JP2002253969A - Catalyst for purifying waste gas and method of purifying waste gas - Google Patents

Catalyst for purifying waste gas and method of purifying waste gas

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Publication number
JP2002253969A
JP2002253969A JP2001058623A JP2001058623A JP2002253969A JP 2002253969 A JP2002253969 A JP 2002253969A JP 2001058623 A JP2001058623 A JP 2001058623A JP 2001058623 A JP2001058623 A JP 2001058623A JP 2002253969 A JP2002253969 A JP 2002253969A
Authority
JP
Japan
Prior art keywords
catalyst
tin oxide
palladium
exhaust gas
hours
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2001058623A
Other languages
Japanese (ja)
Inventor
Hirofumi Otsuka
浩文 大塚
Taketoku Hirano
竹徳 平野
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.)
Osaka Gas Co Ltd
Original Assignee
Osaka Gas 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 Osaka Gas Co Ltd filed Critical Osaka Gas Co Ltd
Priority to JP2001058623A priority Critical patent/JP2002253969A/en
Publication of JP2002253969A publication Critical patent/JP2002253969A/en
Pending legal-status Critical Current

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

Abstract

PROBLEM TO BE SOLVED: To provide a purifying technique of hydrocarbon in a waste gas containing methane and excess oxygen. SOLUTION: The catalyst for purifying the waste gas is for decomposing hydrocarbon contained in the waste gas containing methane and excess oxygen and is formed by supporting palladium on tin oxide.

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、酸素を過剰に含み
メタンを含有する排ガス中の炭化水素の浄化触媒および
該触媒を用いた排ガスの浄化方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a catalyst for purifying hydrocarbons in exhaust gas containing excess oxygen and containing methane, and a method for purifying exhaust gas using the catalyst.

【0002】本発明において、「酸素を過剰に含む(燃
焼)排ガス」とは、本発明触媒に接触させる被処理ガス
(排ガス)が、そこに含まれる炭化水素、一酸化炭素など
の還元性成分を完全に酸化するのに必要な量以上の酸
素、窒素酸化物などの酸化性成分を含むガスであること
を意味する。
In the present invention, the term “exhaust gas containing excessive oxygen (combustion)” refers to the gas to be treated brought into contact with the catalyst of the present invention.
(Exhaust gas) means a gas containing oxygen and nitrogen oxides and other oxidizing components in an amount greater than that necessary to completely oxidize the reducing components such as hydrocarbons and carbon monoxide contained therein. I do.

【0003】[0003]

【従来の技術】排ガス中の炭化水素の酸化除去触媒とし
て、白金やパラジウムなどの白金族金属を担持した触媒
が高い性能を示すことが知られている。例えば、特開昭
51-106691号公報には、アルミナ担体に白金とパラジウ
ムを担持した排ガス浄化用触媒が開示されている。
2. Description of the Related Art It is known that a catalyst carrying a platinum group metal such as platinum or palladium exhibits high performance as a catalyst for oxidizing and removing hydrocarbons in exhaust gas. For example,
JP-A-51-106691 discloses an exhaust gas purifying catalyst in which platinum and palladium are supported on an alumina carrier.

【0004】しかし、このような触媒を用いても、天然
ガスの燃焼排ガスのようにメタンが炭化水素の主成分で
ある場合には,メタンが高い化学的安定性を有するため
に十分な浄化率が得られないという問題がある。
However, even when such a catalyst is used, when methane is a main component of hydrocarbons, such as the combustion exhaust gas of natural gas, a sufficient purification rate is required because methane has high chemical stability. There is a problem that can not be obtained.

【0005】燃焼排ガスの中には、触媒活性低下要因で
ある硫黄酸化物および反応阻害物質である水蒸気が必然
的に含まれるので、触媒活性は短時間内に低下する。灯
油、軽油などの石油系燃料には、硫黄化合物が含まれて
いる。さらに、本来硫黄化合物をほとんど含まない天然
ガス由来の燃料、例えば我が国で供給されている都市ガ
スであっても、付臭剤として硫黄化合物が添加されてい
る。これらの硫黄化合物は、燃焼によって硫黄酸化物を
生成する。
[0005] Since the combustion exhaust gas inevitably contains sulfur oxides, which are a factor for reducing the catalytic activity, and steam, which is a reaction inhibitor, the catalytic activity is reduced within a short time. Petroleum fuels such as kerosene and light oil contain sulfur compounds. Further, even natural gas-derived fuels which essentially contain no sulfur compounds, for example, city gas supplied in Japan, also contain a sulfur compound as an odorant. These sulfur compounds produce sulfur oxides by combustion.

【0006】例えば、ランパート(Lampert)らは、パラ
ジウム触媒を用いてメタン酸化を行った場合に、わずか
に0.1ppmの二酸化硫黄が存在するだけで、数時間内にそ
の触媒活性がほとんど失われることを示し、硫黄酸化物
の存在が触媒活性に著しい悪影響を与えることを明らか
にしている(アプライドキャタリシスB:Applied Cataly
sis B: Environmental, vol.14, pp211-223(1997))。
For example, Lampert et al. Found that when methane oxidation was carried out using a palladium catalyst, only 0.1 ppm of sulfur dioxide was present, and almost no catalytic activity was lost within a few hours. Which shows that the presence of sulfur oxides has a significant adverse effect on the catalytic activity (Applied Catalysis B: Applied Cataly
sis B: Environmental, vol.14, pp211-223 (1997)).

【0007】また、山本らは、アルミナに白金及びパラ
ジウムを担持した触媒を用いた都市ガス燃料の排ガス中
の炭化水素の酸化除去の結果を報告しているが、100時
間程度の間に顕著な活性の低下が見られる(平成8年度
触媒研究発表会講演予稿集(平成8年9月13日発行)。
Further, Yamamoto et al. Reported the results of oxidative removal of hydrocarbons in the exhaust gas of city gas fuel using a catalyst in which platinum and palladium were supported on alumina. A decrease in activity is seen (Preliminary proceedings of the 1996 Catalyst Research Conference (published September 13, 1996).

