JP2003170050A - Exhaust gas cleaning catalyst - Google Patents
Exhaust gas cleaning catalystInfo
- Publication number
- JP2003170050A JP2003170050A JP2001376147A JP2001376147A JP2003170050A JP 2003170050 A JP2003170050 A JP 2003170050A JP 2001376147 A JP2001376147 A JP 2001376147A JP 2001376147 A JP2001376147 A JP 2001376147A JP 2003170050 A JP2003170050 A JP 2003170050A
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- exhaust gas
- carrier
- powder
- occlusion
- 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
Links
- 239000003054 catalyst Substances 0.000 title claims abstract description 68
- 238000004140 cleaning Methods 0.000 title abstract 5
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 claims abstract description 56
- 239000007789 gas Substances 0.000 claims abstract description 41
- AMWRITDGCCNYAT-UHFFFAOYSA-L hydroxy(oxo)manganese;manganese Chemical compound [Mn].O[Mn]=O.O[Mn]=O AMWRITDGCCNYAT-UHFFFAOYSA-L 0.000 claims abstract description 38
- 229910052697 platinum Inorganic materials 0.000 claims abstract description 23
- 239000013078 crystal Substances 0.000 claims abstract description 12
- 230000001603 reducing effect Effects 0.000 claims abstract description 10
- 239000000126 substance Substances 0.000 claims abstract description 10
- 239000000463 material Substances 0.000 claims abstract description 9
- 229910000510 noble metal Inorganic materials 0.000 claims abstract description 5
- 229910052763 palladium Inorganic materials 0.000 claims abstract description 4
- 229910052703 rhodium Inorganic materials 0.000 claims abstract description 4
- 229910052783 alkali metal Inorganic materials 0.000 claims abstract description 3
- 150000001340 alkali metals Chemical class 0.000 claims abstract description 3
- 229910052784 alkaline earth metal Inorganic materials 0.000 claims abstract description 3
- 150000001342 alkaline earth metals Chemical class 0.000 claims abstract description 3
- 229910052761 rare earth metal Inorganic materials 0.000 claims abstract description 3
- 150000002910 rare earth metals Chemical class 0.000 claims abstract description 3
- 239000011232 storage material Substances 0.000 claims description 15
- 229910052751 metal Inorganic materials 0.000 claims 1
- 239000002184 metal Substances 0.000 claims 1
- 230000002708 enhancing effect Effects 0.000 abstract 1
- 238000004519 manufacturing process Methods 0.000 abstract 1
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 description 53
- 239000000843 powder Substances 0.000 description 26
- 238000000746 purification Methods 0.000 description 19
- 229910052788 barium Inorganic materials 0.000 description 13
- DSAJWYNOEDNPEQ-UHFFFAOYSA-N barium atom Chemical compound [Ba] DSAJWYNOEDNPEQ-UHFFFAOYSA-N 0.000 description 11
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 10
- 230000000052 comparative effect Effects 0.000 description 8
- 239000011148 porous material Substances 0.000 description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 7
- 239000000446 fuel Substances 0.000 description 6
- 239000008188 pellet Substances 0.000 description 6
- 238000012360 testing method Methods 0.000 description 6
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 5
- 239000000203 mixture Substances 0.000 description 5
- 229910052700 potassium Inorganic materials 0.000 description 5
- 239000011591 potassium Substances 0.000 description 5
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 4
- MCMNRKCIXSYSNV-UHFFFAOYSA-N Zirconium dioxide Chemical compound O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 description 4
- 239000007864 aqueous solution Substances 0.000 description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 4
- 238000001035 drying Methods 0.000 description 4
- 239000001301 oxygen Substances 0.000 description 4
- 229910052760 oxygen Inorganic materials 0.000 description 4
- 229920006395 saturated elastomer Polymers 0.000 description 4
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 description 3
- 238000002441 X-ray diffraction Methods 0.000 description 3
- 238000002485 combustion reaction Methods 0.000 description 3
- 238000000034 method Methods 0.000 description 3
