriorated in the presence of sulfur oxide (Japanese Patent Laid-Open No. 5-31).
7647 publication). In addition, conventional catalysts for catalytic reduction of nitrogen oxides generally do not have sufficient heat resistance, and there is a strong demand for even higher heat resistance depending on the application.

【0007】そこで、本発明者らは、既に、固体酸担体
にアルミン酸銀を担持させてなる窒素酸化物接触還元用
触媒を提案しており(特願平7−306070号)、こ
の触媒は、上記問題点を改善しているものの、窒素酸化
物の還元率の点で、尚、十分とはいえない。
Therefore, the present inventors have already proposed a catalyst for catalytic reduction of nitrogen oxides, which comprises a solid acid carrier on which silver aluminate is supported (Japanese Patent Application No. 7-306070). Although the above problems are improved, the reduction rate of nitrogen oxides is still insufficient.

【0008】本発明は、上述したような事情に鑑みてな
されたものであって、その目的とするところは、炭化水
素を還元剤として用いる窒素酸化物の接触還元方法であ
って、酸素や硫黄酸化物や水分の共存下においても、多
量の還元剤を用いることなく、低温において排ガス中の
窒素酸化物を安定して且つ効率よく接触還元することが
できる窒素酸化物の接触還元方法を提供することにあ
る。
The present invention has been made in view of the above circumstances, and an object thereof is a catalytic reduction method of nitrogen oxides using a hydrocarbon as a reducing agent, such as oxygen and sulfur. Provided is a method for catalytic reduction of nitrogen oxides which can stably and efficiently catalytically reduce nitrogen oxides in exhaust gas at low temperature without using a large amount of reducing agent even in the presence of oxides and water. Especially.

【0009】[0009]

【課題を解決するための手段】本発明は、排ガスに含ま
れる窒素酸化物を触媒の存在下に還元剤として炭化水素
を用いて接触還元する方法において、第1段階として、
排ガスを窒素酸化物酸化触媒(以下、酸化触媒又は第1
触媒ということがある。)に接触させて、排ガスに含ま
れる一酸化窒素(NO)を二酸化窒素(NO2 )に酸化
し、次いで、このような排ガスに炭化水素を加え、第2
段階として、この排ガスをロジウム金属及びロジウム酸
化物から選ばれる窒素酸化物還元触媒(以下、還元触媒
又は第2触媒ということがある。)に接触させて、窒素
酸化物を窒素に還元することを特徴とする。
The present invention is a method for catalytically reducing nitrogen oxides contained in exhaust gas by using hydrocarbon as a reducing agent in the presence of a catalyst.
The exhaust gas is converted into a nitrogen oxide oxidation catalyst (hereinafter, the oxidation catalyst or the first
Sometimes called a catalyst. ) To oxidize nitric oxide (NO) contained in the exhaust gas into nitrogen dioxide (NO 2 ), and then add hydrocarbons to such exhaust gas,
In a step, the exhaust gas is brought into contact with a nitrogen oxide reduction catalyst (hereinafter sometimes referred to as a reduction catalyst or a second catalyst) selected from rhodium metal and rhodium oxide to reduce the nitrogen oxide to nitrogen. Characterize.

【0010】[0010]

【発明の実施の形態】本発明の方法によれば、第1段階
として、排ガスを窒素酸化物酸化触媒に接触させて、排
ガスに含まれる一酸化窒素(NO)を二酸化窒素(NO
2 )に酸化する。一酸化窒素に比べて、二酸化窒素は、
後述する還元触媒による還元反応において、還元剤であ
る炭化水素との選択反応性によりすぐれるので、第2段
階における窒素酸化物の接触還元に先立って、このよう
に、第1段階において、予め一酸化窒素を二酸化窒素に
酸化することによって、排ガスに含まれる窒素酸化物の
除去率を高めることができる。
According to the method of the present invention, as a first step, the exhaust gas is brought into contact with a nitrogen oxide oxidation catalyst so that nitric oxide (NO) contained in the exhaust gas is converted into nitrogen dioxide (NO).
2 ) to oxidize. Compared to nitric oxide, nitrogen dioxide
In the reduction reaction by the reduction catalyst described later, since it is superior due to the selective reactivity with the hydrocarbon that is the reducing agent, prior to the catalytic reduction of nitrogen oxides in the second step, in this way, in the first step, it is possible By oxidizing nitrogen oxide to nitrogen dioxide, the removal rate of nitrogen oxides contained in the exhaust gas can be increased.