【0008】さらに、特開平8-332392号公報は、酸素過
剰な排ガス中の低濃度炭化水素用酸化触媒として、ハニ
カム基材にアルミナ担体を介して7g/l以上のパラジウム
および3〜20 g/lの白金を担持した触媒を開示してい
る。
Further, Japanese Patent Application Laid-Open No. 8-332392 discloses an oxidation catalyst for low-concentration hydrocarbons in an exhaust gas containing excess oxygen, comprising 7 g / l or more of palladium and 3 to 20 g / l on a honeycomb substrate through an alumina carrier. Disclosed are catalysts carrying l platinum.

【0009】しかし、この触媒を用いても、長期にわた
る耐久性は十分ではなく、活性の経時的な劣化が避けら
れない。
However, even if this catalyst is used, long-term durability is not sufficient, and deterioration of the activity with time cannot be avoided.

【0010】このように、従来技術の大きな問題点とし
て、メタンに対して高い除去率が得られないこと、硫黄
酸化物が共存するような条件で除去率が経時的に大きく
低下することなどが挙げられる。
As described above, the major problems of the prior art are that a high removal rate for methane cannot be obtained, and that the removal rate greatly decreases with time under conditions where sulfur oxides coexist. No.

【0011】このような実状を鑑みて、特開2000-33266
公報には、パラジウムまたはパラジウムと白金とを担持
した酸化スズが、硫黄酸化物共存下でも高いメタン酸化
活性を維持する触媒として開示されている。
In view of such a situation, Japanese Patent Application Laid-Open No. 2000-33266
The publication discloses palladium or tin oxide carrying palladium and platinum as a catalyst that maintains high methane oxidation activity even in the presence of sulfur oxide.

【0012】しかしながら、この触媒を用いても、特に
約400℃以下の低温域で高いメタン除去率を得るために
は、多くの触媒量を要する。
However, even if this catalyst is used, a large amount of catalyst is required in order to obtain a high methane removal rate particularly in a low temperature range of about 400 ° C. or lower.

【0013】[0013]

【発明が解決しようとする課題】本発明は、かかる状況
に鑑みて行われたものであって、酸素を過剰に含み、メ
タンを含有する排ガス中の炭化水素の浄化において、比
較的低温度においても高い活性を有する触媒および触媒
を用いた浄化方法を提供することを目的とする。
SUMMARY OF THE INVENTION The present invention has been made in view of the above circumstances, and is intended to purify hydrocarbons in exhaust gas containing excess oxygen and containing methane at relatively low temperatures. It is another object of the present invention to provide a catalyst having a high activity and a purification method using the catalyst.

【0014】[0014]

【課題を解決するための手段】発明者は、鋭意検討を重
ねた結果、前記特開2000-33266公報と同様に、パラジウ
ム或いはパラジウムおよび白金を活性金属として使用し
た場合に、酸化スズに替えて強酸化処理を施した酸化ス
ズを担体として用いることによって、400℃程度の低温
度においても、顕著に高いメタン酸化活性を有する触媒
が得られることを見出した。また、この触媒が、水蒸気
や硫黄酸化物の共存する燃焼排ガスの条件下においても
安定して高いメタン酸化能を維持することを見出した。
Means for Solving the Problems As a result of intensive studies, the inventor has found that, as in the case of Japanese Patent Application Laid-Open No. 2000-33266, when palladium or palladium and platinum are used as active metals, tin oxide is used instead of tin oxide. It has been found that a catalyst having remarkably high methane oxidation activity can be obtained even at a low temperature of about 400 ° C. by using tin oxide subjected to strong oxidation treatment as a carrier. In addition, they have found that this catalyst stably maintains a high methane oxidizing ability even under conditions of combustion exhaust gas in which steam and sulfur oxides coexist.

【0015】本発明は、かかる知見に基づきなされたも
のであり、下記の排ガス浄化用触媒および排ガス浄化方
法を提供する。 1.メタンを含有し酸素を過剰に含む燃焼排ガス中の炭
化水素の浄化用触媒であって、強酸化処理した酸化スズ
にパラジウムを担持した触媒。 2.メタンを含有し酸素を過剰に含む燃焼排ガス中の炭
化水素の浄化用触媒であって、強酸化処理した酸化スズ
にパラジウムおよび白金を担持した触媒。 3.メタンを含有し酸素を過剰に含む燃焼排ガス中の炭
化水素の浄化方法であって、強酸化処理した酸化スズに
パラジウムを担持した触媒を用いる浄化方法。 4.メタンを含有し酸素を過剰に含む燃焼排ガス中の炭
化水素の浄化方法であって、強酸化処理した酸化スズに
パラジウムおよび白金を担持した触媒を用いる浄化方
法。
The present invention has been made based on such findings, and provides the following exhaust gas purifying catalyst and exhaust gas purifying method. 1. A catalyst for purifying hydrocarbons in a combustion exhaust gas containing methane and excess oxygen, wherein palladium is supported on tin oxide that has been subjected to strong oxidation treatment. 2. A catalyst for purifying hydrocarbons in a combustion exhaust gas containing methane and containing excess oxygen, wherein palladium and platinum are supported on strongly oxidized tin oxide. 3. A method for purifying hydrocarbons in a combustion exhaust gas containing methane and containing an excessive amount of oxygen, wherein the method uses a catalyst in which palladium is supported on tin oxide that has been subjected to strong oxidation treatment. 4. A method for purifying hydrocarbons in a combustion exhaust gas containing methane and containing an excessive amount of oxygen, the method comprising using a catalyst in which palladium and platinum are supported on strongly oxidized tin oxide.

【0016】[0016]

【発明の実施の形態】本発明の触媒は、強酸化処理した
酸化スズ(SnO2)にパラジウム、またはパラジウムと白金
の両方を担持した触媒である。
BEST MODE FOR CARRYING OUT THE INVENTION The catalyst of the present invention is a catalyst in which palladium or both palladium and platinum are supported on tin oxide (SnO 2 ) which has been subjected to a strong oxidation treatment.

【0017】酸化スズの強酸化処理として、公知の方法
を適用できる。例えば、「日野誠、荒田一志、表面、28
巻481頁(1990年)」、「日野誠、荒田一志、表面、34巻51
頁(1996年)」などに記載されている方法を例示できる。
As the strong oxidation treatment of tin oxide, a known method can be applied. For example, "Makoto Hino, Kazushi Arata, Surface, 28
Volume 481 (1990) '', Makoto Hino, Kazushi Arata, Surface, 34, 51
Page (1996) "and the like.

