JP3309024B2 - Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides - Google Patents
Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxidesInfo
- Publication number
- JP3309024B2 JP3309024B2 JP29425594A JP29425594A JP3309024B2 JP 3309024 B2 JP3309024 B2 JP 3309024B2 JP 29425594 A JP29425594 A JP 29425594A JP 29425594 A JP29425594 A JP 29425594A JP 3309024 B2 JP3309024 B2 JP 3309024B2
- Authority
- JP
- Japan
- Prior art keywords
- nitrogen oxides
- removing nitrogen
- catalyst material
- exhaust gas
- oxide
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 title claims description 60
- 239000003054 catalyst Substances 0.000 title claims description 29
- 239000000463 material Substances 0.000 title claims description 22
- 238000000034 method Methods 0.000 title claims description 16
- 239000007789 gas Substances 0.000 claims description 25
- 229910052751 metal Inorganic materials 0.000 claims description 15
- 229910018072 Al 2 O 3 Inorganic materials 0.000 claims description 14
- 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
- 229910052733 gallium Inorganic materials 0.000 claims description 13
- 239000001301 oxygen Substances 0.000 claims description 13
- 239000002131 composite material Substances 0.000 claims description 12
- 229910052759 nickel Inorganic materials 0.000 claims description 11
- 239000002184 metal Substances 0.000 claims description 9
- 229910052596 spinel Inorganic materials 0.000 claims description 9
- 239000011029 spinel Substances 0.000 claims description 9
- 230000001603 reducing effect Effects 0.000 claims description 7
- 229910052799 carbon Inorganic materials 0.000 claims description 6
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 3
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims description 3
- 238000002156 mixing Methods 0.000 claims description 3
- 230000001590 oxidative effect Effects 0.000 claims description 3
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims 5
- GYHNNYVSQQEPJS-UHFFFAOYSA-N Gallium Chemical compound [Ga] GYHNNYVSQQEPJS-UHFFFAOYSA-N 0.000 claims 2
- 239000000843 powder Substances 0.000 description 12
- 239000013078 crystal Substances 0.000 description 9
- 239000012071 phase Substances 0.000 description 8
- 238000002485 combustion reaction Methods 0.000 description 7
- 238000010438 heat treatment Methods 0.000 description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 7
- 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
- 238000000746 purification Methods 0.000 description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 4
- 238000011156 evaluation Methods 0.000 description 4
- 238000006722 reduction reaction Methods 0.000 description 4
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 description 3
- 230000010757 Reduction Activity Effects 0.000 description 3
- 238000002441 X-ray diffraction Methods 0.000 description 3
- 230000003197 catalytic effect Effects 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 229930195733 hydrocarbon Natural products 0.000 description 3
- 150000002430 hydrocarbons Chemical class 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 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
- 229910021536 Zeolite Inorganic materials 0.000 description 2
- 229910021529 ammonia Inorganic materials 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 239000003638 chemical reducing agent Substances 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 238000002425 crystallisation Methods 0.000 description 2
- 230000008025 crystallization Effects 0.000 description 2
- 238000000354 decomposition 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
- 239000000446 fuel Substances 0.000 description 2
- 230000002209 hydrophobic effect Effects 0.000 description 2
- 229910000510 noble metal Inorganic materials 0.000 description 2
- 239000012495 reaction gas Substances 0.000 description 2
- 239000010948 rhodium Substances 0.000 description 2
- 238000012360 testing method Methods 0.000 description 2
- 239000010457 zeolite Substances 0.000 description 2
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 1
- -1 C 3 H 6 and C 3 H 8 Chemical class 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
- 238000003915 air pollution Methods 0.000 description 1
- 150000004703 alkoxides Chemical class 0.000 description 1
- 235000011114 ammonium hydroxide Nutrition 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 238000010531 catalytic reduction reaction Methods 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 230000008094 contradictory effect Effects 0.000 description 1
- 229910052878 cordierite Inorganic materials 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
- 238000007599 discharging Methods 0.000 description 1
- 239000012153 distilled water Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000001804 emulsifying effect Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000004817 gas chromatography Methods 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 239000011812 mixed powder Substances 0.000 description 1
- 150000002823 nitrates Chemical class 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 229910052763 palladium Inorganic materials 0.000 description 1
- 229910052697 platinum Inorganic materials 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
- 238000012827 research and development Methods 0.000 description 1
- 229910052703 rhodium Inorganic materials 0.000 description 1
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 238000003980 solgel method Methods 0.000 description 1
- 238000003746 solid phase reaction Methods 0.000 description 1
- 239000006104 solid solution Substances 0.000 description 1
- 239000007858 starting material Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 238000004876 x-ray fluorescence Methods 0.000 description 1
Landscapes
- Catalysts (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
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.
