JPH08229401A - Oxide catalyst material for removing nitrogen oxide and removal of nitrogen oxide - Google Patents
Oxide catalyst material for removing nitrogen oxide and removal of nitrogen oxideInfo
- Publication number
- JPH08229401A JPH08229401A JP7037314A JP3731495A JPH08229401A JP H08229401 A JPH08229401 A JP H08229401A JP 7037314 A JP7037314 A JP 7037314A JP 3731495 A JP3731495 A JP 3731495A JP H08229401 A JPH08229401 A JP H08229401A
- Authority
- JP
- Japan
- Prior art keywords
- weight
- parts
- palladium
- rhodium
- platinum
- 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 46
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 title claims description 90
- 239000000463 material Substances 0.000 title claims description 30
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 claims abstract description 72
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims abstract description 59
- 239000010948 rhodium Substances 0.000 claims abstract description 37
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims abstract description 34
- 229910052763 palladium Inorganic materials 0.000 claims abstract description 24
- 229910052697 platinum Inorganic materials 0.000 claims abstract description 22
- 229910052703 rhodium Inorganic materials 0.000 claims abstract description 22
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 claims abstract description 22
- 229910052762 osmium Inorganic materials 0.000 claims abstract description 21
- SYQBFIAQOQZEGI-UHFFFAOYSA-N osmium atom Chemical compound [Os] SYQBFIAQOQZEGI-UHFFFAOYSA-N 0.000 claims abstract description 21
- 229910052751 metal Inorganic materials 0.000 claims abstract description 17
- 229910052733 gallium Inorganic materials 0.000 claims abstract description 16
- 229910052759 nickel Inorganic materials 0.000 claims abstract description 15
- GYHNNYVSQQEPJS-UHFFFAOYSA-N Gallium Chemical compound [Ga] GYHNNYVSQQEPJS-UHFFFAOYSA-N 0.000 claims abstract description 8
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims abstract description 4
- 239000007789 gas Substances 0.000 claims description 36
- 238000000034 method Methods 0.000 claims description 19
- 229910018072 Al 2 O 3 Inorganic materials 0.000 claims description 15
- 229910052760 oxygen Inorganic materials 0.000 claims description 14
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 13
- 239000001301 oxygen Substances 0.000 claims description 13
- 229910052596 spinel Inorganic materials 0.000 claims description 10
- 239000011029 spinel Substances 0.000 claims description 10
- 239000002131 composite material Substances 0.000 claims description 9
- 229910052799 carbon Inorganic materials 0.000 claims description 7
- 230000001603 reducing effect Effects 0.000 claims description 6
- 230000001590 oxidative effect Effects 0.000 claims description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 4
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims 2
- 229910052757 nitrogen Inorganic materials 0.000 claims 1
- 239000000843 powder Substances 0.000 abstract description 13
- 239000013078 crystal Substances 0.000 abstract description 10
- 238000002156 mixing Methods 0.000 abstract description 4
- 229910018404 Al2 O3 Inorganic materials 0.000 abstract 1
- 229910000510 noble metal Inorganic materials 0.000 description 13
- 230000010757 Reduction Activity Effects 0.000 description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 9
- 239000012071 phase Substances 0.000 description 8
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 6
- 229910002091 carbon monoxide Inorganic materials 0.000 description 6
- 238000002485 combustion reaction Methods 0.000 description 6
- 238000010438 heat treatment Methods 0.000 description 6
- 239000002184 metal Substances 0.000 description 6
- 238000006722 reduction reaction Methods 0.000 description 6
- 238000011156 evaluation Methods 0.000 description 5
- 238000004519 manufacturing process Methods 0.000 description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 4
- 238000002441 X-ray diffraction Methods 0.000 description 4
- 229910021536 Zeolite Inorganic materials 0.000 description 4
- 230000003197 catalytic effect Effects 0.000 description 4
- 239000003638 chemical reducing agent Substances 0.000 description 4
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 4
- 230000009467 reduction Effects 0.000 description 4
- 239000010457 zeolite Substances 0.000 description 4
- 238000006243 chemical reaction Methods 0.000 description 3
- 239000000446 fuel Substances 0.000 description 3
- 229930195733 hydrocarbon Natural products 0.000 description 3
- 150000002430 hydrocarbons Chemical class 0.000 description 3
- 239000011812 mixed powder Substances 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- 230000002829 reductive effect Effects 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 238000012360 testing method Methods 0.000 description 3
- 238000003915 air pollution Methods 0.000 description 2
- 229910021529 ammonia Inorganic materials 0.000 description 2
- 239000007864 aqueous solution Substances 0.000 description 2
- 239000006227 byproduct Substances 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000001307 helium Substances 0.000 description 2
- 229910052734 helium Inorganic materials 0.000 description 2
- SWQJXJOGLNCZEY-UHFFFAOYSA-N helium atom Chemical compound [He] SWQJXJOGLNCZEY-UHFFFAOYSA-N 0.000 description 2
- 230000002209 hydrophobic effect Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 239000012495 reaction gas Substances 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 238000010792 warming Methods 0.000 description 2
- -1 3 H 6 and C 3 H 8 Chemical class 0.000 description 1
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 1
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 1
- 150000001242 acetic acid derivatives Chemical class 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 150000004703 alkoxides Chemical class 0.000 description 1
- 235000011114 ammonium hydroxide Nutrition 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 238000010531 catalytic reduction reaction Methods 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 230000008094 contradictory effect Effects 0.000 description 1
- 229910052878 cordierite Inorganic materials 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 230000008025 crystallization Effects 0.000 description 1
- JSKIRARMQDRGJZ-UHFFFAOYSA-N dimagnesium dioxido-bis[(1-oxido-3-oxo-2,4,6,8,9-pentaoxa-1,3-disila-5,7-dialuminabicyclo[3.3.1]nonan-7-yl)oxy]silane Chemical compound [Mg++].[Mg++].[O-][Si]([O-])(O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2)O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2 JSKIRARMQDRGJZ-UHFFFAOYSA-N 0.000 description 1
- 239000012153 distilled water Substances 0.000 description 1
- 238000004945 emulsification Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000005755 formation reaction Methods 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 238000013508 migration Methods 0.000 description 1
- 230000005012 migration Effects 0.000 description 1
- 150000002823 nitrates Chemical class 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 239000011819 refractory material Substances 0.000 description 1
- 238000012827 research and development Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 238000003980 solgel method Methods 0.000 description 1
- 238000003746 solid phase reaction Methods 0.000 description 1
- 239000007858 starting material Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 238000005303 weighing Methods 0.000 description 1
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、窒素酸化物を還元除去
することのできる新規な酸化物触媒材料並びにこれを用
いて排気ガス中の窒素酸化物を除去する方法に関するも
ので、とりわけ排気ガス温度が低いディーゼルエンジン
等の窒素酸化物還元除去用触媒並びに該触媒を用いて低
温で排気ガス中の窒素酸化物を除去する方法に関するも
のである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a novel oxide catalyst material capable of reducing and removing nitrogen oxides, and a method for removing nitrogen oxides in exhaust gas using the same, and more particularly to exhaust gas. The present invention relates to a catalyst for nitrogen oxide reduction and removal in diesel engines and the like having a low temperature, and a method for removing nitrogen oxide in exhaust gas at low temperature using the catalyst.