【0011】上記酸化触媒、即ち、第1触媒としては、
特に、限定されるものではないが、好ましくは、白金、
マンガン、パラジウム、イリジウム、ルテニウム及び銅
から選ばれる金属又はその酸化物からなる触媒が用いら
れる。これら金属又はその酸化物は、通常、比表面積の
大きい酸化物、例えば、アルミナ、シリカ、シリカ−ア
ルミナ、ジルコニア、チタニア、ゼオライト等の固体酸
担体に担持されて用いられる。上記金属又はその酸化物
をこのような担体に担持させるには、従来より知られて
いるイオン交換法や含浸法等、適宜の方法によればよ
い。
As the above-mentioned oxidation catalyst, that is, the first catalyst,
Although not particularly limited, preferably platinum,
A catalyst composed of a metal selected from manganese, palladium, iridium, ruthenium and copper or an oxide thereof is used. These metals or oxides thereof are usually used by being supported on an oxide having a large specific surface area, for example, a solid acid carrier such as alumina, silica, silica-alumina, zirconia, titania or zeolite. In order to support the above metal or its oxide on such a carrier, an appropriate method such as a conventionally known ion exchange method or impregnation method may be used.

【0012】上記金属又はその酸化物の担体への担持
量、即ち、上記金属又はその酸化物と担体の重量に対す
る上記金属又はその酸化物の割合は、用いる金属種や触
媒が置かれる反応条件にもよるが、また、必ずしも限定
されるものではないが、通常、金属換算にて、0.001
〜10重量%の範囲であり、好ましくは、0.1〜5重量
%の範囲である。上記金属又はその酸化物の担体への担
持量が0.001重量%よりも少ないときは、上述したよ
うな一酸化窒素を二酸化窒素に酸化する能力が不十分で
ある。しかし、担持量が10重量%を越えても、一酸化
窒素を二酸化窒素に酸化する能力がそれに見合って増大
するものでもなく、経済性の点からも不利である。
The amount of the above-mentioned metal or its oxide supported on the carrier, that is, the ratio of the above-mentioned metal or its oxide to the weight of the above-mentioned metal or its oxide and the carrier depends on the metal species to be used and the reaction conditions under which the catalyst is placed. Although it is not limited to this, it is usually 0.001 in terms of metal.
It is in the range of 10 to 10% by weight, and preferably in the range of 0.1 to 5% by weight. When the amount of the above metal or its oxide supported on the carrier is less than 0.001% by weight, the above-described ability to oxidize nitric oxide to nitrogen dioxide is insufficient. However, even if the supported amount exceeds 10% by weight, the ability to oxidize nitric oxide to nitrogen dioxide does not increase correspondingly, which is also disadvantageous from the economical point of view.

【0013】第1段階において、一酸化窒素を含む排ガ
スをこのような第1触媒に接触させる際の空間速度は、
酸化率の観点からは、低ければ低いほどよいが、しか
し、一酸化窒素を実用的に効率よく酸化する観点から
は、通常、50000〜500000hr-1の範囲であ
る。
In the first stage, the space velocity at which the exhaust gas containing nitric oxide is brought into contact with such a first catalyst is
From the viewpoint of the oxidation rate, the lower the better, the better, but from the viewpoint of effectively oxidizing nitric oxide practically, it is usually in the range of 50,000 to 500,000 hr −1 .

【0014】本発明の方法によれば、このように、排ガ
スを第1触媒に接触させて、排ガスに含まれる一酸化窒
素を二酸化窒素とした後、このような排ガスに還元剤で
ある炭化水素を加え、これを第2触媒に接触させること
によって、上記二酸化窒素を効率よく窒素に還元するこ
とができ、延いては、排ガス中の窒素酸化物の除去率を
高めることができる。
According to the method of the present invention, the exhaust gas is brought into contact with the first catalyst in this manner to convert nitrogen monoxide contained in the exhaust gas into nitrogen dioxide, and then the hydrocarbon as a reducing agent is added to the exhaust gas. And by contacting it with the second catalyst, the nitrogen dioxide can be efficiently reduced to nitrogen, which in turn can increase the removal rate of nitrogen oxides in the exhaust gas.