【0002】[0002]
【従来技術】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。BACKGROUND ART In recent years, contamination of the atmosphere by various pollutants is a major social problem, NO X in the exhaust gas of an automobile that is the moving source of air pollution among them, decompose harmful substances such as CO X, removed There is an urgent need to develop ways to do that.
【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。[0003] Conventionally, NO x and C in exhaust gas of automobiles have been developed.
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、パラジウム(Pd)、白金(Pt)、ロジウム
(Rh)等の貴金属を、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担持したものが用
いられていた。Examples of the three-way catalyst used in such a method include cordierite in which a noble metal such as palladium (Pd), platinum (Pt), and rhodium (Rh) is coated with γ-alumina (Al 2 O 3 ). Supported on a refractory.
【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、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。[0005] However, the three-way catalyst can efficiently purify the exhaust gas only at a low oxygen concentration of about 0.5%, and the oxygen concentration of the exhaust gas is 1%.
However, there is a drawback that it does not work effectively in a high concentration region exceeding the above range.
【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。[0006] Therefore, usually the oxygen concentration in the exhaust gas is measured and controlled to a air-fuel ratio of CO and C X H X, close range to the theoretical equivalent value which may be treated with NO X at a high purification rate 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。[0007] Furthermore, since energy savings and resource savings have been called for in recent years, research and development of a lean burn system for gasoline engines has been carried out in order to achieve low fuel consumption. Has a disadvantage that the exhaust gas cannot be purified due to oxygen poisoning of the noble metal of the catalyst.
【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。[0008] Also, in the present combustion system, exhaust gas is not purified at all because of the high oxygen concentration in the exhaust gas in the current combustion system.
【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 is generated at a high temperature of about 1000 ° C. or more,
As a method for purifying NO X concentration thereof becomes higher as the combustion temperature becomes higher effectively, the there is a selective catalytic reduction method using ammonia in addition, the oxygen concentration in the stationary combustion apparatus such as factories although there are effective for purification of the NO X in the high exhaust gas, applying this method to a mobile combustion device such as an automobile has a problem in terms of 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 I have.
【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、ディーゼルエンジンのように排気ガス中に水
分を含むような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く、その用途が限定されるという
課題があり、耐熱性だけではなく耐水性にも優れた触媒
材料が望まれていた。However, those using a metal-supported hydrophobic zeolite as a catalyst have poor water resistance, and when exhaust gas contains moisture as in a diesel engine, the presence of water vapor does not exist. Therefore, there is a problem that the purification rate of NO X is greatly reduced with time, and the use thereof is limited. Therefore, a catalyst material excellent not only in heat resistance but also in water resistance 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
素濃度の高い排気ガスを、該排気ガスの流速が高速度で
あっても、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 or the like, and is effective in discharging exhaust gas having a high oxygen concentration containing water, such as a diesel engine, even if the flow rate of the exhaust gas is high. there is provided a nitrogen oxide removal method using a catalyst useful materials and it can be purified NO X in the exhaust gas.
【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、Niおよび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、Al2 O3 を混合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。SUMMARY OF THE INVENTION The present invention has been made in view of the above-mentioned problems, and it is an object of the present invention to provide a composite oxide containing Ni and Ga as main metal elements having a spinel-type crystal phase containing Al 2 O 3 . It has been found that the mixed oxide catalyst material has excellent catalytic activity over a long period even at a high oxygen concentration in the presence of water vapor.
【0014】即ち、本発明の窒素酸化物除去用酸化物触
媒材料は、Niおよび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 粉末を混合して成る触媒材料である。That is, the oxide catalyst material for removing nitrogen oxides of the present invention contains a composite oxide powder containing Ni and Ga as main metal elements and having a crystal phase having a spinel structure, and an Al 2 O 3 powder. Is a catalyst material obtained by mixing
【0015】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、Ni及び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、A
l2 O3 を混合した触媒材料と、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 according to the present invention is characterized in that the crystal phase containing Ni and Ga as main metal elements is spinel type in an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present. In the composite oxide having the structure, A
It is characterized in that a catalyst material mixed with l 2 O 3 is brought into contact with an exhaust gas containing nitrogen oxides.