【0002】[0002]
【従来の技術】近年、各種汚染物質による大気の汚れが
大きな社会問題となり、その中でも大気汚染の移動発生
源となっている自動車の排気ガス中のNOX 、COX 等
の有害物質を分解、除去する方法の開発が急務となって
いる。2. Description of the Related Art In recent years, air pollution caused by various pollutants has become a major social problem, and among them, harmful substances such as NO x and CO x in exhaust gas of automobiles, which are sources of migration of air pollution, are decomposed. There is an urgent need to develop a method for removal.
【0003】従来より自動車の排気ガス中のNOX 、C
OX 等の有害物質を分解、除去する方法として、一酸化
炭素(CO)及び炭化水素(CX HX )の酸化と、窒素
酸化物(NOX )の還元を同時に行う三元触媒を用いる
方法が採用されてきた。Conventionally, NO x , C in the exhaust gas of automobiles
Decomposing harmful substances O X such as a method of removing, using an oxidation of carbon monoxide (CO) and hydrocarbons (C X H X), nitrogen oxide three-way catalyst to perform reduction at the same time the (NO X) The method has been adopted.
【0004】そのような方法に用いられる三元触媒とし
ては、γ−アルミナ(Al2 O3 )で被覆したコージェ
ライト等の耐火物に、パラジウム(Pd)、白金(P
t)、ロジウム(Rh)等の貴金属を担持したものが用
いられていた。As a three-way catalyst used in such a method, a refractory material such as cordierite coated with γ-alumina (Al 2 O 3 ) is used, and palladium (Pd) or platinum (Pd) is used.
t) and those carrying a noble metal such as rhodium (Rh) have been used.
【0005】しかしながら、前記三元触媒は、およそ
0.5%程度の低酸素濃度においてのみ排気ガスの浄化
を効率よく行うことができるが、排気ガスの酸素濃度が
1%を越えるような高濃度域では有効に働かなくなると
いう欠点がある。However, although the three-way catalyst can efficiently purify the exhaust gas only at a low oxygen concentration of about 0.5%, the three-way catalyst has a high oxygen concentration of more than 1%. It has the drawback of not working effectively in the region.
【0006】そこで、通常は排気ガス中の酸素濃度を測
定し、CO及びCX HX 、NOX を高い浄化率で処理し
得る理論等量値に近い範囲の空燃比となるように制御す
ることが行われているが、前記CO及びCX HX と、N
OX の発生メカニズムが相反する特性を有するため、限
られた状態での燃焼を維持しなければならず、それより
高い酸素濃度中での排気ガス浄化はほとんどできていな
いのが現状である。Therefore, normally, the oxygen concentration in the exhaust gas is measured, and the air-fuel ratio is controlled so that CO, C X H X , and NO X can be processed at a high purification rate, and the air-fuel ratio is in a range close to the theoretical equivalent value. However, the CO and C X H X , and N
Since O X generation mechanisms have contradictory properties, it is necessary to support combustion in a state where limited exhaust gas purification at a high oxygen concentration in than it is at present, not hardly.
【0007】更に、昨今、省エネルギー、省資源も叫ば
れていることから、ガソリンエンジンにおいては、低燃
費化を図るために希薄燃焼方式の研究開発が行われてい
るが、この場合、排気ガス中の酸素濃度は数%と高くな
り、触媒の貴金属が酸素被毒により排気ガスの浄化がで
きなくなるという欠点がある。Further, since energy saving and resource saving have recently been demanded, in a gasoline engine, research and development of a lean combustion system have been carried out in order to achieve low fuel consumption. Has a disadvantage that the noble metal of the catalyst cannot be purified by exhaust gas due to oxygen poisoning.
【0008】またディーゼルエンジンにおいても、現在
の燃焼方式では排気ガス中の酸素濃度が高いために排気
ガスの浄化が全くなされていないのが現状である。Also in the diesel engine, in the present combustion system, the exhaust gas is not purified at all because the oxygen concentration in the exhaust gas is high.
【0009】一方、約1000℃以上の高温で発生し、
燃焼温度が高くなるほどその濃度が高くなるNOX を効
果的に浄化する方法としては、前記以外にアンモニアを
用いた選択的接触還元法があるが、工場等の固定式の燃
焼装置における酸素濃度の高い排気ガス中のNOX の浄
化に対しては有効ではあるものの、本方法を自動車等の
移動式燃焼装置に適用することは安全性の面で問題があ
る。On the other hand, it occurs at a high temperature of about 1000 ° C. or higher,
As a method of effectively purifying NO X , the concentration of which increases as the combustion temperature increases, there is a selective catalytic reduction method using ammonia in addition to the above method. Although effective for purifying NO x in high exhaust gas, applying this method to a mobile combustion device such as an automobile has a problem in safety.