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 2
- 229910021536 Zeolite Inorganic materials 0.000 description 2
- 229910000272 alkali metal oxide Inorganic materials 0.000 description 2
- 150000001552 barium Chemical class 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 2
- 238000011156 evaluation Methods 0.000 description 2
- 238000010304 firing Methods 0.000 description 2
- 229930195733 hydrocarbon Natural products 0.000 description 2
- 150000002430 hydrocarbons Chemical class 0.000 description 2
- 238000001027 hydrothermal synthesis Methods 0.000 description 2
- 238000005259 measurement Methods 0.000 description 2
- SCVFZCLFOSHCOH-UHFFFAOYSA-M potassium acetate Chemical compound [K+].CC([O-])=O SCVFZCLFOSHCOH-UHFFFAOYSA-M 0.000 description 2
- 238000002360 preparation method Methods 0.000 description 2
- 239000010948 rhodium Substances 0.000 description 2
- 239000000377 silicon dioxide Substances 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 239000010457 zeolite Substances 0.000 description 2
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 102100033041 Carbonic anhydrase 13 Human genes 0.000 description 1
- 101000867860 Homo sapiens Carbonic anhydrase 13 Proteins 0.000 description 1
- 229910018663 Mn O Inorganic materials 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 239000001099 ammonium carbonate Substances 0.000 description 1
- 235000012501 ammonium carbonate Nutrition 0.000 description 1
- ITHZDDVSAWDQPZ-UHFFFAOYSA-L barium acetate Chemical compound [Ba+2].CC([O-])=O.CC([O-])=O ITHZDDVSAWDQPZ-UHFFFAOYSA-L 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000011259 mixed solution Substances 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 235000011056 potassium acetate Nutrition 0.000 description 1
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 description 1
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、排気ガス浄化触媒
に関し、特に内燃機関リーン運転時の酸素過剰排気ガス
中の窒素酸化物(NOx)に対する吸蔵・浄化能力を高
めた排気ガス浄化触媒に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas purifying catalyst, and more particularly to an exhaust gas purifying catalyst having an enhanced ability to store and purify nitrogen oxides (NOx) in oxygen-excess exhaust gas during lean operation of an internal combustion engine.
【0002】[0002]
【従来の技術】排気ガス浄化触媒の性能はエンジンの設
定空燃比によって大きく左右され、希薄混合気、つまり
空燃比の大きいリーン側では燃焼後の排気ガス中の酸素
量が多くなり、酸化作用が活発に、還元作用が不活発に
なる。逆に、空燃比の小さいリッチ側では燃焼後の排気
ガス中の酸素量が少なくなり、酸化作用が不活発に、還
元作用が活発になる。2. Description of the Related Art The performance of an exhaust gas purifying catalyst is greatly influenced by the set air-fuel ratio of the engine, and the lean air-fuel mixture, that is, the lean side where the air-fuel ratio is large, has a large amount of oxygen in the exhaust gas after combustion, resulting in oxidation. Actively, the reducing action becomes inactive. On the other hand, on the rich side where the air-fuel ratio is small, the amount of oxygen in the exhaust gas after combustion becomes small, and the oxidizing action becomes inactive and the reducing action becomes active.
【0003】近年、自動車の低燃費化の要請に応えて通
常走行時になるべく酸素過剰の混合気で燃焼させるリー
ン側での運転が行なわれており、リーン側でも十分にN
Oxを浄化できる触媒が望まれていた。In recent years, in response to the demand for low fuel consumption of automobiles, lean side operation in which the air-fuel mixture is burned with an oxygen-rich mixture as much as possible during normal driving has been performed, and the lean side is sufficiently operated.
A catalyst that can purify Ox has been desired.
【0004】本出願人は、特開平6−31139号公報
において、酸素過剰下の排気ガス中の一酸化炭素(C
O)、炭化水素(HC)、窒素酸化物(NOx)を同時
に浄化するための排気ガス浄化触媒を提案した。これ
は、酸素過剰の排気ガスを、多孔質担体にアルカリ金属
酸化物および白金を担持させた排気ガス浄化触媒に接触
させることにより、リーン運転時に発生した上記NOx
等の浄化対象物質をアルカリ金属酸化物に吸蔵させ、リ
ッチ運転時に放出された浄化対象物質を白金により還元
浄化する吸蔵還元型触媒である。The applicant of the present invention has disclosed in Japanese Patent Application Laid-Open No. 6-31139 that carbon monoxide (C
We have proposed an exhaust gas purification catalyst for simultaneously purifying O), hydrocarbons (HC), and nitrogen oxides (NOx). This is because the exhaust gas in excess of oxygen is brought into contact with an exhaust gas purifying catalyst in which a porous carrier carries an alkali metal oxide and platinum, whereby the above-mentioned NOx generated during lean operation.