【0016】本発明において、前記複合酸化物は、Ni
及び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以上がより望まし
く、とりわけ1.5以上であれば最も好ましい。In the present invention, the composite oxide is Ni
And Ga as a main metal element, and has a crystal phase of a spinel structure represented by NiGa 2 O 4 as a general formula, and the correlation between Ni and Ga of the composite oxide is as follows:
When discussing the count ratio of Ga to Ni by fluorescent X-ray analysis, 1.4 or more is more desirable from the viewpoint of catalytic activity, and especially 1.5 or more is most desirable.
【0017】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。It is considered that Al 2 O 3 having a high specific surface area is suitable, and practically 60 m 2
/ G or more, and the change in the catalytic activity due to the mixed amount of Al 2 O 3 is small, but the mixed amount is 20-70.
% By weight is preferred, and most preferably 25 to 60% by weight.
【0018】更に、前記複合酸化物にAl2 O3 を混合
した触媒材料と、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 、
C3H6 、C3 H8 等の炭化水素、CH3 OH、C2 H
5 OH等のアルコール、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。Furthermore, when a catalyst material in which Al 2 O 3 is mixed with the composite oxide and an exhaust gas containing nitrogen oxides are brought into contact, C 2 H 4 ,
Hydrocarbons such as C 3 H 6 and C 3 H 8 , CH 3 OH, C 2 H
When an alcohol such as 5 OH or a carbon gas having a reducing property such as CO is contained and brought into contact with the catalyst material, NO
X- reduction is further improved.
【0019】[0019]
【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
したものであることから、触媒材料中のAl2 O3 がN
Oを酸化してNO2 の生成を促進し、NOよりNO2 に
対する還元活性の方が高いNi−Ga系酸化物触媒によ
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 comprises N
i and Ga contained as the main metal element, a complex oxide crystal phase having a spinel structure, since it is a mixture of Al 2 O 3, Al 2 O 3 in the catalyst material is N
O is oxidized to promote the formation of NO 2, the high Ni-Ga-based oxide catalyst towards reducing activity against NO 2 from NO, exhibit high properties in reducing decomposition of the NO X.
【0020】[0020]
【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 The oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides according to the present invention will be described in detail below with reference to examples.
【0021】本発明の窒素酸化物除去用酸化物触媒材料
の製造方法は、先ず、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A
l2 O3 から成る混合粉末が得られる。In the method for producing an oxide catalyst material for removing nitrogen oxides according to the present invention, first, a predetermined amount of a raw material powder containing Ni and Ga is weighed, sufficiently stirred and mixed, and then an Al 2 O 3 powder is added. Then, by performing a heat treatment at a temperature of 500 to 1600 ° C. for 5 to 30 hours in an oxidizing atmosphere, a composite oxide of a spinel crystal containing Ni and Ga as main metal elements and A
A mixed powder consisting of l 2 O 3 is obtained.
【0022】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, etc., which form oxides by heat treatment, can be used.
【0023】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, the raw material powder, it is considered a reductive decomposition characteristic of the NO X is improved by solid solution of Ga metal NiGa 2 O 4 showing the spinel structure of stoichiometric, of Ga to Ni metal It is desirable to mix such that the element ratio becomes 2.1 or more.
【0024】また前記複合酸化物は、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。The composite oxide can be synthesized by a solid phase reaction with an oxide or another metal salt, a sol-gel method such as a metal alkoxide, or the like. Not something.
【0025】前記製造方法において、いずれも熱処理
は、熱処理温度が500℃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。[0025] In any of the above-mentioned manufacturing methods, in any of the heat treatments, if the heat treatment temperature is lower than 500 ° C, the crystallization becomes insufficient. If the heat treatment temperature exceeds 1600 ° C, the crystallization becomes insufficient. In the atmosphere, 5
Although the heat treatment is performed for 30 hours, heat treatment at a particularly low temperature is effective for increasing the specific surface area of the powder, and practically, it is desirable to set the specific surface area to be 60 m 2 / g or more.
【0026】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、25〜75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, when evaluating the present invention, Ni (NO 3 ) 2 .6H 2 O and Ga (NO 3 ) 3 were used as starting materials.
Using a 9H 2 O reagent, weigh so that the metal element ratio of Ni and Ga is 1: 3, dissolve these reagents in distilled water, and neutralize with ammonia water while stirring.
25 to 75 parts by weight of Al 2 O 3 powder was added to 100 parts by weight of the formed slurry, and the mixture was sufficiently stirred and mixed with an ultrasonic emulsifying and dispersing machine, and then freeze-dried.