【0010】そこで、前記諸問題を解消するものとし
て、金属を担持した疎水性ゼオライトを触媒として炭化
水素と接触させながらNOX を除去する方法が、特開平
4−349938号公報等に提案されている。[0010] Therefore, as to solve the above problems, a method of the hydrophobic zeolite carrying the metal removing NO X while in contact with the hydrocarbon as a catalyst, is proposed in JP-A 4-349938 Patent Publication There is.
【0011】[0011]
【発明が解決しようとする課題】しかしながら、前記金
属を担持した疎水性ゼオライトを触媒とするものは耐水
性が悪く、例えば、ディーゼルエンジンのように排気ガ
ス中に水分を含む場合には、水蒸気の存在によりNOX
の浄化率の経時低下が大きいという課題があり、更に、
その排気ガス温度が350℃以下と低い場合には、前記
触媒はNO還元活性が低く、その用途が限定される上、
更に、副生成ガスとして地球温暖化の原因とされている
N2 Oが発生するという課題もあり、耐熱性だけではな
く耐水性にも優れ、かつ350℃以下の低温度域まで広
範囲に渡ってNO還元活性を示し、N2 Oを生成しない
触媒材料が望まれていた。However, a catalyst using the above-mentioned metal-supporting hydrophobic zeolite as a catalyst has poor water resistance. For example, when water is contained in exhaust gas such as a diesel engine, water vapor NO X by existence
There is a problem that the purification rate of
When the exhaust gas temperature is as low as 350 ° C. or lower, the catalyst has low NO reduction activity, and its use is limited.
Furthermore, there is a problem that N 2 O, which is a cause of global warming, is generated as a by-product gas, and not only heat resistance is excellent, but also water resistance is excellent, and it is widely used in a low temperature range of 350 ° C. or lower. A catalyst material that exhibits NO reduction activity and does not generate N 2 O has been desired.
【0012】[0012]
【発明の目的】本発明はアンモニア等の毒性の強い還元
剤を必要とせず、ディーゼルエンジン等の水分を含む酸
素濃度の高い比較的低温の排気ガスを、該排気ガスの流
速が高速度であっても、N2 Oを生成することなく広範
囲の温度域で有効に排気ガス中のNOX を浄化すること
ができる有用な触媒材料並びにそれを用いた窒素酸化物
除去方法を提供するものである。SUMMARY OF THE INVENTION The present invention does not require a highly toxic reducing agent such as ammonia, and provides a relatively low-temperature exhaust gas having a high oxygen concentration containing water, such as a diesel engine, with a high flow velocity of the exhaust gas. Even so, the present invention provides a useful catalyst material capable of effectively purifying NO x in exhaust gas in a wide temperature range without producing N 2 O, and a nitrogen oxide removing method using the same. .
【0013】[0013]
【課題を解決するための手段】本発明は、上記課題に鑑
みなされたもので、ニッケル(Ni)およびガリウム
(Ga)を主たる金属元素として含有する結晶相がスピ
ネル型構造である複合酸化物にアルミナ(Al2 O3 )
を混合した担持体に、貴金属であるパラジウム(Pd)
と、同じく白金(Pt)、ロジウム(Rh)、オスミウ
ム(Os)の内、少なくとも一種を担持した酸化物触媒
材料が、水蒸気存在下の高い酸素濃度でも広い温度範囲
に渡って優れた触媒活性を長期にわたり有することを見
出したものである。The present invention has been made in view of the above problems, and provides a composite oxide having a spinel structure as a crystal phase containing nickel (Ni) and gallium (Ga) as main metal elements. Alumina (Al 2 O 3 )
Noble metal palladium (Pd)
Similarly, an oxide catalyst material supporting at least one of platinum (Pt), rhodium (Rh), and osmium (Os) exhibits excellent catalytic activity over a wide temperature range even at high oxygen concentration in the presence of water vapor. It has been found to have a long term.
【0014】即ち、本発明の窒素酸化物除去用酸化物触
媒材料は、ニッケル(Ni)およびガリウム(Ga)を
主たる金属元素として含有し、その結晶相がスピネル型
構造を有する複合酸化物粉末とAl2 O3 粉末を混合し
た担持体に、パラジウム(Pd)と、白金(Pt)、ロ
ジウム(Rh)、オスミウム(Os)の内、少なくとも
一種を前記担持体100重量部に対して合計0.05〜
0.4重量部担持したことを特徴とするものである。That is, the oxide catalyst material for removing nitrogen oxides of the present invention contains a composite oxide powder containing nickel (Ni) and gallium (Ga) as main metal elements and having a crystal phase having a spinel type structure. Palladium (Pd), platinum (Pt), rhodium (Rh), and osmium (Os) were added to a support in which Al 2 O 3 powder was mixed, and at least one of them was added in a total amount of 0. 05-
It is characterized by carrying 0.4 parts by weight.
【0015】特に、前記パラジウム(Pd)と、白金
(Pt)、ロジウム(Rh)、オスミウム(Os)の
内、少なくとも一種を前記担持体100重量部に対して
合計0.07〜0.3重量部担持した酸化物触媒材料で
あることが好ましく、とりわけ主成分として前記パラジ
ウム(Pd)を50重量%以上含有し、該主成分と白金
(Pt)、ロジウム(Rh)、オスミウム(Os)の
内、少なくとも一種を前記担持体100重量部に対して
合計0.07〜0.2重量部担持したものが最も好まし
い。In particular, at least one of palladium (Pd), platinum (Pt), rhodium (Rh), and osmium (Os) is added in a total amount of 0.07 to 0.3 parts by weight per 100 parts by weight of the carrier. It is preferable that the oxide catalyst material is partially supported, and in particular, contains 50% by weight or more of the palladium (Pd) as a main component, and among the main component and platinum (Pt), rhodium (Rh), and osmium (Os). It is most preferable that at least one kind is supported in a total amount of 0.07 to 0.2 parts by weight with respect to 100 parts by weight of the carrier.