【0015】上記炭化水素からなる還元剤としては、例
えば、気体状のものとして、メタン、エタン、プロパ
ン、プロピレン、ブチレン等の炭化水素ガス、液体状の
ものとして、ペンタン、ヘキサン、オクタン、ヘプタ
ン、ベンゼン、トルエン、キシレン等の単一成分系の炭
化水素、ガソリン、灯油、軽油、重油等の鉱油系炭化水
素等を用いることができる。特に、本発明においては、
上記したなかでも、エチレン、プロピレン、イソブチレ
ン、1−ブテン、2−ブテン等の低級アルケン、プロパ
ン、ブタン等の低級アルカン、軽油等が還元剤として好
ましく用いられる。これら炭化水素は、単独で用いても
よく、又は必要に応じて二種以上併用してもよい。
Examples of the reducing agent composed of the above hydrocarbons include hydrocarbon gases such as methane, ethane, propane, propylene and butylene as gaseous substances, and pentane, hexane, octane and heptane as liquid substances. Single-component hydrocarbons such as benzene, toluene, xylene, and mineral oil hydrocarbons such as gasoline, kerosene, light oil, and heavy oil can be used. In particular, in the present invention,
Among the above, lower alkenes such as ethylene, propylene, isobutylene, 1-butene and 2-butene, lower alkanes such as propane and butane, and light oil are preferably used as the reducing agent. These hydrocarbons may be used alone or in combination of two or more as needed.

【0016】上記還元剤としての炭化水素は、用いる具
体的な炭化水素によって異なるが、通常、排ガス中の窒
素酸化物(実質的に、一酸化窒素と二酸化窒素とからな
る。)に対するモル比にて、0.1〜2程度の範囲にて用
いられる。炭化水素の使用量が窒素酸化物に対するモル
比にて、0.1未満であるときは、窒素酸化物に対して十
分な還元活性を得ることができず、他方、モル比が2を
越えるときは、未反応の炭化水素の排出量が多くなるた
めに、窒素酸化物の接触還元処理の後に、これを回収す
るための後処理が必要となる。
The hydrocarbon as the reducing agent varies depending on the specific hydrocarbon used, but is usually in a molar ratio with respect to nitrogen oxides in the exhaust gas (substantially consisting of nitric oxide and nitrogen dioxide). Therefore, it is used in the range of about 0.1 to 2. When the amount of the hydrocarbon used is less than 0.1 in terms of the molar ratio to the nitrogen oxides, sufficient reduction activity for the nitrogen oxides cannot be obtained. On the other hand, when the molar ratio exceeds 2, Since a large amount of unreacted hydrocarbons is emitted, a post-treatment for recovering the nitrogen oxides after the catalytic reduction treatment of the nitrogen oxides is required.

【0017】尚、排ガス中に存在する燃料等の未燃焼物
乃至不完全燃焼生成物、即ち、炭化水素類やパティキュ
レート類等も還元剤として有効であり、これらも本発明
における炭化水素に含まれる。このことから、見方を変
えれば、本発明の方法は、排ガス中の炭化水素類やパテ
ィキュレート類等を減少させ、又は除去する方法として
も有用であるということができる。
Incidentally, unburned substances or incompletely burned products such as fuel existing in the exhaust gas, that is, hydrocarbons and particulates are also effective as the reducing agent, and these are also included in the hydrocarbon in the present invention. Be done. From this point of view, it can be said that the method of the present invention is also useful as a method for reducing or removing hydrocarbons and particulates in exhaust gas.

【0018】第2触媒は、ロジウム金属及びロジウム酸
化物から選ばれる。これらは、通常、比表面積の大きい
酸化物、例えば、アルミナ、シリカ、シリカ−アルミ
ナ、ジルコニア、チタニア、ゼオライト等の固体酸担体
に担持されて用いられる。ロジウム金属やロジウム酸化
物をこのような担体に担持させるには、第1触媒の場合
と同様に、従来より知られているイオン交換法や含浸法
等、適宜の方法によればよい。
The second catalyst is selected from rhodium metal and rhodium oxide. These are usually used by being supported on a solid acid carrier such as an oxide having a large specific surface area, for example, alumina, silica, silica-alumina, zirconia, titania, zeolite and the like. In order to support the rhodium metal or the rhodium oxide on such a carrier, an appropriate method such as an ion exchange method or an impregnation method known in the related art may be used as in the case of the first catalyst.