Is a storage-reduction catalyst in which a substance to be purified such as a substance to be purified is stored in an alkali metal oxide and the substance to be purified released during rich operation is reduced and purified by platinum.
【0005】これは、それまでの汎用触媒、例えばアル
ミナ担体にパラジウム、白金、ロジウムを担持させた三
元触媒等に比べて格段に高い浄化性能を発揮できる。[0005] This can exhibit a far higher purification performance than conventional general-purpose catalysts such as a three-way catalyst in which palladium, platinum and rhodium are supported on an alumina carrier.
【0006】しかし、環境浄化に対する社会的要請は一
層高まる趨勢にあり、浄化性能を更に高めた排気ガス浄
化触媒が求められていた。However, the social demand for environmental purification is increasing, and there has been a demand for an exhaust gas purification catalyst having further improved purification performance.
【0007】浄化性能を向上させる大きな要因として、
吸蔵材および還元触媒を担持する担体の担持濃度の向上
が重要である。As a major factor for improving the purification performance,
It is important to improve the supported concentration of the carrier that supports the storage material and the reduction catalyst.
【0008】この観点からは、上記提案の排気ガス浄化
触媒には限界があった。すなわち、担体として用いてい
るアルミナ、ゼオライト、ジルコニア、シリカアルミ
ナ、シリカ等の多孔質構造では、その担持能力に対して
既に担持濃度が飽和状態であり、更に担持濃度を高める
ことはできなかった。From this viewpoint, the exhaust gas purifying catalyst proposed above has a limit. That is, in the porous structure of alumina, zeolite, zirconia, silica-alumina, silica, etc. used as a carrier, the supporting concentration was already saturated with respect to its supporting ability, and the supporting concentration could not be further increased.
【0009】[0009]
【発明が解決しようとする課題】本発明は、担体の担持
濃度を更に高めることにより浄化性能を高めた排気ガス
浄化触媒を提供することを目的とする。SUMMARY OF THE INVENTION It is an object of the present invention to provide an exhaust gas purifying catalyst whose purifying performance is improved by further increasing the supported concentration of the carrier.
【0010】[0010]
【課題を解決するための手段】上記目的を達成するため
に、本発明の排気ガス浄化触媒は、担体に、浄化対象物
質を吸蔵する吸蔵材と、この吸蔵材から放出された浄化
対象物質を還元浄化する還元触媒とを担持させた吸蔵還
元型の排気ガス浄化触媒において、ホーランダイト型結
晶構造を有するマンガン酸化物から成る担体に、吸蔵材
としての窒素酸化物吸蔵元素と、還元触媒としての貴金
属とを担持して成ることを特徴とする。In order to achieve the above object, the exhaust gas purifying catalyst of the present invention has, on a carrier, an occlusion material that occludes a substance to be purified and a substance to be purified released from the substance. In an exhaust reduction type exhaust gas purification catalyst supporting a reduction catalyst for reduction and purification, a carrier made of manganese oxide having a hollandite type crystal structure, a nitrogen oxide storage element as an absorption material, and a reduction catalyst It is characterized by supporting a noble metal.
【0011】窒素酸化物吸蔵元素は、典型的にはアルカ
リ金属、アルカリ土類金属および希土類金属から成る群
から選択される。The nitrogen oxide storage element is typically selected from the group consisting of alkali metals, alkaline earth metals and rare earth metals.
【0012】貴金属は、典型的には、Pt、Pdおよび
Rhから成る群から選択される。The noble metal is typically selected from the group consisting of Pt, Pd and Rh.
【0013】[0013]
【発明の実施の形態】本発明の排気ガス浄化触媒は、吸
蔵材および還元触媒の担体を、ホーランダイト(Hollan
dite)型結晶構造を有するマンガン酸化物で構成した点
に特徴がある。このホーランダイト型結晶構造は、Mn
O6八面体を基本単位とし、これが縦2単位×横2単位
配列して中央に細孔が形成された構造であり、担体全体
としては三次元細孔構造を備えている。BEST MODE FOR CARRYING OUT THE INVENTION In the exhaust gas purifying catalyst of the present invention, the storage material and the carrier for the reduction catalyst are made of hollandite.
It is characterized in that it is composed of manganese oxide having a dite) type crystal structure. This hollandite type crystal structure is Mn
O 6 octahedron is the basic unit, and this is a structure in which 2 units in the vertical direction × 2 units in the horizontal direction are arranged and a pore is formed in the center, and the entire carrier has a three-dimensional pore structure.