【0016】更に、本発明の窒素酸化物除去方法は、高
濃度の酸素と還元性を有する炭素含有ガスが存在する酸
化雰囲気中で、ニッケル(Ni)とガリウム(Ga)を
主たる金属元素として含有する結晶相がスピネル型構造
である複合酸化物に、Al2O3 を混合した担持体に、
パラジウム(Pd)と、白金(Pt)、ロジウム(R
h)、オスミウム(Os)の内、少なくとも一種を前記
担持体100重量部に対して合計0.05〜0.4重量
部担持して成る酸化物触媒材料と、窒素酸化物を含む排
気ガスを接触させることを特徴とするものである。Further, the method for removing nitrogen oxides of the present invention contains nickel (Ni) and gallium (Ga) as main metal elements in an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present. To a carrier prepared by mixing Al 2 O 3 with a complex oxide whose crystal phase is a spinel structure,
Palladium (Pd), platinum (Pt), rhodium (R
h), an oxide catalyst material formed by supporting at least one of osmium (Os) in a total amount of 0.05 to 0.4 parts by weight with respect to 100 parts by weight of the support, and an exhaust gas containing nitrogen oxides. It is characterized in that they are brought into contact with each other.
【0017】なかでも、前記酸化物触媒材料として、パ
ラジウム(Pd)と、白金(Pt)、ロジウム(R
h)、オスミウム(Os)の内、少なくとも一種を担持
体100重量部に対して合計0.07〜0.3重量部担
持したものを用いることが望ましく、更に、主成分とし
て前記パラジウム(Pd)を50重量%以上含有し、該
主成分と白金(Pt)、ロジウム(Rh)、オスミウム
(Os)の内、少なくとも一種を前記担持体100重量
部に対して合計0.07〜0.2重量部担持したものを
用いることが最も好ましい。Among them, as the oxide catalyst material, palladium (Pd), platinum (Pt) and rhodium (R) are used.
It is desirable to use at least one of h) and osmium (Os) which is carried in a total amount of 0.07 to 0.3 parts by weight with respect to 100 parts by weight of the carrier, and further, palladium (Pd) as the main component is used. Of 50% by weight or more, and the main component and at least one of platinum (Pt), rhodium (Rh), and osmium (Os) in total of 0.07 to 0.2 parts by weight relative to 100 parts by weight of the carrier. It is most preferable to use a partially supported one.
【0018】本発明において、前記窒素酸化物除去用酸
化物触媒材料として、前記担持体に貴金属であるパラジ
ウム(Pd)と、同じく白金(Pt)、ロジウム(R
h)、オスミウム(Os)の内、少なくとも一種を担持
体100重量部に対して合計0.05重量部未満しか担
持しなかった場合には、350℃以下の低温域ではNO
還元活性が現れず、逆に、0.4重量部を越えると、還
元剤の単純酸化反応だけが進行し、NO還元反応が現れ
ない。In the present invention, as the oxide catalyst material for removing nitrogen oxides, palladium (Pd), which is a noble metal, and platinum (Pt) and rhodium (R) are also used for the carrier.
h) and osmium (Os), when at least one of them is less than 0.05 parts by weight in total with respect to 100 parts by weight of the carrier, NO in a low temperature range of 350 ° C. or lower
On the contrary, when the amount exceeds 0.4 parts by weight, only the simple oxidation reaction of the reducing agent proceeds and the NO reduction reaction does not appear.
【0019】従って、前記窒素酸化物除去用酸化物触媒
材料は、前記担持体にパラジウム(Pd)と、白金(P
t)、ロジウム(Rh)、オスミウム(Os)の内、少
なくとも一種の合計量が、担持体100重量部に対して
合計0.05〜0.4重量部担持して成るものに限定さ
れ、触媒活性の点からは合計0.07〜0.3重量部担
持したものが望ましく、とりわけ広範囲の温度域での触
媒活性という点からは主成分としてパラジウム(Pd)
を50重量%以上含有し、該主成分との合計量が0.0
7〜0.2重量部であるものが最も好ましい。Therefore, in the oxide catalyst material for removing nitrogen oxides, the carrier is palladium (Pd) and platinum (Pd).
t), rhodium (Rh), and osmium (Os), the total amount of at least one kind is limited to a total amount of 0.05 to 0.4 parts by weight based on 100 parts by weight of the carrier, and a catalyst. From the viewpoint of activity, it is desirable to support a total of 0.07 to 0.3 parts by weight, and particularly palladium (Pd) as a main component from the viewpoint of catalytic activity in a wide temperature range.
Of 50% by weight or more, and the total amount of the main components is 0.0
Most preferred is 7 to 0.2 parts by weight.
【0020】尚、前記複合酸化物はニッケル(Ni)と
ガリウム(Ga)を主たる金属元素として含有し、一般
式としてNiGa2 O4 で表されるスピネル型構造の結
晶相を有するものであり、該複合酸化物のNiとGaの
相関は、Niに対するGaの蛍光X線分析によるカウン
ト比で論ずると、触媒活性の点からは1.4以上が望ま
しく、とりわけ1.5以上が最も好ましい。The composite oxide contains nickel (Ni) and gallium (Ga) as main metal elements and has a spinel type crystal phase represented by NiGa 2 O 4 as a general formula. The correlation between Ni and Ga of the composite oxide is preferably 1.4 or more, and most preferably 1.5 or more, from the viewpoint of catalytic activity, in terms of the count ratio of Ga to Ni by fluorescent X-ray analysis.
【0021】また、前記Al2 O3 は高い比表面積を有
するものが適当であると考えられ、実用的には60m2
/g以上が望ましく、また、Al2 O3 混合量による触
媒活性の変化は少ないものの、その混合量は20〜70
重量%が好ましく、25〜60重量%が最も望ましい。Further, it is considered appropriate that the Al 2 O 3 has a high specific surface area, and 60 m 2 is practically used.