【0019】本発明においては、担体としては、上記し
たなかでは、特に、耐熱性にすぐれると共に、担持効果
にすぐれるアルミナが好ましく用いられる。アルミナの
なかでも、特開平7−171347号公報に記載されて
いるように、アルカリ金属及びアルカリ土類金属の含有
量が0.5重量%以下であり、径60オングストローム以
下の細孔から形成される細孔容積が0.06cm3 /g以
上、径80オングストローム以下の細孔から形成される
細孔容積が0.1cm3 /g以上であるアルミナが特に好ま
しく用いられる。このような細孔容積を有する多孔質の
アルミナは、還元剤の適度な酸化を促進し、これに担持
されているロジウム金属又はロジウム酸化物と協同し
て、窒素酸化物を効果的に接触還元することができる。
In the present invention, as the carrier, alumina among the above is particularly preferably used because it has excellent heat resistance and an excellent loading effect. Among alumina, as described in JP-A-7-171347, the content of alkali metal and alkaline earth metal is 0.5% by weight or less, and it is formed from pores having a diameter of 60 angstroms or less. that a pore volume of 0.06 cm 3 / g or more, a pore volume formed from the following pore diameters 80 Å are particularly preferably used alumina is 0.1 cm 3 / g or more. Porous alumina having such a pore volume promotes appropriate oxidation of the reducing agent, and cooperates with the rhodium metal or rhodium oxide supported on it to effectively catalytically reduce nitrogen oxides. can do.

【0020】このように、ロジウム金属又はロジウム酸
化物からなる第2触媒は、従来、知られている成形方法
によって、それ自体にて、又は担体に担持させた後、ハ
ニカム状、球状等の種々の形状に成形することができ
る。この成形の際に、成形助剤、成形体補強体、無機繊
維、有機バインダー等を適宜配合してもよい。また、第
2触媒は、予め成形された不活性な基材上にウオッシュ
・コート法等によって被覆担持させることもできる。上
記基材としては、例えば、コージェライトのような粘土
からなるハニカム構造体に担持させることができる。更
に、必要に応じて、従来、知られているその他の触媒の
任意の調製法によることもできる。
As described above, the second catalyst made of rhodium metal or rhodium oxide can be formed into a honeycomb shape, a spherical shape or the like by itself or after being supported on a carrier by a conventionally known molding method. Can be molded into the shape of. At the time of this molding, a molding aid, a molded body reinforcement, an inorganic fiber, an organic binder, and the like may be appropriately compounded. The second catalyst can also be supported by coating on a preformed inert base material by a wash coat method or the like. As the substrate, for example, it can be supported on a honeycomb structure made of clay such as cordierite. Further, if necessary, any other known method for preparing a catalyst may be used.

【0021】ロジウム金属又はロジウム酸化物の担体へ
の担持量は、0.01〜1重量%の範囲であることが好ま
しい。担持量が0.01重量%よりも少ないときは、窒素
酸化物の還元活性が十分でなく、他方、1重量%よりも
多いときは、酸化活性が高すぎて、選択性に劣ることと
なる。本発明によれば、ロジウム金属又はロジウム酸化
物の担体への担持量は、特に、0.05〜0.5重量%の範
囲が好ましい。
The amount of the rhodium metal or rhodium oxide supported on the carrier is preferably 0.01 to 1% by weight. When the supported amount is less than 0.01% by weight, the reducing activity of nitrogen oxides is not sufficient, while when it is more than 1% by weight, the oxidizing activity is too high, resulting in poor selectivity. . According to the present invention, the amount of rhodium metal or rhodium oxide loaded on the carrier is particularly preferably in the range of 0.05 to 0.5% by weight.

【0022】第2段階において、主として二酸化窒素か
らなる窒素酸化物と共に炭化水素を含む排ガスをこのよ
うな第2触媒に接触させる際の空間速度は、通常、50
00〜50000hr-1の範囲である。第2段階における
触媒は、第1段階における触媒に比べて、酸化活性が小
さく、窒素酸化物との選択性にすぐれるので、高い脱硝
率を得るには、空間速度は小さいことが好ましいが、通
常、実用上、上記の範囲の空間速度が採用される。 本
発明の方法によれば、第1段階及び第2段階における反
応温度は、150〜450℃の範囲である。必要に応じ
て、第1段階及び第2段階において、反応温度を変えて
もよい。
In the second stage, the space velocity at which the exhaust gas containing hydrocarbons together with nitrogen oxides mainly consisting of nitrogen dioxide is brought into contact with such a second catalyst is usually 50.
The range is from 00 to 50,000 hr -1 . The catalyst in the second stage has a smaller oxidizing activity and a better selectivity with respect to nitrogen oxides than the catalyst in the first stage. Therefore, in order to obtain a high denitration rate, it is preferable that the space velocity is small. Usually, practically, the space velocity in the above range is adopted. According to the method of the present invention, the reaction temperature in the first step and the second step is in the range of 150 to 450 ° C. If necessary, the reaction temperature may be changed in the first stage and the second stage.