【0014】この三次元細孔構造は、排気ガスが担体中
に十分拡散することを可能とすると同時に、吸蔵材およ
び還元触媒を原子単位で高分散に担持して担持濃度を飛
躍的に高め、排気ガス浄化触媒としての浄化能力を格段
に向上させる。This three-dimensional pore structure enables the exhaust gas to sufficiently diffuse in the carrier, and at the same time, the storage material and the reduction catalyst are supported in a highly dispersed manner in atomic units to dramatically increase the supported concentration, The purification ability as an exhaust gas purification catalyst is significantly improved.
【0015】従来の排気ガス浄化触媒で担体として用い
ていたアルミナ、ジルコニア、シリカアルミナ、シリカ
等、は、本発明のような三次元細孔構造を持たないた
め、「多孔質構造」とはいっても本発明による原子レベ
ルでの高分散担持に比べれば担持形態は平面的であっ
た。Alumina, zirconia, silica-alumina, silica, etc., which have been used as carriers in conventional exhaust gas purification catalysts, do not have the three-dimensional pore structure of the present invention, and are therefore called "porous structures". Also, compared with the highly dispersed carrier at the atomic level according to the present invention, the carrier form was planar.
【0016】また、やはり従来から担体として用いられ
ていたZSM-5に代表されるゼオライトは、本発明と
同等の三次元細孔構造を有するが、骨格を形成するSi
O2が吸蔵元素と反応してガラス化してしまうため、吸
蔵還元型の排気ガス浄化触媒の担体として用いることは
できない。Zeolite represented by ZSM-5, which has also been conventionally used as a carrier, has a three-dimensional pore structure equivalent to that of the present invention, but Si which forms a skeleton.
Since O 2 reacts with the storage element to become vitrified, it cannot be used as a carrier of the storage reduction type exhaust gas purification catalyst.
【0017】[0017]
【実施例】〔実施例1〕本発明により、ホーランダイト
型結晶構造を有するマンガン酸化物から成る担体に、N
Ox吸蔵材としてのバリウム(Ba)と還元触媒として
の白金(Pt)を担持した排気ガス浄化触媒を下記の手
順で作製した。[Example 1] According to the present invention, a carrier comprising manganese oxide having a hollandite type crystal structure
An exhaust gas purification catalyst carrying barium (Ba) as an Ox storage material and platinum (Pt) as a reduction catalyst was produced by the following procedure.
【0018】<担体:ホーランダイト型マンガン酸化物
の調製>200mlのイオン交換水にKMnO411.
8gを溶解した水溶液を調製した。<Support: Preparation of hollandite type manganese oxide> KMnO 4 11.
An aqueous solution in which 8 g was dissolved was prepared.
【0019】別に、60mlのイオン交換水にMnSO
4(脱水)11.6gを溶解した水溶液を調製した。Separately, 60 ml of ion-exchanged water was added to MnSO 4.
An aqueous solution in which 11.6 g of 4 (dehydrated) was dissolved was prepared.
【0020】上記2種の水溶液を混合した後、濃硝酸6
mlを加えた。After mixing the above two aqueous solutions, concentrated nitric acid 6
ml was added.
【0021】得られた混合溶液を、容積300mlのオ
ートクレーブに入れて、100℃×24時間の水熱合成
を行った。The obtained mixed solution was placed in an autoclave having a volume of 300 ml and subjected to hydrothermal synthesis at 100 ° C. for 24 hours.
【0022】水熱合成による生成物を濾過して固形分を
回収し,イオン交換水で洗浄した後、120℃で乾燥し
て、粉末サンプルを得た。The product obtained by hydrothermal synthesis was filtered to collect solids, washed with ion-exchanged water, and dried at 120 ° C. to obtain a powder sample.
【0023】上記の手順でサンプル粉末を5バッチ調製
した。Five batches of sample powder were prepared by the above procedure.
【0024】得られたサンプル粉末についてX線回折を
行ったところ、ホーランダイト型結晶構造を持つことが
確認された。CuKα線によるX線回折チャートの例を
図1に示す。When the obtained sample powder was subjected to X-ray diffraction, it was confirmed to have a hollandite type crystal structure. An example of an X-ray diffraction chart using CuKα rays is shown in FIG.
【0025】また、上記サンプル粉末の比表面積は13
5m2g−1であった。The specific surface area of the sample powder is 13
It was 5 m < 2 > g <-1 >.