/ G or more is desirable, and although the change in catalyst activity due to the Al 2 O 3 mixed amount is small, the mixed amount is 20 to 70.
Weight percent is preferred and 25-60 weight percent is most desirable.
【0022】更に、前記複合酸化物にAl2 O3 を混合
した担持体に、貴金属であるパラジウム(Pd)と、同
じく白金(Pt)、ロジウム(Rh)、オスミウム(O
s)の内、少なくとも一種を前記担持体100重量部に
対して合計0.05〜0.4重量部担持した酸化物触媒
材料と、窒素酸化物を含む排気ガスを接触させる際、該
排気ガス雰囲気中に、還元剤としてC2 H4 、C
3 H6 、C3 H8 等の炭化水素、CH3 OH、C2 H5
OH等のアルコールや、CO等の還元性を有する炭素ガ
ス等を含有させて、前記触媒材料と接触させると、NO
X 還元性が一層高くなる。Further, on the carrier in which Al 2 O 3 is mixed with the complex oxide, palladium (Pd) which is a noble metal, platinum (Pt), rhodium (Rh) and osmium (O) are also used.
In the case of contacting an exhaust gas containing nitrogen oxide with an oxide catalyst material supporting 0.05 to 0.4 parts by weight in total of 100 parts by weight of the carrier, the exhaust gas containing C 2 H 4 and C as reducing agents in the atmosphere
Hydrocarbons such as 3 H 6 and C 3 H 8 , CH 3 OH, C 2 H 5
When an alcohol such as OH or a reducing carbon gas such as CO is contained and brought into contact with the catalyst material, NO
X- reducing property becomes higher.
【0023】[0023]
【作用】本発明の窒素酸化物除去用酸化物触媒材料並び
に窒素酸化物除去方法によれば、酸化物触媒材料は、N
i及びGaを主たる金属元素として含有し、結晶相がス
ピネル型構造を有する複合酸化物と、Al2 O3 を混合
した担持体に、パラジウム(Pd)と、白金(Pt)、
ロジウム(Rh)、オスミウム(Os)の内、少なくと
も一種を前記担持体100重量部に対して合計0.05
〜0.4重量部担持したことから、350℃を越える高
温域では前記担持体中のAl2 O3 がNOを酸化してN
O2 の生成を促進し、NOよりNO2 に対する還元活性
の方が高い前記複合酸化物によって、NOX の還元分解
作用で高い特性を示す。According to the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention, the oxide catalyst material is N
Palladium (Pd), platinum (Pt), a mixed oxide containing i and Ga as main metal elements and having a crystal phase having a spinel structure and Al 2 O 3 were mixed,
At least one of rhodium (Rh) and osmium (Os) is added in a total amount of 0.05 based on 100 parts by weight of the carrier.
Since about 0.4 part by weight was supported, Al 2 O 3 in the carrier oxidizes NO in a high temperature range exceeding 350 ° C.
The composite oxide, which promotes the production of O 2 and has a higher reduction activity for NO 2 than NO, exhibits high characteristics due to the reductive decomposition action of NO X.
【0024】一方、350℃以下の低温域では、担持し
た前記2種以上の貴金属の触媒作用により、広範囲の温
度域でNO還元活性を示す。On the other hand, in the low temperature range of 350 ° C. or lower, NO reduction activity is exhibited in a wide temperature range due to the catalytic action of the two or more kinds of the noble metals carried.
【0025】更に、一般に貴金属担持触媒において、N
O還元反応の副生成物として生じるN2 Oは、本発明の
酸化物触媒材料では、担持体と貴金属との相互作用によ
りNOからN2 への反応の選択性が高くなることから、
N2 O生成反応は生じないと考えられる。Further, generally in noble metal-supported catalysts, N
In the oxide catalyst material of the present invention, N 2 O produced as a by-product of the O reduction reaction increases the selectivity of the reaction from NO to N 2 due to the interaction between the carrier and the noble metal.
It is considered that the N 2 O formation reaction does not occur.
【0026】[0026]
【実施例】以下、本発明の窒素酸化物除去用酸化物触媒
材料並びに窒素酸化物除去方法について、実施例に基づ
き詳細に述べる。EXAMPLES Hereinafter, the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention will be described in detail based on examples.
【0027】本発明の窒素酸化物除去用酸化物触媒材料
は、Ni及びGaを含有する原料粉末を所定量秤量し、
十分に攪拌混合した後、Al2 O3 粉末を添加し、酸化
雰囲気中、500〜1600℃の温度で5〜30時間熱
処理することにより、Ni及びGaを主たる金属元素と
するスピネル型結晶の複合酸化物とAl2 O3 から成る
混合粉末が得られる。The oxide catalyst material for removing nitrogen oxides of the present invention is obtained by weighing a predetermined amount of raw material powder containing Ni and Ga,
After sufficiently stirring and mixing, Al 2 O 3 powder was added, and heat treatment was performed at a temperature of 500 to 1600 ° C. for 5 to 30 hours in an oxidizing atmosphere to form a composite of spinel-type crystals containing Ni and Ga as main metal elements. A mixed powder of oxide and Al 2 O 3 is obtained.
【0028】次いで、前記混合粉末を担持体として、所
定量の貴金属を含有する水溶液を加えて蒸発乾固し、ヘ
リウム(He)気体中、400〜600℃の温度で3〜
5時間熱処理して本発明の酸化物触媒材料が得られる。Then, using the mixed powder as a carrier, an aqueous solution containing a predetermined amount of a noble metal is added and the mixture is evaporated to dryness, and the mixture is heated in a helium (He) gas at a temperature of 400 to 600 ° C. for 3 to 3 times.
After heat treatment for 5 hours, the oxide catalyst material of the present invention is obtained.