【0023】本発明によれば、上述したように、第1段
階において、排ガスを酸化触媒に接触させて、排ガスに
含まれる一酸化窒素を二酸化窒素に酸化し、次いで、こ
のような排ガスに炭化水素を加え、第2段階として、こ
の排ガスをロジウム金属及びロジウム酸化物から選ばれ
る窒素酸化物還元触媒に接触させて、二酸化窒素を窒素
に還元するので、低い温度域においても、窒素酸化物を
安定して且つ効率よく還元分解することができる。
According to the present invention, as described above, in the first step, the exhaust gas is brought into contact with the oxidation catalyst to oxidize the nitric oxide contained in the exhaust gas into nitrogen dioxide, and then the exhaust gas is carbonized. Hydrogen is added, and as a second step, this exhaust gas is brought into contact with a nitrogen oxide reduction catalyst selected from rhodium metal and rhodium oxide to reduce nitrogen dioxide to nitrogen, so that nitrogen oxides are removed even in a low temperature range. Stable and efficient reductive decomposition can be performed.

【0024】[0024]

【実施例】以下に各段階のための触媒の調製例と共に実
施例を挙げて本発明を説明するが、本発明はこれら実施
例により何ら限定されるものではない。
EXAMPLES The present invention will be described below with reference to examples along with examples of catalyst preparation for each step, but the present invention is not limited to these examples.

【0025】(1)第1触媒の調製 調製例1 塩化白金酸(H2 PtCl6 ・6H2 O)5.31gをイ
オン交換水100mLに溶解させた。予め120℃にて
24時間乾燥させた平均粒径3mmのγ−アルミナ(住
友化学工業(株)製KHA−24)100mLを上記塩
化白金酸水溶液に投入し、30分間攪拌して、アルミナ
の細孔内に塩化白金酸水溶液を十分に含浸させた。
(1) Preparation of First Catalyst Preparation Example 1 5.31 g of chloroplatinic acid (H 2 PtCl 6 .6H 2 O) was dissolved in 100 mL of deionized water. 100 mL of γ-alumina (KHA-24 manufactured by Sumitomo Chemical Co., Ltd.) having an average particle diameter of 3 mm, which had been dried in advance at 120 ° C. for 24 hours, was added to the above chloroplatinic acid aqueous solution and stirred for 30 minutes to form alumina fine particles. The pores were thoroughly impregnated with a chloroplatinic acid aqueous solution.

【0026】次いで、γ−アルミナを塩化白金酸水溶液
から分離し、表面に付着した過剰の水溶液を除去した
後、100℃で12時間乾燥させ、更に、空気中、50
0℃で焼成して、白金をγ−アルミナに1重量%の担持
量で担持させた触媒(A−1)を得た。
Next, γ-alumina was separated from the chloroplatinic acid aqueous solution, the excess aqueous solution adhering to the surface was removed, and then dried at 100 ° C. for 12 hours, and further, in air, 50
It was calcined at 0 ° C. to obtain a catalyst (A-1) in which platinum was supported on γ-alumina in a supported amount of 1% by weight.

【0027】調製例2 塩化白金酸に代えて、硝酸マンガン2.87g用いた以外
は、調製例1と同様にして、二酸化マンガンをγ−アル
ミナに1重量%の担持量で担持させた触媒(A−2)を
得た。
Preparation Example 2 A catalyst prepared by supporting manganese dioxide on γ-alumina in an amount of 1% by weight was carried out in the same manner as in Preparation Example 1 except that 2.87 g of manganese nitrate was used instead of chloroplatinic acid. A-2) was obtained.

【0028】調製例3 塩化白金酸に代えて、塩化パラジウム(PdCl2 )3.
3gを用いた以外は、調製例1と同様にして、パラジウ
ムをγ−アルミナに1重量%の担持量で担持させた触媒
(A−3)を得た。
Preparation Example 3 Instead of chloroplatinic acid, palladium chloride (PdCl 2 ) 3.
A catalyst (A-3) was obtained in which palladium was supported on γ-alumina in a supported amount of 1% by weight in the same manner as in Preparation Example 1 except that 3 g was used.

【0029】調製例4 塩化白金酸に代えて、塩化イリジウム(IrCl4 )1
7.4gを用いた以外は、調製例1と同様にして、イリジ
ウムをγ−アルミナに5重量%の担持量で担持させた触
媒(A−4)を得た。
Preparation Example 4 Instead of chloroplatinic acid, iridium chloride (IrCl 4 ) 1
A catalyst (A-4) was obtained in which iridium was supported on γ-alumina in a supported amount of 5% by weight in the same manner as in Preparation Example 1 except that 7.4 g was used.