【0026】<触媒作製:バリウム(Ba)および白金
(Pt)の担持>上記で作製したホーランダイト型マン
ガン酸化物粉末20gを水に分散させ、これに酢酸バリ
ウム8.5gを加えた後、濃縮乾固して、酢酸バリウム
担持粉末とした。<Catalyst Preparation: Supporting Barium (Ba) and Platinum (Pt)> 20 g of the hollandite-type manganese oxide powder prepared above was dispersed in water, and 8.5 g of barium acetate was added thereto, followed by concentration. It was dried to obtain barium acetate-supported powder.
【0027】この酢酸バリウム担持粉末を550℃で2
時間焼成した。This barium acetate-supported powder was heated at 550 ° C. for 2 hours.
Burned for hours.
【0028】炭酸アンモニウム(NH4HCO3)2.
1gを300gの水に溶解した水溶液に、上記焼成後の
酢酸バリウム担持粉末を分散させ、15分間攪拌した
後、吸引濾過した固形分を乾燥して、炭酸バリウム担持
粉末とした。Ammonium carbonate (NH 4 HCO 3 ) 2.
The barium acetate-supporting powder after firing was dispersed in an aqueous solution in which 1 g was dissolved in 300 g of water, and after stirring for 15 minutes, the solid content filtered by suction was dried to obtain a barium carbonate-supporting powder.
【0029】この炭酸バリウム担持粉末を300gの水
に分散させ、これに、白金(Pt)のモル数が1.71
×10−3molとなるようにジニトロジアミン白金錯
体溶液を加え、30分間攪拌した後、濃縮乾燥して粉末
を回収した。This barium carbonate-supporting powder was dispersed in 300 g of water, and the number of moles of platinum (Pt) was 1.71.
A dinitrodiamine platinum complex solution was added so as to have a concentration of × 10 -3 mol, the mixture was stirred for 30 minutes, and then concentrated and dried to recover a powder.
【0030】この粉末を110℃で2時間乾燥した後、
450℃で2時間焼成した。After drying this powder at 110 ° C. for 2 hours,
It was baked at 450 ° C. for 2 hours.
【0031】これにより、ホーランダイト型マンガン酸
化物から成る担体に、NOx吸蔵材としてのバリウム
(Ba)と、還元触媒としての白金(Pt)とが担持さ
れた粉末状の排気ガス浄化触媒が得られた。As a result, a powdery exhaust gas purifying catalyst in which barium (Ba) as a NOx storage material and platinum (Pt) as a reducing catalyst are supported on a carrier made of hollandite type manganese oxide is obtained. Was given.
【0032】得られた触媒粉末は、白金(Pt)の担持
濃度が触媒粉末1g当たり8.54×10−5mol、
バリウム(Ba)の担持濃度が触媒粉末1g当たり1.
67×10−3molである。The obtained catalyst powder had a supported concentration of platinum (Pt) of 8.54 × 10 −5 mol per 1 g of the catalyst powder,
The supported concentration of barium (Ba) was 1.
It is 67 × 10 −3 mol.
【0033】上記触媒粉末を直径1〜3mmのペレット
に成形して、試験に供した。The above catalyst powder was molded into pellets having a diameter of 1 to 3 mm and subjected to a test.
【0034】〔実施例2〕本発明により、ホーランダイ
ト型結晶構造を有するマンガン酸化物から成る担体に、
NOx吸蔵材としてのバリウム(K)と還元触媒として
の白金(Pt)を担持した排気ガス浄化触媒を下記の手
順で作製した。Example 2 According to the present invention, a carrier composed of manganese oxide having a hollandite type crystal structure,
An exhaust gas purification catalyst carrying barium (K) as a NOx storage material and platinum (Pt) as a reduction catalyst was produced by the following procedure.
【0035】実施例1で作製したホーランダイト型マン
ガン酸化物粉末20gを300gの水に分散させ、これ
に、白金(Pt)のモル数が1.71×10−3mol
となるようにジニトロジアミン白金錯体溶液を加え、3
0分間攪拌した後、濃縮乾燥して粉末を回収した。20 g of the hollandite-type manganese oxide powder prepared in Example 1 was dispersed in 300 g of water, and the number of moles of platinum (Pt) was 1.71 × 10 −3 mol.
Add the dinitrodiamine platinum complex solution so that
After stirring for 0 minutes, the powder was collected by concentration and drying.