【0029】前記原料粉末としては、例えば、Ni及び
Gaの酸化物や、熱処理により酸化物を生成するそれら
の炭酸塩、硝酸塩、酢酸塩等を用いることができる。As the raw material powder, for example, oxides of Ni and Ga, and their carbonates, nitrates, acetates and the like which produce oxides by heat treatment can be used.
【0030】また、前記原料粉末は、定比のスピネル型
構造を示すNiGa2 O4 にGa金属を固溶することに
よりNOX の還元分解特性が向上すると考えられること
から、Niに対するGaの金属元素比が2.1以上にな
るように配合することが望ましい。Further, since it is considered that the raw material powder improves the reductive decomposition property of NO x by solid-dissolving Ga metal in NiGa 2 O 4 having a stoichiometric spinel structure, the metal of Ga with respect to Ni is It is desirable to mix them so that the element ratio is 2.1 or more.
【0031】更に、前記複合酸化物は、前記以外に酸化
物や他の金属塩による固相反応や、金属アルコキシド等
のゾル−ゲル法等により合成できるものであり、何等こ
れらの製造方法に限定されるものではない。Further, the above-mentioned composite oxide can be synthesized by a solid-phase reaction with oxides or other metal salts other than the above, or by a sol-gel method of metal alkoxide, etc., and is not limited to these production methods. It is not something that will be done.
【0032】前記混合粉末の熱処理は、その温度が50
0℃より低いと結晶化が不充分となり、逆に1600℃
を越えると緻密化してしまうため、500〜1600℃
の温度で、酸化雰囲気中、5〜30時間行うが、特に低
い温度で熱処理することが粉末の比表面積を高めるため
に有効であり、実用的には、比表面積が60m2 /g以
上となるように設定することが望ましい。The temperature of the heat treatment of the mixed powder is 50
If the temperature is lower than 0 ℃, the crystallization will be insufficient, and conversely 1600 ℃.
If it exceeds, it will be densified, so it is 500-1600 ℃
At a temperature of 5 to 30 hours in an oxidizing atmosphere, but heat treatment at a particularly low temperature is effective for increasing the specific surface area of the powder, and practically the specific surface area is 60 m 2 / g or more. It is desirable to set
【0033】次に、本発明を評価するに際し、出発原料
としてNi(NO3 )2 ・6H2 OとGa(NO3 )3
・9H2 Oの試薬を用い、NiとGaの金属元素比が
1:3となるように秤量し、これら試薬を蒸留水中に溶
解させ、撹拌しながらアンモニア水で中和し、この時、
生成した沈澱物の泥漿100重量部にAl2 O3 の粉末
を、50重量部添加し、超音波乳化分散機で十分に攪拌
混合した後、これを凍結乾燥させた。Next, in evaluating the present invention, Ni (NO 3 ) 2 .6H 2 O and Ga (NO 3 ) 3 were used as starting materials.
-Using a reagent of 9H 2 O, weighed so that the metal element ratio of Ni and Ga was 1: 3, dissolved these reagents in distilled water, and neutralized with ammonia water while stirring.
50 parts by weight of Al 2 O 3 powder was added to 100 parts by weight of the resulting precipitate, and the mixture was sufficiently stirred and mixed by an ultrasonic emulsification disperser, and then freeze-dried.
【0034】次に、該乾燥粉末を大気中、700℃の温
度で30時間、熱処理した後、該粉末に、表1に示す量
の各貴金属を含有する水溶液を添加し、蒸発乾固した
後、ヘリウム(He)気流中、500℃の温度で3時間
熱処理した。Next, the dry powder was heat-treated in the air at a temperature of 700 ° C. for 30 hours, and then an aqueous solution containing each noble metal in an amount shown in Table 1 was added to the powder and evaporated to dryness. In a helium (He) stream, heat treatment was performed at a temperature of 500 ° C. for 3 hours.
【0035】その後、前記貴金属を担持した粉末を金型
プレスにより成形後、CIP成形し、該成形体を解砕し
て篩別し、500μmを越え、700μm以下に整粒し
て評価用試料を調製した。After that, the powder carrying the noble metal is molded by a die press, CIP-molded, the molded body is crushed and sieved, and the particles are sized to exceed 500 μm and 700 μm or less to obtain a sample for evaluation. Prepared.
【0036】尚、前記担持体に貴金属を全く担持しない
もの、及び担持体をゼオライトとし、前記貴金属を担持
したものをそれぞれ比較例とした。Comparative examples were those in which no noble metal was supported on the carrier, and those in which the carrier was zeolite and the noble metal was supported.
【0037】[0037]
【表1】 [Table 1]
【0038】かくして得られた評価用試料の蛍光X線分
析により求めたNiに対するGaのカウント比は、1.
93であった。The count ratio of Ga to Ni determined by fluorescent X-ray analysis of the thus obtained evaluation sample was 1.
It was 93.
【0039】また、X線回折測定(XRD)により結晶
相を同定し、結晶相がスピネル結晶とγ−Al2 O3 相
から成ることを確認した。The crystal phase was identified by X-ray diffraction measurement (XRD), and it was confirmed that the crystal phase consisted of a spinel crystal and a γ-Al 2 O 3 phase.
【0040】次いで、NOが1000ppm、O2 が1
0%、H2 Oが10%、還元剤としてC2 H4 が100
0ppm、残部がHeから成る水蒸気を含有した反応ガ
スを、該反応ガスと触媒材料が接触する条件として、W
/Fを0.03g・sec/ccに設定し、前記評価用
試料を充填した触媒層に流し、250〜600℃の温度
範囲でNOの還元により生成したN2 をガスクロマトグ
ラフで測定し、N2 の生成量から各温度でのNO転換率
を求め、前記測定温度範囲内で350℃以下の低温域で
広範囲に一定以上のNO還元活性を示すものを良と評価
した。Next, NO of 1000 ppm and O 2 of 1
0%, H 2 O 10%, C 2 H 4 100 as reducing agent
A reaction gas containing water vapor of 0 ppm and the rest being He is used as a condition for contacting the reaction gas with the catalyst material.