【0030】調製例5 塩化白金酸に代えて、塩化ルテニウム(RuCl3 )4.
1gを用いた以外は、調製例1と同様にして、ルテニウ
ムをγ−アルミナに1重量%の担持量で担持させた触媒
(A−5)を得た。
Preparation Example 5 Instead of chloroplatinic acid, ruthenium chloride (RuCl 3 ) 4.
A catalyst (A-5) was obtained in which ruthenium was loaded on γ-alumina in a loading amount of 1% by weight, in the same manner as in Preparation Example 1 except that 1 g was used.

【0031】調製例6 塩化白金酸に代えて、硝酸銅(Cu(NO3 2 ・3H
2 O)2.42gを用いた以外は、調製例1と同様にし
て、酸化第二銅をγ−アルミナに1重量%の担持量で担
持させた触媒(A−6)を得た。
[0031] Instead of Preparation 6 chloroplatinic acid, copper nitrate (Cu (NO 3) 2 · 3H
2 O) 2.42 g was used, and in the same manner as in Preparation Example 1, a catalyst (A-6) was obtained in which cupric oxide was supported on γ-alumina in a supported amount of 1% by weight.

【0032】(2)第2触媒の調製 調製例7 硝酸ロジウム(Rh(NO3 2 ・2H2 O)0.64g
をイオン交換水100mLに溶解させた。予め120℃
で24時間乾燥させた平均粒径3mmのγ−アルミナ
(住友化学工業(株)製KHA−24)100mLを上
記硝酸ロジウム水溶液に投入し、30分間攪拌して、ア
ルミナの細孔内に硝酸ロジウム水溶液を十分に含浸させ
た。
(2) Preparation of Second Catalyst Preparation Example 7 Rhodium Nitrate (Rh (NO 3 ) 2 .2H 2 O) 0.64 g
Was dissolved in 100 mL of ion-exchanged water. 120 ° C in advance
100 mL of γ-alumina (KHA-24 manufactured by Sumitomo Chemical Co., Ltd.) having an average particle size of 3 mm dried for 24 hours was charged into the above rhodium nitrate aqueous solution, stirred for 30 minutes, and the rhodium nitrate in the pores of the alumina The aqueous solution was thoroughly impregnated.

【0033】次いで、γ−アルミナを硝酸ロジウム水溶
液から分離し、表面に付着した過剰の水溶液を除去した
後、100℃で12時間乾燥させ、更に、空気中、50
0℃で焼成して、ロジウムをγ−アルミナに0.1重量%
の担持量で担持させた触媒(B−1)を得た。
Then, γ-alumina was separated from the rhodium nitrate aqueous solution, and after removing the excess aqueous solution adhering to the surface, it was dried at 100 ° C. for 12 hours, and further, in air, 50
0.1% by weight of rhodium in γ-alumina by firing at 0 ° C
A catalyst (B-1) supported in the supported amount was obtained.

【0034】調製例8 調製例7において、硝酸ロジウム0.06gを用いた以外
は、調製例8と同様にして、ロジウムをγ−アルミナに
0.01重量%の担持量で担持させた触媒(B−2)を得
た。
Preparation Example 8 Rhodium was converted to γ-alumina in the same manner as in Preparation Example 8 except that 0.06 g of rhodium nitrate was used in Preparation Example 7.
A catalyst (B-2) supported in an amount of 0.01% by weight was obtained.

【0035】調製例9 調製例7において、硝酸ロジウム3.20gを用いた以外
は、調製例8と同様にして、ロジウムをγ−アルミナに
0.5重量%の担持量で担持させた触媒(B−3)を得
た。
Preparation Example 9 Rhodium was converted into γ-alumina in the same manner as in Preparation Example 8 except that 3.20 g of rhodium nitrate was used in Preparation Example 7.
A catalyst (B-3) supported in an amount of 0.5% by weight was obtained.

【0036】調製例10 調製例7において、硝酸ロジウム6.40gを用いた以外
は、調製例8と同様にして、ロジウムをγ−アルミナに
1.0重量%の担持量で担持させた触媒(B−4)を得
た。
Preparation Example 10 Rhodium was converted into γ-alumina in the same manner as in Preparation Example 8 except that 6.40 g of rhodium nitrate was used in Preparation Example 7.
A catalyst (B-4) supported in an amount of 1.0% by weight was obtained.