【0036】この粉末を110℃で2時間乾燥した後、
450℃で2時間焼成して、白金(Pt)担持粉末とし
た。After drying this powder at 110 ° C. for 2 hours,
It was baked at 450 ° C. for 2 hours to obtain a platinum (Pt) -supported powder.
【0037】上記焼成後の白金担持粉末を200mlの
水に分散させ、これに酢酸カリウム3.26gを加えた
後、濃縮乾燥して粉末を回収した。The platinum-supported powder after firing was dispersed in 200 ml of water, 3.26 g of potassium acetate was added thereto, and the mixture was concentrated and dried to recover the powder.
【0038】この粉末を120℃で2時間乾燥した後、
550℃で2時間焼成した。After drying this powder at 120 ° C. for 2 hours,
It was baked at 550 ° C. for 2 hours.
【0039】これにより、ホーランダイト型マンガン酸
化物から成る担体に、NOx吸蔵材としてのカリウム
(K)と、還元触媒としての白金(Pt)とが担持され
た粉末状の排気ガス浄化触媒が得られた。As a result, a powdery exhaust gas purifying catalyst in which potassium (K) as a NOx storage material and platinum (Pt) as a reducing catalyst are supported on a carrier made of hollandite type manganese oxide is obtained. Was given.
【0040】得られた触媒粉末は、白金(Pt)の担持
濃度が触媒粉末1g当たり8.54×10−5mol、
カリウム(K)の担持濃度が触媒粉末1g当たり1.6
7×10−3molである。The obtained catalyst powder had a supported concentration of platinum (Pt) of 8.54 × 10 −5 mol per 1 g of the catalyst powder,
The supported concentration of potassium (K) was 1.6 per 1 g of catalyst powder.
It is 7 × 10 −3 mol.
【0041】上記触媒粉末を直径1〜3mmのペレット
に成形して、試験に供した。The above catalyst powder was molded into pellets having a diameter of 1 to 3 mm and subjected to a test.
【0042】〔比較例1〕比較のために、実施例1にお
けるホーランダイト型マンガン酸化物に代えて、従来の
γ−アルミナ(γ−Al2O3)を担体とした用いた以
外は、実施例1と同様にして排気ガス浄化触媒を作製
し、ペレットの成形して試験に供した。Comparative Example 1 For comparison, except that the conventional γ-alumina (γ-Al 2 O 3 ) was used as a carrier instead of the hollandite-type manganese oxide in Example 1, execution was carried out. An exhaust gas purification catalyst was produced in the same manner as in Example 1, pellets were molded and subjected to the test.
【0043】〔比較例2〕比較のために、実施例2にお
けるホーランダイト型マンガン酸化物に代えて、従来の
γ−アルミナ(γ−Al2O3)を担体とした用いた以
外は、実施例1と同様にして排気ガス浄化触媒を作製
し、ペレットに成形して試験に供した。[Comparative Example 2] For comparison, an experiment was conducted except that the conventional γ-alumina (γ-Al 2 O 3 ) was used as a carrier instead of the hollandite type manganese oxide in Example 2. An exhaust gas purification catalyst was produced in the same manner as in Example 1, molded into pellets, and subjected to the test.
【0044】実施例1、2および比較例1、2により作
製した触媒ペレットについて、下記条件にてモデルガス
評価試験を行った。A model gas evaluation test was conducted on the catalyst pellets produced in Examples 1 and 2 and Comparative Examples 1 and 2 under the following conditions.
【0045】<モデルガス評価試験>触媒ペレットを反
応容器内に配置し、表1に示すモデル排気ガスをガス空
間速度100,000h−1にて導入した。<Model Gas Evaluation Test> The catalyst pellets were placed in a reaction vessel, and the model exhaust gas shown in Table 1 was introduced at a gas space velocity of 100,000 h −1 .
【0046】触媒床温度を200〜600℃の範囲で種
々に設定し、リッチガス定常状態からリーンガス定常状
態に切り換えて、反応容器から排出されるガスのNOx
濃度が定常状態になるまでに触媒が吸蔵したNOx量
(NOx飽和吸蔵量)を測定した。The catalyst bed temperature is variously set in the range of 200 to 600 ° C., the rich gas steady state is switched to the lean gas steady state, and NOx of the gas discharged from the reaction vessel is changed.
The amount of NOx stored by the catalyst until the concentration reached a steady state (NOx saturated storage amount) was measured.