/ F was set to 0.03 g · sec / cc, the sample for evaluation was flown through the catalyst layer, and N 2 produced by the reduction of NO in the temperature range of 250 to 600 ° C. was measured by a gas chromatograph. The NO conversion rate at each temperature was determined from the amount of production of 2 , and those having a NO reduction activity above a certain level in a low temperature range of 350 ° C. or lower within the measurement temperature range were evaluated as good.
【0041】更に、N2 O生成の有無を前記同様のガス
クロマトグラフで測定した。Further, the presence or absence of N 2 O production was measured by the same gas chromatograph as above.
【0042】[0042]
【表2】 [Table 2]
【0043】表2から明らかなように、比較例である貴
金属を担持しない試料番号1は、350℃以下の温度で
はNO還元活性を全く示さず、また、ゼオライト担持体
の試料番号34は、350℃以下の温度でNO還元活性
を示すものの、N2 Oの生成が確認されており、更に本
発明の請求範囲外である資料番号9、21、27は、3
50℃以下の温度ではNO還元活性が全体に低く、実用
的でない。As is clear from Table 2, the sample No. 1, which does not support the noble metal, which is a comparative example, shows no NO reduction activity at a temperature of 350 ° C. or lower, and the sample No. 34 of the zeolite carrier has a temperature of 350. Although it shows NO reduction activity at a temperature of ℃ or less, the production of N 2 O has been confirmed, and the material numbers 9, 21, and 27, which are outside the scope of the present invention, are 3
At a temperature of 50 ° C. or lower, NO reduction activity is low as a whole, which is not practical.
【0044】それに対して、本発明ではいずれも350
℃以下の温度を含め、広範囲の温度域で十分なNO還元
活性を示し、かつN2 Oも存在しないことが分かる。On the other hand, in the present invention, all 350
It can be seen that a sufficient NO reduction activity is exhibited in a wide temperature range including a temperature of 0 ° C. or lower, and N 2 O does not exist.
【0045】また、前記評価用試料を用い、4気筒のデ
ィーゼルエンジン台上試験装置の排気管にセットし、該
ディーゼルエンジンを最高回転数、全負荷の条件で10
0時間運転する耐久試験を実施し、試験後の評価用試料
について前記同様にしてNO還元活性を評価したが、3
50〜450℃の温度範囲でNO転換率が20%以上で
あり、N2 Oも検出されないことが確認でき、耐熱性及
び耐水性にも優れていることが証明された。Using the above-mentioned sample for evaluation, it was set in the exhaust pipe of a four-cylinder diesel engine bench test apparatus, and the diesel engine was operated under the conditions of maximum rotation speed and full load.
A durability test of running for 0 hours was carried out, and the NO reduction activity of the evaluation sample after the test was evaluated in the same manner as described above.
It was confirmed that the NO conversion rate was 20% or more in the temperature range of 50 to 450 ° C., N 2 O was not detected, and the heat resistance and water resistance were excellent.
【0046】[0046]
【発明の効果】以上、詳述したように本発明の窒素酸化
物除去用酸化物触媒材料並びに窒素酸化物除去方法によ
れば、該酸化物触媒材料はNiとGaを主たる金属元素
として含有するスピネル型構造の複合酸化物にAl2 O
3 を混合した担持体に、パラジウム(Pd)と、白金
(Pt)、ロジウム(Rh)、オスミウム(Os)の
内、少なくとも一種を前記担持体100重量部に対して
合計0.05〜0.4重量部担持したものであり、高濃
度の酸素と還元性を有する炭素含有ガスが存在する酸化
雰囲気中で、前記酸化物触媒材料と窒素酸化物を含む排
気ガスを接触させることから、水蒸気が存在する雰囲気
中は勿論、排気ガス中の酸素濃度が3%以上の高酸素濃
度雰囲気下であっても、その上、ガスの流速が高速度で
あっても、350℃以下の低温域で広範囲に優れたNO
X 還元性能を有し、N2 Oが全く発生しないことから、
排気ガス中に含まれるNOX を有効に還元除去すること
ができ、省エネルギー、省資源及び地球温暖化防止を目
標として開発される今後のディーゼルエンジンやリーン
バーンエンジン等の各種内燃機関の排気ガスをはじめ、
NOX を含有する各種有害物質の浄化に極めて有用なも
のである。As described above in detail, according to the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention, the oxide catalyst material contains Ni and Ga as main metal elements. Al 2 O for spinel type complex oxide
3 to carrier obtained by mixing total, and palladium (Pd), platinum (Pt), of the rhodium (Rh), osmium (Os), at least one with respect to the carrier 100 parts by weight from 0.05 to 0. 4 parts by weight are carried, and since the oxide catalyst material and the exhaust gas containing nitrogen oxide are brought into contact with each other in an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present, steam is generated. Not only in the existing atmosphere but also in a high oxygen concentration atmosphere in which the oxygen concentration in the exhaust gas is 3% or more, and in addition, even if the gas flow rate is high, a wide range in a low temperature range of 350 ° C or less Excellent NO
It has X reduction performance and does not generate N 2 O at all,
Exhaust gas from various internal combustion engines such as diesel engine and lean burn engine, which can be effectively reduced and removed of NO X contained in exhaust gas and is developed with the goal of energy saving, resource saving and prevention of global warming. Begin,
It is extremely useful for purifying various harmful substances containing NO x .