【0018】代表的な強酸化処理として、以下の方法を
例示できる。水酸化スズ(Sn(OH)4)を硫酸アンモニウム
水溶液(硫酸アンモニウムに含まれる硫黄のSn(OH)4
対する重量比が、0.5〜8%程度(好ましくは3〜6%程
度))に含浸し、1〜20時間程度(好ましくは3〜10時間
程度)保持した後、蒸発乾固する。その後、空気中など
の酸化雰囲気下において、400〜600℃程度(好ましくは
500〜550℃程度)で1〜20時間程度(好ましくは3〜10時
間程度)焼成することによって強酸化処理を施した酸化
スズを得る。なお、水酸化スズの状態で硫酸イオンと接
触させて処理することが必要であり、水酸化スズを一旦
焼成するなどして酸化スズとして結晶化させたあとや、
通常の酸化スズを用いて前記のような処理を施しても、
本発明の効果は得られない。
The following method can be exemplified as a typical strong oxidation treatment. Impregnating tin hydroxide (Sn (OH) 4 ) with an aqueous solution of ammonium sulfate (the weight ratio of sulfur contained in ammonium sulfate to Sn (OH) 4 is about 0.5 to 8% (preferably about 3 to 6%)) After holding for about 20 hours (preferably about 3 to 10 hours), evaporate to dryness. Then, in an oxidizing atmosphere such as air, about 400 to 600 ° C. (preferably
By baking at about 500 to 550 ° C. for about 1 to 20 hours (preferably about 3 to 10 hours), tin oxide subjected to strong oxidation treatment is obtained. In addition, it is necessary to perform treatment by contacting with sulfuric acid ions in the state of tin hydroxide.
Even if the above treatment is performed using ordinary tin oxide,
The effect of the present invention cannot be obtained.

【0019】水酸化スズ(Sn(OH)4)の調製法として、以
下の方法を例示できる。塩化スズ(SnCl4)、硫酸スズ(Sn
(SO4)2)などの水溶液にアンモニア水などを滴下しpHを9
〜10程度とする。この溶液を攪拌しながら20〜80℃程度
で30分〜20時間程度熟成させ、その後沈殿を濾取し、必
要に応じて水などで洗浄し、水酸化スズ(Sn(OH)4)の沈
殿を得る。
The following method can be exemplified as a method for preparing tin hydroxide (Sn (OH) 4 ). Tin chloride (SnCl 4 ), tin sulfate (Sn
(SO 4 ) 2 )) to an aqueous solution such as ammonia water to adjust the pH to 9
~ 10 or so. The solution is aged at about 20 to 80 ° C. for about 30 minutes to 20 hours while stirring, and then the precipitate is collected by filtration, washed with water as necessary, and then precipitated with tin hydroxide (Sn (OH) 4 ). Get.

【0020】強酸化処理の方法として、上記以外にタン
グステン酸(H2WO4)と水酸化スズ(Sn(OH)4)とを湿式混練
したのち、空気中などの酸化雰囲気下において、600〜9
00℃程度(好ましくは700〜800℃程度)で1〜20時間程
度(好ましくは3〜10時間程度)焼成することによっ
て、タングステン修飾酸化スズとする方法なども例示で
きる。
As a method of the strong oxidation treatment, in addition to the above, after tungstic acid (H 2 WO 4 ) and tin hydroxide (Sn (OH) 4 ) are wet-kneaded, the mixture is subjected to a wet kneading process in an oxidizing atmosphere such as air. 9
A method of baking at about 00 ° C. (preferably about 700 to 800 ° C.) for about 1 to 20 hours (preferably about 3 to 10 hours) to obtain tungsten-modified tin oxide can also be exemplified.

【0021】本発明の触媒の比表面積は、特に制限され
ないが、通常50〜200m2/g程度、好ましくは50〜100m2/g
程度、より好ましくは55〜80m2/g程度である。触媒の調
製に用いる強酸化処理酸化スズの比表面積は、焼成工程
においてその比表面積がほぼ変化しないので、上記範囲
とほぼ同様である。なお、本件における比表面積の値
は、BET法による測定値とする。
The specific surface area of the catalyst of the present invention is not particularly limited, usually 50 to 200 m 2 / g, preferably about 50 to 100 m 2 / g
Degree, more preferably about 55 to 80 m 2 / g. The specific surface area of the strongly oxidized tin oxide used for preparing the catalyst is almost the same as the above range because the specific surface area does not substantially change in the firing step. The value of the specific surface area in this case is a value measured by the BET method.

【0022】パラジウムの担持量(白金と併用する場合
も含む)は、特に制限されないが、強酸化処理した酸化
スズの重量に対して、通常0.5〜20%程度、より好まし
くは1〜5%程度である。パラジウムの担持量が、少なす
ぎる場合には、触媒活性が十分に発揮されない恐れがあ
るのに対して、多すぎる場合には、パラジウムの粒径が
大きくなりすぎ、パラジウムが活性金属として有効に使
われなくなる恐れがある。
The amount of palladium carried (including the case where platinum is used together with platinum) is not particularly limited, but is usually about 0.5 to 20%, more preferably about 1 to 5%, based on the weight of the strongly oxidized tin oxide. It is. If the amount of supported palladium is too small, the catalytic activity may not be sufficiently exhibited.On the other hand, if the amount is too large, the particle size of palladium becomes too large and palladium is effectively used as an active metal. There is a risk of getting lost.

【0023】白金の担持量は、パラジウムに対する重量
比で、通常2〜100%程度であり、より好ましくは5〜50
%程度である。白金の担持量が少なすぎる場合には、両
金属の併用による効果の改善が、十分に発現されないお
それがあるのに対して、多すぎる場合には、活性金属と
してのパラジウムの機能を阻害するおそれがある。
The supported amount of platinum is usually about 2 to 100% by weight relative to palladium, and more preferably 5 to 50%.
%. If the amount of supported platinum is too small, the effect of the combination of the two metals may not be sufficiently improved, whereas if it is too large, the function of palladium as an active metal may be impaired. There is.