【0047】[0047]
【表1】 [Table 1]
【0048】図2に、吸蔵材がバリウム(Ba)である
実施例1および比較例1についての測定結果を示し、図
3に、吸蔵材がカリウム(K)である実施例2および比
較例2についての測定結果を示す。FIG. 2 shows the measurement results of Example 1 and Comparative Example 1 in which the storage material is barium (Ba), and FIG. 3 shows Example 2 and Comparative Example 2 in which the storage material is potassium (K). The measurement result of is shown.
【0049】各図から、いずれの吸蔵材を用いた場合
も、従来のようにγ−アルミナを担体とする比較例1、
2に比べて、本発明によるホーランダイト型マンガン酸
化物を担体とする実施例1、2は、NOx吸蔵量が格段
に向上していることが分かる。これは、本発明の触媒は
担体として用いたホーランダイト型マンガン酸化物の三
次元細孔が、吸蔵材としてのバリウムまたはカリウムを
原子レベルで高分散に担持し、かつ触媒中で排気ガスを
十分に拡散させるためであると考えられる。同様に、還
元触媒としての白金も三次元細孔に原子レベルで高分散
に担持されていると考えられ、NOxの吸蔵能力および
放出ガスの還元能力が向上し、高い浄化能力を備えた排
気ガス浄化触媒が得られる。From each figure, no matter which storage material was used, Comparative Example 1 using γ-alumina as a carrier as in the conventional case,
It can be seen that the NOx storage amount is significantly improved in Examples 1 and 2 in which the hollandite-type manganese oxide according to the present invention is used as a carrier, as compared with 2. This is because three-dimensional pores of hollandite-type manganese oxide used as a carrier in the catalyst of the present invention carry barium or potassium as a storage material in a highly dispersed manner at the atomic level, and exhaust gas is sufficiently contained in the catalyst. It is thought to be for the purpose of diffusion. Similarly, it is considered that platinum as a reducing catalyst is also highly dispersed and supported on the three-dimensional pores at the atomic level, and the NOx storage capacity and the exhaust gas reduction capacity are improved, and the exhaust gas with high purification capacity is provided. A purification catalyst is obtained.
【0050】[0050]
【発明の効果】本発明によれば、担体としてホーランダ
イト型結晶構造を有するマンガン酸化物を用いたことに
より、吸蔵材および還元触媒を三次元細孔に原子レベル
で高分散に担持できるため、従来の触媒では得られなか
った高いNOx浄化能力が得られる。According to the present invention, since the manganese oxide having a hollandite type crystal structure is used as the carrier, the occluding material and the reducing catalyst can be carried in the three-dimensional pores at a high atomic level dispersion. A high NOx purification capacity that cannot be obtained with conventional catalysts can be obtained.
【図1】図1は、本発明によるホーランダイト型結晶構
造マンガン酸化物のX線回折チャートの一例を示すグラ
フである。FIG. 1 is a graph showing an example of an X-ray diffraction chart of a hollandite type crystal structure manganese oxide according to the present invention.
【図2】図2は、種々の温度におけるNOx飽和吸蔵量
を、本発明によるホーランダイト型結晶構造マンガン酸
化物から成る担体にNOx吸蔵材としてのバリウム(B
a)と還元触媒としての白金(Pt)とを担持させた触
媒(実施例1)と、従来のγ−アルミナ(γ−Al2O
3)から成る担体に同じ吸蔵材および白金を担持させた
触媒(比較例1)とについて比較して示すグラフであ
る。FIG. 2 is a graph showing the saturated storage amount of NOx at various temperatures in a carrier made of hollandite type crystal structure manganese oxide according to the present invention as barium (B) as a NOx storage material.
a) and a catalyst supporting platinum (Pt) as a reduction catalyst (Example 1) and conventional γ-alumina (γ-Al 2 O).
3 is a graph showing comparison with a catalyst (Comparative Example 1) in which the same occlusion material and platinum are supported on a carrier composed of 3 ).
【図3】図3は、種々の温度におけるNOx飽和吸蔵量
を、本発明によるホーランダイト型結晶構造マンガン酸
化物から成る担体にNOx吸蔵材としてのカリウム
(K)と還元触媒としての白金(Pt)とを担持させた
触媒(実施例2)と、従来のγ−アルミナ(γ−Al2
O3)から成る担体に同じ吸蔵材および白金を担持させ
た触媒(比較例2)とについて比較して示すグラフであ
る。FIG. 3 is a graph showing the NOx saturated storage amount at various temperatures in a carrier composed of hollandite-type crystal structure manganese oxide according to the present invention, potassium (K) as a NOx storage material, and platinum (Pt) as a reduction catalyst. ) And a conventional catalyst (Example 2) and conventional γ-alumina (γ-Al 2
3 is a graph showing a comparison of a catalyst (Comparative Example 2) in which the same storage material and platinum are supported on a carrier made of O 3 ).