【0037】実施例1〜11(評価試験) 下記の組成を有するガスを第1段階にて第1触媒(A−
1〜6)にて処理した後、このガスに還元剤(炭化水
素)を加え、第2段階にて第2触媒(B−1〜4)にて
処理して、窒素酸化物含有ガスの窒素酸化物接触還元を
行ない、第1段階において、一酸化窒素の二酸化窒素へ
の転化率と、第2段階の後の窒素酸化物の除去率とをそ
れぞれケミカルルミネッセンス法にて求めた。結果を表
1及び表2に示す。
Examples 1 to 11 (Evaluation test) A gas having the following composition was used in the first stage in the first catalyst (A-
1 to 6), then a reducing agent (hydrocarbon) is added to this gas, and the gas is treated with the second catalyst (B-1 to 4) in the second stage to obtain nitrogen gas containing nitrogen oxides. Oxide catalytic reduction was performed, and in the first step, the conversion rate of nitric oxide to nitrogen dioxide and the removal rate of nitrogen oxides after the second step were determined by the chemiluminescence method. The results are shown in Tables 1 and 2.

【0038】(試験条件) (1)ガス組成(第1段階) NO 500ppm O2 10容量% 水 6容量% 窒素 残部 (2)ガス組成(第2段階) 第1段階で処理したガスに還元剤(炭化水素)を500
ppm加えた。還元剤として軽油を用いた場合、軽油は
C換算でC12とした。) (3)空間速度 第1段階 50000、100000又は20000
0(hr-1) 第2段階 20000又は50000(hr-1) (4)反応温度 250℃、300℃、350℃、
400℃又は450℃
(Test conditions) (1) Gas composition (first step) NO 500ppm O 2 10 volume% water 6 volume% nitrogen balance (2) Gas composition (second step) Gas treated in the first step and reducing agent (Hydrocarbon) 500
ppm was added. When light oil was used as the reducing agent, the light oil was C12 in terms of C. ) (3) Space velocity 1st stage 50000, 100000 or 20000
0 (hr -1 ) 2nd stage 20000 or 50000 (hr -1 ) (4) Reaction temperature 250 ° C, 300 ° C, 350 ° C,
400 ° C or 450 ° C

【0039】比較例1〜4(評価試験) 窒素酸化物含有ガスを第1段階(窒素酸化物含有ガスに
還元剤を加えた後、酸化触媒でのみ処理する。)か、又
は第2段階(窒素酸化物含有ガスに還元剤を加えた後、
還元触媒でのみ処理する。)のいずれか一方のみで処理
した以外は、実施例と同様にして、窒素酸化物含有ガス
の窒素酸化物接触還元を行ない、窒素酸化物含有ガスを
第1段階のみで処理した場合には、一酸化窒素への二酸
化窒素への転化率を、また、窒素酸化物含有ガスを第2
段階のみで処理した場合には、窒素酸化物の除去率をそ
れぞれケミカルルミネッセンス法にて求めた。結果を表
1及び表2に示す。
Comparative Examples 1 to 4 (Evaluation Test) The nitrogen oxide-containing gas was treated in the first stage (after adding the reducing agent to the nitrogen oxide-containing gas, then treated only with the oxidation catalyst) or in the second stage ( After adding the reducing agent to the nitrogen oxide-containing gas,
Treat with reducing catalyst only. ), Except that only one of the above) was treated, catalytic reduction of nitrogen oxide-containing gas was carried out in the same manner as in Example, and when the nitrogen oxide-containing gas was treated only in the first stage, The conversion of nitrogen dioxide to nitric oxide and the nitrogen oxide containing gas
When the treatment was performed only in stages, the removal rate of nitrogen oxides was obtained by the chemiluminescence method. The results are shown in Tables 1 and 2.

【0040】[0040]

【表1】 [Table 1]

【0041】[0041]

【表2】 [Table 2]

【0042】[0042]