【0024】本発明の触媒は、必要に応じてバインダー
を加えるなどして、ペレット状、ハニカム状などの任意
の形状に成型してもよい。或いは、耐火性ハニカム上に
ウオッシュコートしたりして用いてもよい。好ましくは
耐火性ハニカム上にウオッシュコートして用いられる。
The catalyst of the present invention may be formed into an arbitrary shape such as a pellet or a honeycomb by adding a binder if necessary. Alternatively, it may be used after being wash-coated on a fire-resistant honeycomb. Preferably, it is used after being wash-coated on a refractory honeycomb.

【0025】本発明の触媒は、例えば、強酸化処理した
酸化スズをパラジウム化合物、必要に応じて更に白金化
合物を溶解させた溶液に含浸させ、酸化雰囲気下で焼成
する方法などによって得られる。焼成前に、必要に応じ
て、乾燥を行ってもよい。
The catalyst of the present invention can be obtained, for example, by impregnating a strongly oxidized tin oxide with a solution in which a palladium compound and, if necessary, a platinum compound are further dissolved, and baking it in an oxidizing atmosphere. Before baking, drying may be performed, if necessary.

【0026】パラジウム化合物および必要に応じて用い
る白金化合物は、溶液中において、それぞれの金属イオ
ンを解離する化合物であれば特に制限されない。パラジ
ウム化合物として、例えば、硝酸パラジウム、テトラア
ンミンパラジウム硝酸塩、塩化パラジウムなどを例示で
きる。これらのなかでは、硝酸パラジウム、テトラアン
ミンパラジウム硝酸塩が好ましい。白金化合物として、
テトラアンミン白金硝酸塩、塩化白金酸などを例示でき
る。これらのなかでは、テトラアンミン白金硝酸塩が好
ましい。溶媒は、水が好ましいが、エタノール、アセト
ンなどの水溶性有機溶媒を加えた混合溶媒としてもよ
い。或いは、硝酸などの酸性水溶液を溶媒として用いて
も良い。
The palladium compound and the platinum compound used as required are not particularly limited as long as they dissociate the respective metal ions in the solution. Examples of the palladium compound include palladium nitrate, tetraammine palladium nitrate, palladium chloride and the like. Of these, palladium nitrate and tetraammine palladium nitrate are preferred. As a platinum compound,
Examples thereof include tetraammineplatinum nitrate and chloroplatinic acid. Of these, tetraammineplatinum nitrate is preferred. The solvent is preferably water, but may be a mixed solvent to which a water-soluble organic solvent such as ethanol or acetone is added. Alternatively, an acidic aqueous solution such as nitric acid may be used as the solvent.

【0027】パラジウムと白金とを併用する場合には、
両者を逐次担持してもよいし、同時に担持してもよい。
特に必要のない限り、両者を同時に担持する方が経済的
である。
When palladium and platinum are used together,
Both may be carried sequentially or simultaneously.
Unless it is particularly necessary, it is more economical to carry both at the same time.

【0028】次いで、所定の活性金属を含浸させた強酸
化処理した酸化スズを必要に応じて乾燥させた後、空気
中などの酸化雰囲気下においてこれを焼成する。焼成温
度は、通常400℃〜600℃程度、より好ましくは500℃〜5
50℃程度である。焼成温度が高すぎると、担持された活
性金属が極端に凝集して活性を損なうおそれがあり、一
方、低すぎると、担持した活性金属の安定性に問題が生
じる恐れがある。焼成時間は、通常1〜20時間程度、好
ましくは2〜10時間程度である。
Next, the tin oxide that has been subjected to the strong oxidation treatment and impregnated with a predetermined active metal is dried if necessary, and then fired in an oxidizing atmosphere such as in air. The firing temperature is usually about 400 ° C to 600 ° C, more preferably 500 ° C to 5 ° C.
It is around 50 ° C. If the firing temperature is too high, the supported active metal may be extremely agglomerated and impair the activity, while if too low, the stability of the supported active metal may be problematic. The firing time is usually about 1 to 20 hours, preferably about 2 to 10 hours.

【0029】本発明の触媒を耐火性ハニカム上にウオッ
シュコートする場合には、予め調製した触媒をスラリー
状にしてウオッシュコートしてもよいし、或いは、予め
強酸化処理した酸化スズを耐火性ハニカム上にウオッシ
ュコートしてから、パラジウム、必要に応じて白金を担
持してもよい。
When the catalyst of the present invention is wash-coated on a refractory honeycomb, the catalyst prepared in advance may be slurry-coated and wash-coated, or tin oxide which has been subjected to a strong oxidation treatment may be washed with a refractory honeycomb. After wash-coating on top, palladium and, if necessary, platinum may be supported.

【0030】本発明の排ガス浄化方法は、強酸化処理し
た酸化スズにパラジウム、必要に応じて更に白金を担持
した触媒を用いることを特徴とする。
The exhaust gas purifying method of the present invention is characterized by using a catalyst in which palladium is supported on tin oxide subjected to strong oxidation treatment and, if necessary, platinum is further supported.

【0031】触媒量は、ガス時間当たり空間速度(GHSV)
で、通常200000h-1以下程度であり、より好ましくは10
00〜60000h-1程度である。触媒使用量が少なすぎる場
合、即ちGHSV値が大きすぎる場合には、有効な浄化率が
得られない恐れがある。一方、触媒使用量が多すぎる場
合、即ちGHSV値が小さすぎる場合には、浄化率は向上す
るが、経済性の問題に加えて、触媒層での圧力損失が大
きくなるという問題が生じるおそれがある。
The amount of catalyst is determined by the gas hourly space velocity (GHSV).
And usually about 200,000 h -1 or less, more preferably 10
It is about 00 to 60000 h -1 . If the amount of the catalyst used is too small, that is, if the GHSV value is too large, an effective purification rate may not be obtained. On the other hand, when the amount of the catalyst used is too large, that is, when the GHSV value is too small, the purification rate is improved, but in addition to the problem of economy, there is a possibility that a problem that the pressure loss in the catalyst layer becomes large may occur. is there.