Claims (6)
たる金属元素として含有するスピネル型構造の複合酸化
物とアルミナ(Al2 O3 )とを混合した担持体に、パ
ラジウム(Pd)と、白金(Pt)、ロジウム(R
h)、オスミウム(Os)の内、少なくとも一種を前記
担持体100重量部に対して合計0.05〜0.4重量
部担持したことを特徴とする窒素酸化物除去用酸化物触
媒材料。1. A support in which a composite oxide having a spinel structure containing nickel (Ni) and gallium (Ga) as main metal elements and alumina (Al 2 O 3 ) are mixed, and palladium (Pd) is added to the support. Platinum (Pt), Rhodium (R
h), and at least one of osmium (Os) is supported in a total amount of 0.05 to 0.4 parts by weight with respect to 100 parts by weight of the support, and an oxide catalyst material for removing nitrogen oxides.
t)、ロジウム(Rh)、オスミウム(Os)の内、少
なくとも一種を前記担持体100重量部に対して合計
0.07〜0.3重量部担持したことを特徴とする請求
項1記載の窒素酸化物除去用酸化物触媒材料。2. Palladium (Pd) and platinum (Pd)
At least one of t), rhodium (Rh), and osmium (Os) is supported in a total amount of 0.07 to 0.3 parts by weight with respect to 100 parts by weight of the support, and nitrogen is contained. Oxide catalyst material for oxide removal.
主成分と白金(Pt)、ロジウム(Rh)、オスミウム
(Os)の内、少なくとも一種を前記担持体100重量
部に対して合計0.07〜0.2重量部担持したことを
特徴とする請求項1及び請求項2記載の窒素酸化物除去
用酸化物触媒材料。3. Palladium (Pd) as a main component, and at least one of the main component and platinum (Pt), rhodium (Rh), and osmium (Os) is added in a total amount of 0 based on 100 parts by weight of the carrier. 0.07 to 0.2 part by weight is supported, and the oxide catalyst material for removing nitrogen oxides according to claim 1 or 2,
スが存在する酸化雰囲気中で、ニッケル(Ni)とガリ
ウム(Ga)を主たる金属元素として含有するスピネル
型構造の複合酸化物とアルミナ(Al2 O3 )を混合し
た担持体に、パラジウム(Pd)と、白金(Pt)、ロ
ジウム(Rh)、オスミウム(Os)の内、少なくとも
一種を前記担持体100重量部に対して合計0.05〜
0.4重量部担持して成る酸化物触媒材料を、窒素酸化
物を含む排気ガスに接触させることを特徴とする窒素酸
化物除去方法。4. A composite oxide having a spinel structure and nickel containing nickel (Ni) and gallium (Ga) as main metal elements in an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present. (Al 2 O 3 ) is mixed in the carrier, and at least one of palladium (Pd), platinum (Pt), rhodium (Rh), and osmium (Os) is added to the carrier in a total amount of 0. .05
A method for removing nitrogen oxides, characterized in that 0.4 parts by weight of an oxide catalyst material is brought into contact with exhaust gas containing nitrogen oxides.
t)、ロジウム(Rh)、オスミウム(Os)の内、少
なくとも一種を担持体100重量部に対して合計0.0
7〜0.3重量部担持して成る酸化物触媒材料を、窒素
酸化物を含む排気ガスに接触させることを特徴とする請
求項4記載の窒素酸化物除去方法。5. Palladium (Pd) and platinum (Pd)
t), rhodium (Rh), and osmium (Os), at least one of which is 0.0 in total with respect to 100 parts by weight of the carrier.
5. The method for removing nitrogen oxides according to claim 4, wherein the oxide catalyst material supported by 7 to 0.3 parts by weight is brought into contact with exhaust gas containing nitrogen oxides.
主成分と白金(Pt)、ロジウム(Rh)、オスミウム
(Os)の内、少なくとも一種を前記担持体100重量
部に対して合計0.07〜0.2重量部担持して成る酸
化物触媒材料を、窒素酸化物を含む排気ガスに接触させ
ることを特徴とする請求項4及び請求項5記載の窒素酸
化物除去方法。6. Palladium (Pd) as a main component, and at least one of the main component and platinum (Pt), rhodium (Rh), and osmium (Os) is added to 100 parts by weight of the support in total. The method for removing nitrogen oxides according to claim 4 or 5, wherein the oxide catalyst material supported by 0.07 to 0.2 parts by weight is brought into contact with exhaust gas containing nitrogen oxides.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP7037314A JPH08229401A (en) | 1995-02-24 | 1995-02-24 | Oxide catalyst material for removing nitrogen oxide and removal of nitrogen oxide |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP7037314A JPH08229401A (en) | 1995-02-24 | 1995-02-24 | Oxide catalyst material for removing nitrogen oxide and removal of nitrogen oxide |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH08229401A true JPH08229401A (en) | 1996-09-10 |
Family
ID=12494229
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP7037314A Pending JPH08229401A (en) | 1995-02-24 | 1995-02-24 | Oxide catalyst material for removing nitrogen oxide and removal of nitrogen oxide |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH08229401A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2000059600A1 (en) * | 1999-03-30 | 2000-10-12 | The University Of Queensland | Catalyst systems for reduction of oxides of nitrogen |
JP2016523693A (en) * | 2013-05-17 | 2016-08-12 | ジョンソン、マッセイ、パブリック、リミテッド、カンパニーJohnson Matthey Public Limited Company | Oxidation catalyst for compression ignition engines |
CN112871166A (en) * | 2021-01-21 | 2021-06-01 | 中国科学院宁波城市环境观测研究站 | Supported catalyst and preparation method and application thereof |
-
1995
- 1995-02-24 JP JP7037314A patent/JPH08229401A/en active Pending
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2000059600A1 (en) * | 1999-03-30 | 2000-10-12 | The University Of Queensland | Catalyst systems for reduction of oxides of nitrogen |
JP2016523693A (en) * | 2013-05-17 | 2016-08-12 | ジョンソン、マッセイ、パブリック、リミテッド、カンパニーJohnson Matthey Public Limited Company | Oxidation catalyst for compression ignition engines |
JP2019025480A (en) * | 2013-05-17 | 2019-02-21 | ジョンソン、マッセイ、パブリック、リミテッド、カンパニーJohnson Matthey Public Limited Company | Oxidation catalyst for compression ignition engine |
CN112871166A (en) * | 2021-01-21 | 2021-06-01 | 中国科学院宁波城市环境观测研究站 | Supported catalyst and preparation method and application thereof |
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