【発明の効果】表1及び表2に示す結果から明らかなよ
うに、本発明の方法によれば、酸素や硫黄酸化物や水分
の共存下においても、多量の還元剤を用いることなく、
低い温度域において、排ガス中の窒素酸化物を安定して
且つ効率よく接触還元することができる。
As is clear from the results shown in Tables 1 and 2, according to the method of the present invention, even in the presence of oxygen, sulfur oxides and water, a large amount of reducing agent is not used.
In a low temperature range, nitrogen oxides in exhaust gas can be stably and efficiently catalytically reduced.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01J 23/46 301 B01J 23/46 311A 311 23/72 A 23/72 B01D 53/36 102B 102G (72)発明者 田畑 啓一 大阪府堺市戎島町5丁1番地 堺化学工業 株式会社中央研究所内─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 6 Identification number Office reference number FI technical display location B01J 23/46 301 B01J 23/46 311A 311 23/72 A 23/72 B01D 53/36 102B 102G ( 72) Inventor Keiichi Tabata 5-1, Ebishima-cho, Sakai City, Osaka Prefecture Central Research Laboratory, Sakai Chemical Industry Co., Ltd.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】排ガスに含まれる窒素酸化物を触媒の存在
下に還元剤として炭化水素を用いて接触還元する方法に
おいて、第1段階として、排ガスを窒素酸化物酸化触媒
に接触させて、排ガスに含まれる一酸化窒素(NO)を
二酸化窒素(NO2 )に酸化し、次いで、このような排
ガスに炭化水素を加え、第2段階として、この排ガスを
ロジウム金属及びロジウム酸化物から選ばれる窒素酸化
物還元触媒に接触させて、窒素酸化物を窒素に還元する
ことを特徴とする窒素酸化物接の触還元方法。
1. A method for catalytically reducing nitrogen oxides contained in exhaust gas by using hydrocarbon as a reducing agent in the presence of a catalyst, wherein the exhaust gas is brought into contact with a nitrogen oxide oxidation catalyst as a first step. Is oxidized to nitrogen dioxide (NO 2 ), then hydrocarbon is added to such exhaust gas, and as a second step, this exhaust gas is treated with nitrogen selected from rhodium metal and rhodium oxide. A catalytic reduction method for contacting nitrogen oxides, which comprises contacting an oxide reduction catalyst to reduce nitrogen oxides to nitrogen.
【請求項2】窒素酸化物酸化触媒が白金、マンガン、パ
ラジウム、イリジウム、ルテニウム及び銅から選ばれる
金属又はその酸化物からなる触媒である請求項1に記載
の方法。
2. The method according to claim 1, wherein the nitrogen oxide oxidation catalyst is a catalyst composed of a metal selected from platinum, manganese, palladium, iridium, ruthenium and copper or an oxide thereof.
【請求項3】炭化水素が軽油である請求項1に記載の方
法。
3. The method according to claim 1, wherein the hydrocarbon is light oil.
【請求項4】第1段階及び第2段階において、150〜
450℃の範囲の温度で排ガスを触媒に接触させる請求
項1又は2に記載の方法。
4. The method according to claim 1, wherein in the first and second stages,
The method according to claim 1 or 2, wherein the exhaust gas is brought into contact with the catalyst at a temperature in the range of 450 ° C.
JP14399796A 1996-06-06 1996-06-06 Method for catalytic reduction of nitrogen oxides Expired - Fee Related JP3791968B2 (en)

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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000262863A (en) * 1999-03-17 2000-09-26 Jisedai Haigas Shokubai Kenkyusho:Kk Exhaust gas cleaning catalyst combination device
WO2002007879A1 (en) * 2000-07-24 2002-01-31 Toyota Jidosha Kabushiki Kaisha Particulate burning catalyst
JP2008155204A (en) * 2006-11-29 2008-07-10 Ict:Kk Oxidation catalyst and exhaust gas purification system using the same
US7781367B2 (en) 2006-12-05 2010-08-24 Tanaka Kikinzoku Kogyo K.K. Exhaust gas cleaning catalyst and process for producing the same
JP2012038565A (en) * 2010-08-06 2012-02-23 Gs Yuasa Corp Fuel cell use catalyst-carrying powder manufacturing method, fuel cell use electrode manufacturing method, and fuel cell use electrode
JP2012516228A (en) * 2009-01-28 2012-07-19 ズード−ケミー アーゲー Diesel oxidation catalyst with excellent activity at low temperatures

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000262863A (en) * 1999-03-17 2000-09-26 Jisedai Haigas Shokubai Kenkyusho:Kk Exhaust gas cleaning catalyst combination device
WO2002007879A1 (en) * 2000-07-24 2002-01-31 Toyota Jidosha Kabushiki Kaisha Particulate burning catalyst
US7138353B2 (en) 2000-07-24 2006-11-21 Toyota Jidosha Kabushiki Kaisha Particulate burning catalyst
JP2008155204A (en) * 2006-11-29 2008-07-10 Ict:Kk Oxidation catalyst and exhaust gas purification system using the same
JP2013056336A (en) * 2006-11-29 2013-03-28 Ict:Kk Oxidation catalyst and exhaust-gas purification system using the same
US7781367B2 (en) 2006-12-05 2010-08-24 Tanaka Kikinzoku Kogyo K.K. Exhaust gas cleaning catalyst and process for producing the same
JP2012516228A (en) * 2009-01-28 2012-07-19 ズード−ケミー アーゲー Diesel oxidation catalyst with excellent activity at low temperatures
JP2012038565A (en) * 2010-08-06 2012-02-23 Gs Yuasa Corp Fuel cell use catalyst-carrying powder manufacturing method, fuel cell use electrode manufacturing method, and fuel cell use electrode

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