【0032】本発明の排ガス浄化方法における触媒層の
温度は、通常350〜600℃程度、好ましくは400〜500℃程
度である。本発明の触媒は高い活性を有するが、あまり
に低温では触媒活性が下がり有効な転化率が得られない
恐れがあり、一方、温度が高すぎる場合には、触媒の耐
久性が悪化するおそれがある。
The temperature of the catalyst layer in the exhaust gas purification method of the present invention is usually about 350 to 600 ° C., preferably about 400 to 500 ° C. The catalyst of the present invention has high activity, but if the temperature is too low, the catalyst activity may be reduced and an effective conversion may not be obtained, while if the temperature is too high, the durability of the catalyst may be deteriorated. .

【0033】本発明方法が浄化対象とする排ガス中の炭
化水素は、排ガス中の炭化水素であれば特に制限されな
いが、例えば、メタン、エタンなどの低級飽和炭化水素
が挙げられる。排ガス中の炭化水素の濃度は、特に制限
されないが、メタン換算で通常50〜5000ppm程度であ
る。炭化水素の濃度が著しく高い場合には、触媒層で急
激な反応と共に温度上昇が生じるので、触媒層での温度
上昇(触媒層出口温度と入口温度との差)が、150℃以下
となる条件で用いるのが好ましい。
The hydrocarbon in the exhaust gas to be purified by the method of the present invention is not particularly limited as long as it is a hydrocarbon in the exhaust gas, and examples thereof include lower saturated hydrocarbons such as methane and ethane. The concentration of the hydrocarbon in the exhaust gas is not particularly limited, but is usually about 50 to 5000 ppm in terms of methane. When the concentration of hydrocarbon is extremely high, the temperature rises in the catalyst layer together with the rapid reaction, so that the temperature rise in the catalyst layer (difference between the catalyst layer outlet temperature and the inlet temperature) is 150 ° C or less. It is preferable to use them.

【0034】排ガス中の酸素濃度は、酸素、酸化窒素な
どの酸化性成分を過剰に含んだ状態であれば特に制限さ
れない。酸素濃度は、体積基準として、約2%以上であ
り、且つ排ガス中の炭化水素などの還元性成分の酸化当
量の約5倍以上であることが好ましい。酸素濃度が極め
て低い場合(例えば、体積基準で約1%以下)には、反応
速度が遅くなりすぎる恐れがある。このように排ガス中
の酸素濃度が低すぎる場合には、排ガスの温度が好適な
範囲を下回らないように留意しつつ、適当量の空気を混
合した空気混合排ガスを触媒に接触させてもよい。
The oxygen concentration in the exhaust gas is not particularly limited as long as it contains oxidizing components such as oxygen and nitrogen oxide in excess. The oxygen concentration is preferably about 2% or more on a volume basis and about 5 times or more the oxidation equivalent of a reducing component such as hydrocarbon in the exhaust gas. If the oxygen concentration is very low (eg, about 1% or less by volume), the reaction rate may be too slow. When the oxygen concentration in the exhaust gas is too low as described above, an air-mixed exhaust gas obtained by mixing an appropriate amount of air may be brought into contact with the catalyst while taking care that the temperature of the exhaust gas does not fall below a suitable range.

【0035】[0035]

【発明の効果】排ガス中には、通常5%〜15%程度の水
蒸気が含まれているが、本発明の方法によれば、このよ
うに水蒸気を含む排ガスに対しても有効な浄化性能が得
られる。
The exhaust gas usually contains about 5% to 15% of water vapor. However, according to the method of the present invention, an effective purification performance can be obtained even for an exhaust gas containing water vapor. can get.

【0036】排ガス中には、水蒸気の他に触媒活性を著
しく低下させる硫黄酸化物が通常含まれるが、本発明の
触媒は、硫黄成分による活性低下に対して高い抵抗性を
示すので、浄化性能は長期にわたって高く維持される。
The exhaust gas usually contains sulfur oxides, which significantly reduce the catalytic activity, in addition to the water vapor. However, the catalyst of the present invention has high resistance to the decrease in the activity due to the sulfur component. Remains high over time.

【0037】本発明の触媒によると、400℃程度の低温
度においても高い触媒活性を示すことができる。
According to the catalyst of the present invention, a high catalytic activity can be exhibited even at a low temperature of about 400 ° C.

【0038】[0038]

【実施例】以下、実施例に基づき、本発明をより詳細に
説明するが、本発明はこれらの実施例に限定されるもの
ではない。
EXAMPLES Hereinafter, the present invention will be described in more detail based on examples, but the present invention is not limited to these examples.

【0039】実施例1(5% Pd/硫酸化酸化スズ(1)の調
製) 塩化スズ(SnCl4・5H2O)48gを純水500mlに溶解し、60
℃に保って良く攪拌しながらアンモニア水を滴下した。
pHが9.5となったところで、アンモニア水の滴下を止め
て、60℃で1時間攪拌を続けた。この液を濾過し、濾取
した固体を純水で水洗し、乾燥して水酸化スズ(Sn(O
H)4)を得た。この水酸化スズ(6.2g)を硫酸アンモニウム
0.97gを溶解した水溶液(30ml)に15時間浸漬した後、蒸
発乾固し、空気中550℃で4時間焼成して、硫酸化酸化
スズ(1)を得た。
[0039] Example 1 (5% Pd / preparation of a sulfated tin oxide (1)) of tin chloride (SnCl 4 · 5H 2 O) 48g was dissolved in pure water 500 ml, 60
Aqueous ammonia was added dropwise while maintaining the temperature at 0 ° C and stirring well.
When the pH reached 9.5, the dropping of the aqueous ammonia was stopped, and stirring was continued at 60 ° C. for 1 hour. This solution was filtered, and the collected solid was washed with pure water, dried and dried with tin hydroxide (Sn (O
H) 4 ) was obtained. This tin hydroxide (6.2 g) was treated with ammonium sulfate
After immersing for 15 hours in an aqueous solution (30 ml) in which 0.97 g was dissolved, the residue was evaporated to dryness and calcined at 550 ° C. for 4 hours in the air to obtain sulfated tin oxide (1).