───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D048 AA06 AA13 AA18 AB05 BA01Y BA02Y BA14X BA15X BA18Y BA28X BA30X BA31X BA33Y BA41X BB01 EA04 4G069 AA03 BB02A BB02B BB04A BB04B BC01A BC03A BC03B BC08A BC13A BC13B BC38A BC62A BC62B BC71A BC72A BC75A BC75B CA02 CA03 CA08 CA09 CA13 EA02Y EB18Y EC22X EC22Y ─────────────────────────────────────────────────── ─── Continued front page F-term (reference) 4D048 AA06 AA13 AA18 AB05 BA01Y BA02Y BA14X BA15X BA18Y BA28X BA30X BA31X BA33Y BA41X BB01 EA04 4G069 AA03 BB02A BB02B BB04A BB04B BC01A BC03A BC03B BC08A BC13A BC13B BC38A BC62A BC62B BC71A BC72A BC75A BC75B CA02 CA03 CA08 CA09 CA13 EA02Y EB18Y EC22X EC22Y
Claims (3)
と、この吸蔵材から放出された浄化対象物質を還元浄化
する還元触媒とを担持させた吸蔵還元型の排気ガス浄化
触媒において、 ホーランダイト型結晶構造を有するマンガン酸化物から
成る担体に、吸蔵材としての窒素酸化物吸蔵元素と、還
元触媒としての貴金属とを担持して成ることを特徴とす
る排気ガス浄化触媒。1. An occlusion-reduction type exhaust gas purifying catalyst in which a carrier carries an occlusion material for occlusion of a substance to be purified and a reduction catalyst for reducing and purifying the substance to be purified released from the occlusion material, An exhaust gas purifying catalyst, characterized in that a carrier made of manganese oxide having a dite-type crystal structure carries a nitrogen oxide storage element as a storage material and a noble metal as a reduction catalyst.
属、アルカリ土類金属および希土類金属から成る群から
選択されることを特徴とする請求項1記載の排気ガス浄
化触媒。2. The exhaust gas purifying catalyst according to claim 1, wherein the nitrogen oxide storage element is selected from the group consisting of alkali metals, alkaline earth metals and rare earth metals.
成る群から選択されることを特徴とする請求項1または
2記載の排気ガス浄化触媒。3. The exhaust gas purifying catalyst according to claim 1, wherein the metal is selected from the group consisting of Pt, Pd and Rh.
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JP2001376147A JP2003170050A (en) | 2001-12-10 | 2001-12-10 | Exhaust gas cleaning catalyst |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2001376147A JP2003170050A (en) | 2001-12-10 | 2001-12-10 | Exhaust gas cleaning catalyst |
Publications (1)
Publication Number | Publication Date |
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JP2003170050A true JP2003170050A (en) | 2003-06-17 |
Family
ID=19184400
Family Applications (1)
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2019525831A (en) * | 2016-06-30 | 2019-09-12 | ビーエーエスエフ コーポレーション | Manganese oxide catalyst and catalytic device for removing formaldehyde and volatile organic compounds |
CN112717922A (en) * | 2019-10-28 | 2021-04-30 | 中国石油化工股份有限公司 | Tert-butyl alcohol pretreatment catalyst and preparation method and application thereof |
-
2001
- 2001-12-10 JP JP2001376147A patent/JP2003170050A/en active Pending
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2019525831A (en) * | 2016-06-30 | 2019-09-12 | ビーエーエスエフ コーポレーション | Manganese oxide catalyst and catalytic device for removing formaldehyde and volatile organic compounds |
JP7173871B2 (en) | 2016-06-30 | 2022-11-16 | ビーエーエスエフ コーポレーション | Manganese oxide based catalyst and catalytic device for removing formaldehyde and volatile organic compounds |
CN112717922A (en) * | 2019-10-28 | 2021-04-30 | 中国石油化工股份有限公司 | Tert-butyl alcohol pretreatment catalyst and preparation method and application thereof |
CN112717922B (en) * | 2019-10-28 | 2023-01-10 | 中国石油化工股份有限公司 | Tert-butyl alcohol pretreatment catalyst and preparation method and application thereof |
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