【0027】次に、該乾燥粉末を大気中、700℃の温
度で30時間、熱処理して酸化物触媒粉末を調製し、該
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。Next, the dried powder is heat-treated in the atmosphere at a temperature of 700 ° C. for 30 hours to prepare an oxide catalyst powder. The powder is molded by a die press, and then CIP-molded. The sample was crushed, sieved, and sized to exceed 500 μm and 700 μm or less to prepare a sample for evaluation.
【0028】尚、Al2 O3 を混合しないものを前記同
様に調製して比較例とした。A sample without Al 2 O 3 was prepared in the same manner as described above and used as a comparative example.
【0029】かくして得られた評価用材料の粉末を用い
て蛍光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 X-ray fluorescence analysis using the thus obtained powder of the evaluation material was 1.93.
【0030】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
からなることを確認した。The crystal phase was identified by X-ray diffraction measurement (XRD), and it was confirmed that the crystal phase was composed of a spinel crystal and a γ-Al 2 O 3 phase.
【0031】次いで、NOが1000ppm、O2 が5
%又は10%、H2 Oが10%、還元剤としてC2 H4
が1000ppm又はC3 H6 が666ppm、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、前記評価用材料を充填した触
媒層に流し、300〜600℃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、N
2 の生成量から最高活性を示す450℃のNO転換率を
NO還元活性として評価した。[0031] Then, NO is 1000ppm, O 2 5
% Or 10%, H 2 O is 10%, and C 2 H 4 is used as a reducing agent.
The reaction gas containing 1000 ppm or 666 ppm of C 3 H 6 , and the balance consisting of He, was mixed with 0.03 g of W / F as a condition for contacting the reaction gas with the catalyst material.
Set to sec / cc, flow through the catalyst layer filled with the evaluation material, measure N 2 generated by reduction of NO in a temperature range of 300 to 600 ° C. by gas chromatography,
The NO conversion rate at 450 ° C., which shows the highest activity based on the production amount of 2 , was evaluated as NO reduction activity.
【0032】[0032]
【表1】 [Table 1]
【0033】表1から明らかなように、Al2 O3 を混
合しない比較例である試料番号1、5、11及び15
は、いずれも450℃におけるNO還元活性が33%以
下であるのに対して、本発明では450℃におけるNO
還元活性が35%以上を示していることが分かる。As is apparent from Table 1, Sample Nos. 1, 5, 11 and 15 which are comparative examples in which Al 2 O 3 was not mixed were used.
Indicate that the NO reduction activity at 450 ° C. is 33% or less,
It can be seen that the reducing activity shows 35% or more.
【0034】また、前記評価用の複合酸化物を使用し、
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100時間運転する耐久試験を実施し、試験後の
複合酸化物について前記同様にしてNO還元活性を評価
したが、NO転換率はほとんど低下していないことが確
認でき、耐水性に優れていることも証明された。Further, using the composite oxide for evaluation described above,
A 4-cylinder diesel engine bench test device was set in the exhaust pipe, and a durability test was performed in which the diesel engine was operated for 100 hours under the conditions of the maximum rotation speed and full load. When the NO reduction activity was evaluated, it was confirmed that the NO conversion rate was hardly reduced, and it was also proved that the NO conversion rate was excellent.
【0035】[0035]
【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
O3 を混合したものであることから、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、優れたNOX 還元性能を有することか
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, 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 is added to the spinel-type composite oxide.
Since it is a mixture of O 3 , even in a high oxygen concentration atmosphere where the oxygen concentration in the exhaust gas is 3% or more as well as in an atmosphere where water vapor is present, the gas flow rate is high. even superior because it has a NO X reduction performance was, it is possible to effectively reduce and remove NO X contained in the exhaust gas, energy saving, future diesel engines and lean to resource saving is developed as the target including exhaust gas for various internal combustion engine such as burn engine, it is extremely useful for the purification of various harmful substances containing NO X.
Claims (2)
(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、アルミナ(Al2 O3 )を混合した
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 nitrogen oxide removal method comprising mixing alumina (Al 2 O 3 ) with a composite oxide having a spinel structure containing at least nickel (Ni) and gallium (Ga) as main metal elements. For oxide catalyst materials.
スが存在する酸化雰囲気中で、少なくともニッケル(N
i)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に、アルミナ(Al2 O
3 )を混合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窒素酸化物除
去方法。2. In an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present, at least nickel (N)
i) and alumina (Al 2 O) as a composite oxide having a spinel structure containing gallium (Ga) as a main metal element
3. A method for removing nitrogen oxides, comprising contacting an oxide catalyst material obtained by mixing 3 ) with an exhaust gas containing nitrogen oxides.
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JP3309024B2 true JP3309024B2 (en) | 2002-07-29 |
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