【0040】この硫酸化酸化スズ(1)5.35gをPdとして0.
27gを含有する硝酸パラジウム水溶液10mlに15時間浸漬
した後、蒸発乾固し、空気中500℃で4時間焼成して、5
% Pd/硫酸化酸化スズ(1)を得た。この触媒のBET比表面
積は、58m2/gであった。
This sulfated tin oxide (1) (5.35 g) was used as Pd at 0.1%.
After immersion in 10 ml of an aqueous solution of palladium nitrate containing 27 g for 15 hours, the mixture was evaporated to dryness, and calcined at 500 ° C. for 4 hours in air.
% Pd / sulfated tin oxide (1) was obtained. The BET specific surface area of this catalyst was 58 m 2 / g.

【0041】比較例1(5% Pd/酸化スズの調製) 実施例1と同様にして得た水酸化スズを空気中550℃で
4時間焼成して酸化スズを得た。この酸化スズ5gをPdと
して0.25gを含有する硝酸パラジウム水溶液20mlに15時
間浸漬し、蒸発乾固し、500℃で4時間焼成して5% Pd/
酸化スズを得た。この触媒のBET表面積は16m2/gであっ
た。
Comparative Example 1 (Preparation of 5% Pd / tin oxide) Tin hydroxide obtained in the same manner as in Example 1 was calcined in air at 550 ° C. for 4 hours to obtain tin oxide. 5 g of this tin oxide was immersed in 20 ml of an aqueous palladium nitrate solution containing 0.25 g of Pd for 15 hours, evaporated to dryness, and calcined at 500 ° C. for 4 hours to obtain 5% Pd /
Tin oxide was obtained. The BET surface area of this catalyst was 16 m 2 / g.

【0042】比較例2(5% Pd/ジルコニアの調製) ジルコニア(東ソー製、TZ-0)3gを、Pdとして0.15gを
含有する硝酸パラジウム水溶液20mlに15時間浸漬した
後、蒸発乾固し、空気中500℃で4時間焼成して5% Pd/
ジルコニアを得た。
Comparative Example 2 (Preparation of 5% Pd / Zirconia) 3 g of zirconia (TZ-0, manufactured by Tosoh Corporation) was immersed in 20 ml of an aqueous palladium nitrate solution containing 0.15 g of Pd for 15 hours, and evaporated to dryness. Fired in air at 500 ℃ for 4 hours, 5% Pd /
Zirconia was obtained.

【0043】実施例2(5% Pd-1% Pt/硫酸化酸化スズ
(1)の調製) Pdとして0.27gを含有する硝酸パラジウム水溶液とジニ
トロジアンミン白金0.088gと69%硝酸0.5mlとを混合溶解
して純水で希釈して溶液(10ml)を調製した。この溶液に
実施例1と同様にして得た硫酸化酸化スズ(1)5.35gを15
時間浸漬し、蒸発乾固し、空気中500℃で4時間焼成し
て5% Pd-1% Pt/硫酸化酸化スズ(1)を得た。この触媒のB
ET表面積は58m2/gであった。
Example 2 (5% Pd-1% Pt / sulfated tin oxide)
Preparation of (1) An aqueous solution of palladium nitrate containing 0.27 g of Pd, 0.088 g of dinitrodiammineplatinum and 0.5 ml of 69% nitric acid were mixed and dissolved, and diluted with pure water to prepare a solution (10 ml). 5.35 g of sulfated tin oxide (1) obtained in the same manner as in Example 1 was added to this solution.
It was immersed for an hour, evaporated to dryness, and calcined in air at 500 ° C. for 4 hours to obtain 5% Pd-1% Pt / sulfated tin oxide (1). B of this catalyst
The ET surface area was 58 m 2 / g.

【0044】実施例3(5% Pd-1% Pt/硫酸化酸化スズ
(2)の調製) 実施例1と同様にして得た水酸化スズ18.6gを硫酸アン
モニウム3.1gを溶解する20mlの水溶液に15時間浸漬した
後、蒸発乾固し、空気中400℃で4時間焼成して、硫酸
化酸化スズ(2)を得た。
Example 3 (5% Pd-1% Pt / sulfated tin oxide)
(Preparation of (2)) 18.6 g of tin hydroxide obtained in the same manner as in Example 1 was immersed in a 20 ml aqueous solution of 3.1 g of ammonium sulfate for 15 hours, evaporated to dryness, and calcined at 400 ° C. in air for 4 hours. Thus, sulfated tin oxide (2) was obtained.

【0045】Pdとして0.32gを含有する硝酸パラジウム
水溶液とジニトロジアンミン白金0.105gと69%硝酸0.5ml
とを混合溶解して純水で希釈して溶液(10ml)を調製し
た。この溶液に硫酸化酸化スズ(2)6.4gを15時間浸漬
し、蒸発乾固し、空気中500℃で4時間焼成して5% Pd-1
% Pt/硫酸化酸化スズ(2)を得た。
An aqueous solution of palladium nitrate containing 0.32 g of Pd, 0.105 g of dinitrodiammine platinum and 0.5 ml of 69% nitric acid
Was mixed and dissolved, and diluted with pure water to prepare a solution (10 ml). 6.4 g of sulfated tin oxide (2) was immersed in this solution for 15 hours, evaporated to dryness, and calcined in air at 500 ° C. for 4 hours to obtain 5% Pd-1.
% Pt / sulfated tin oxide (2) was obtained.

【0046】実施例4(5% Pd-1% Pt/硫酸化酸化スズ
(3)の調製) 実施例1と同様にして得た水酸化スズ6.2gを硫酸アンモ
ニウム0.21gを溶解する10mlの水溶液に15時間浸漬した
後、蒸発乾固し、550℃で4時間焼成して、硫酸化酸化
スズ(3)を得た。
Example 4 (5% Pd-1% Pt / sulfated tin oxide)
(Preparation of (3)) 6.2 g of tin hydroxide obtained in the same manner as in Example 1 was immersed in 10 ml of an aqueous solution in which 0.21 g of ammonium sulfate was dissolved for 15 hours, evaporated to dryness, and calcined at 550 ° C. for 4 hours. Thus, sulfated tin oxide (3) was obtained.

【0047】Pdとして0.27gを含有する硝酸パラジウム
水溶液とジニトロジアンミン白金0.088gと69%硝酸0.5ml
とを混合溶解して純水で希釈して溶液(10ml)を調製し
た。この溶液に硫酸化酸化スズ(3)5.4gを15時間浸漬
し、蒸発乾固し、空気中500℃で4時間焼成して5% Pd-1
% Pt/硫酸化酸化スズ(3)を得た。
An aqueous solution of palladium nitrate containing 0.27 g of Pd, 0.088 g of dinitrodiammine platinum and 0.5 ml of 69% nitric acid
Was mixed and dissolved, and diluted with pure water to prepare a solution (10 ml). 5.4 g of sulfated tin oxide (3) was immersed in this solution for 15 hours, evaporated to dryness, and calcined in air at 500 ° C. for 4 hours to obtain 5% Pd-1.
% Pt / sulfated tin oxide (3) was obtained.

【0048】実施例5(5% Pd-1% Pt/硫酸化酸化スズ
(4)の調製) 実施例1と同様にして得た水酸化スズ6.2gを硫酸アンモ
ニウム1.55gを溶解する10mlの水溶液に15時間浸漬した
後、蒸発乾固し、空気中550℃で4時間焼成して、硫酸
化酸化スズ(4)を得た。
Example 5 (5% Pd-1% Pt / sulfated tin oxide)
(Preparation of (4)) 6.2 g of tin hydroxide obtained in the same manner as in Example 1 was immersed in a 10 ml aqueous solution of 1.55 g of ammonium sulfate for 15 hours, evaporated to dryness, and calcined at 550 ° C. for 4 hours in air. Thus, sulfated tin oxide (4) was obtained.

【0049】Pdとして0.27gを含有する硝酸パラジウム
水溶液とジニトロジアンミン白金0.09gと69%硝酸0.5ml
とを混合溶解して純水で希釈して溶液(10ml)を調製し
た。この溶液に硫酸化酸化スズ(4)5.5gを15時間浸漬
し、蒸発乾固し、空気中500℃で4時間焼成して5% Pd-1
% Pt/硫酸化酸化スズ(4)を得た。
An aqueous solution of palladium nitrate containing 0.27 g of Pd, 0.09 g of dinitrodiammine platinum and 0.5 ml of 69% nitric acid
Was mixed and dissolved, and diluted with pure water to prepare a solution (10 ml). 5.5 g of sulfated tin oxide (4) was immersed in this solution for 15 hours, evaporated to dryness, and calcined in air at 500 ° C. for 4 hours to form 5% Pd-1.
% Pt / sulfated tin oxide (4) was obtained.

【0050】比較例3(5% Pd-1% Pt/硫酸含浸酸化スズ
の調製) 実施例1と同様にして得た水酸化スズを550℃で4時間
焼成して酸化スズとした。この8.1gを3M硫酸150mlに投
入して30分攪拌後、濾過して、空気中550℃で4時間焼
成し硫酸含浸酸化スズを得た。
Comparative Example 3 (Preparation of 5% Pd-1% Pt / tin oxide impregnated with sulfuric acid) Tin hydroxide obtained in the same manner as in Example 1 was calcined at 550 ° C. for 4 hours to obtain tin oxide. This 8.1 g was put into 150 ml of 3M sulfuric acid, stirred for 30 minutes, filtered, and calcined in air at 550 ° C. for 4 hours to obtain sulfuric acid-impregnated tin oxide.

【0051】この硫酸含浸酸化スズを硫酸化酸化スズ
(1)に代えて用いた他は、実施例2と同様にして、5% Pd
-1% Pt/硫酸含浸酸化スズを得た。この触媒のBET表面積
は37m 2/gであった。
The sulfuric acid-impregnated tin oxide is replaced with sulfated tin oxide.
Except that it was used in place of (1), 5% Pd
-1% Pt / sulfuric acid impregnated tin oxide was obtained. BET surface area of this catalyst
Is 37m Two/ g.

【0052】実施例6(触媒評価試験1) 実施例1〜5および比較例1〜3において調製した触媒
をそれぞれ打錠成型し、それぞれ 1 mlとって反応管に
充填した。この反応管にメタン 1000 ppm、酸素10%、水
蒸気10%、二酸化硫黄8 ppm、残部窒素からなる組成のガ
スをGHSV(ガス時間当たり空間速度)40000 h-1の条件
にて流通し、触媒層温度を400℃に保ってメタン転化率
の経時変化を測定した。反応層前後のガス組成は水素炎
イオン化検知器を有するガスクロマトグラフにより測定
した。試験開始後1, 5, 10, 30, 36, 42時間後のメタン
転化率(%)を表1に示す。ここでメタン転化率とは、
以下の式によって求められる値である。
Example 6 (Catalyst Evaluation Test 1) Each of the catalysts prepared in Examples 1 to 5 and Comparative Examples 1 to 3 was tableted, and 1 ml of each was filled in a reaction tube. A gas composed of 1000 ppm of methane, 10% of oxygen, 10% of water vapor, 8 ppm of sulfur dioxide, and the balance of nitrogen was passed through this reactor under the conditions of GHSV (gas hourly space velocity) of 40,000 h -1 and the catalyst layer While maintaining the temperature at 400 ° C., the change with time of the methane conversion was measured. The gas composition before and after the reaction layer was measured by a gas chromatograph equipped with a flame ionization detector. Table 1 shows the methane conversion (%) 1, 5, 10, 30, 36, and 42 hours after the start of the test. Here, the methane conversion is
It is a value obtained by the following equation.

【0053】[0053]

【式1】 (Equation 1)

【0054】[0054]

【表1】 [Table 1]

【0055】表1から明らかなように、実施例の触媒
は、触媒活性を著しく低下させる二酸化硫黄の共存下で
あり、400℃という低い温度であってもきわめて安定し
た活性を示した。
As is evident from Table 1, the catalysts of the examples were in the presence of sulfur dioxide, which significantly reduced the catalytic activity, and exhibited extremely stable activities even at temperatures as low as 400 ° C.

【0056】これに対して、単なる酸化スズを担体とし
て用いた場合には、活性の低下は顕著である(比較例
1)。また、硫酸に含浸させた酸化スズを担体として用
いても、本発明と同様の効果が得られないことも明らか
である(比較例3)。
On the other hand, when mere tin oxide was used as the carrier, the activity was significantly reduced (Comparative Example 1). It is also clear that the same effect as in the present invention cannot be obtained when tin oxide impregnated in sulfuric acid is used as a carrier (Comparative Example 3).

【0057】実施例7(触媒評価試験2) 実施例2の触媒を実施例6と同じ条件でさらに長時間に
わたって試験した。試験開始後のメタン転化率は、下表
の通り推移した。
Example 7 (Catalyst Evaluation Test 2) The catalyst of Example 2 was tested under the same conditions as in Example 6 for a longer time. The methane conversion rate after the start of the test changed as shown in the table below.

【0058】[0058]

【表2】 [Table 2]

【0059】本発明の触媒が、長期にわたって安定した
メタン転化率を示すことが明らかである。
It is clear that the catalysts of the present invention show stable methane conversion over a long period.

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D048 AA18 AB01 AB07 BA21X BA30X BA31X BA46X BB01 BB02 BC01 4G069 AA03 BA45A BB02A BB02B BB04A BB10A BB10B BC22A BC22B BC60A BC72A BC72B BC75A BC75B CA02 CA03 CA07 CA15 EA02Y EA18 EA19 EC02Y EC03Y ED07 ──────────────────────────────────────────────────続 き Continued on the front page F term (reference) 4D048 AA18 AB01 AB07 BA21X BA30X BA31X BA46X BB01 BB02 BC01 4G069 AA03 BA45A BB02A BB02B BB04A BB10A BB10B BC22A BC22B BC60A BC72A BC72B BC75 EA02 CA03 EA02 CA03 EA02

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】メタンを含有し酸素を過剰に含む燃焼排ガ
ス中の炭化水素の浄化用触媒であって、強酸化処理した
酸化スズにパラジウムを担持した触媒。
1. A catalyst for purifying hydrocarbons in a combustion exhaust gas containing methane and containing an excess of oxygen, wherein palladium is carried on strongly oxidized tin oxide.
【請求項2】メタンを含有し酸素を過剰に含む燃焼排ガ
ス中の炭化水素の浄化用触媒であって、強酸化処理した
酸化スズにパラジウムおよび白金を担持した触媒。
2. A catalyst for purifying hydrocarbons in a combustion exhaust gas containing methane and containing an excessive amount of oxygen, wherein palladium and platinum are supported on strongly oxidized tin oxide.
【請求項3】メタンを含有し酸素を過剰に含む燃焼排ガ
ス中の炭化水素の浄化方法であって、強酸化処理した酸
化スズにパラジウムを担持した触媒を用いる浄化方法。
3. A method for purifying hydrocarbons in a combustion exhaust gas containing methane and containing an excessive amount of oxygen, the method comprising using a catalyst in which palladium is carried on tin oxide subjected to strong oxidation treatment.
【請求項4】メタンを含有し酸素を過剰に含む燃焼排ガ
ス中の炭化水素の浄化方法であって、強酸化処理した酸
化スズにパラジウムおよび白金を担持した触媒を用いる
浄化方法。
4. A method for purifying hydrocarbons in a combustion exhaust gas containing methane and containing an excessive amount of oxygen, which comprises using a catalyst in which palladium and platinum are supported on tin oxide subjected to strong oxidation treatment.
JP2001058623A 2001-03-02 2001-03-02 Catalyst for purifying waste gas and method of purifying waste gas Pending JP2002253969A (en)

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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2004103554A1 (en) * 2003-05-26 2004-12-02 Tokyo Gas Company Limited Catalyst for oxidizing and removing methane in exhaust gas method for clarifying exhaust gas
JP2006116444A (en) * 2004-10-22 2006-05-11 Japan Energy Corp Exhaust gas purifying catalyst and manufacturing method therefor
JP2006116445A (en) * 2004-10-22 2006-05-11 Japan Energy Corp Exhaust gas purifying catalyst and manufacturing method therefor
JP2007266799A (en) * 2006-03-28 2007-10-11 Hitachi Ltd Ip telephone system and ip telephone terminal registration method
CN103288286A (en) * 2013-06-28 2013-09-11 陕西煤业化工技术研究院有限责任公司 Catalytic oxidation treatment method for desulfurized waste liquid
EP3501639A4 (en) * 2016-08-17 2020-04-01 Mitsui Mining & Smelting Co., Ltd. Methane oxidation catalyst
WO2021132335A1 (en) * 2019-12-27 2021-07-01 国立大学法人京都大学 Solid solution nanoparticles, method for producing same, dispersion liquid of solution solid nanoparticles, and catalyst

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2004103554A1 (en) * 2003-05-26 2004-12-02 Tokyo Gas Company Limited Catalyst for oxidizing and removing methane in exhaust gas method for clarifying exhaust gas
JP2006116444A (en) * 2004-10-22 2006-05-11 Japan Energy Corp Exhaust gas purifying catalyst and manufacturing method therefor
JP2006116445A (en) * 2004-10-22 2006-05-11 Japan Energy Corp Exhaust gas purifying catalyst and manufacturing method therefor
JP2007266799A (en) * 2006-03-28 2007-10-11 Hitachi Ltd Ip telephone system and ip telephone terminal registration method
JP4605066B2 (en) * 2006-03-28 2011-01-05 株式会社日立製作所 IP telephone system and IP telephone terminal registration method
CN103288286A (en) * 2013-06-28 2013-09-11 陕西煤业化工技术研究院有限责任公司 Catalytic oxidation treatment method for desulfurized waste liquid
CN103288286B (en) * 2013-06-28 2015-03-18 陕西煤业化工技术研究院有限责任公司 Catalytic oxidation treatment method for desulfurized waste liquid
EP3501639A4 (en) * 2016-08-17 2020-04-01 Mitsui Mining & Smelting Co., Ltd. Methane oxidation catalyst
WO2021132335A1 (en) * 2019-12-27 2021-07-01 国立大学法人京都大学 Solid solution nanoparticles, method for producing same, dispersion liquid of solution solid nanoparticles, and catalyst

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