JPH04219144A - Exhaust gas purification catalyst - Google Patents
Exhaust gas purification catalystInfo
- Publication number
- JPH04219144A JPH04219144A JP2411255A JP41125590A JPH04219144A JP H04219144 A JPH04219144 A JP H04219144A JP 2411255 A JP2411255 A JP 2411255A JP 41125590 A JP41125590 A JP 41125590A JP H04219144 A JPH04219144 A JP H04219144A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- catalyst
- zeolite
- alkaline earth
- cobalt
- 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 59
- 238000000746 purification Methods 0.000 title claims abstract description 16
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 claims abstract description 66
- 239000007789 gas Substances 0.000 claims abstract description 42
- 239000010457 zeolite Substances 0.000 claims abstract description 34
- 229910021536 Zeolite Inorganic materials 0.000 claims abstract description 31
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims abstract description 31
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 24
- 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 21
- 229910052802 copper Inorganic materials 0.000 claims abstract description 21
- 229910052703 rhodium Inorganic materials 0.000 claims abstract description 21
- 229910052784 alkaline earth metal Inorganic materials 0.000 claims abstract description 18
- 150000001342 alkaline earth metals Chemical class 0.000 claims abstract description 18
- 229910052593 corundum Inorganic materials 0.000 claims abstract description 18
- 229910001845 yogo sapphire Inorganic materials 0.000 claims abstract description 18
- 229930195733 hydrocarbon Natural products 0.000 claims abstract description 16
- 150000002430 hydrocarbons Chemical class 0.000 claims abstract description 16
- 239000000377 silicon dioxide Substances 0.000 claims abstract description 12
- 229910052681 coesite Inorganic materials 0.000 claims abstract description 11
- 229910052906 cristobalite Inorganic materials 0.000 claims abstract description 11
- 235000012239 silicon dioxide Nutrition 0.000 claims abstract description 11
- 229910052682 stishovite Inorganic materials 0.000 claims abstract description 11
- 229910052905 tridymite Inorganic materials 0.000 claims abstract description 11
- 229910017052 cobalt Inorganic materials 0.000 claims description 28
- 239000010941 cobalt Substances 0.000 claims description 28
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 claims description 28
- 239000010948 rhodium Substances 0.000 claims description 20
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 19
- 239000010949 copper Substances 0.000 claims description 19
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 claims description 17
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 14
- 229910002091 carbon monoxide Inorganic materials 0.000 claims description 14
- 238000002485 combustion reaction Methods 0.000 abstract description 8
- 229910052791 calcium Inorganic materials 0.000 abstract description 2
- 239000004215 Carbon black (E152) Substances 0.000 abstract 2
- 230000000052 comparative effect Effects 0.000 description 13
- 239000007864 aqueous solution Substances 0.000 description 12
- 239000007788 liquid Substances 0.000 description 10
- 238000000034 method Methods 0.000 description 10
- 239000000203 mixture Substances 0.000 description 10
- 238000000926 separation method Methods 0.000 description 10
- 229910052788 barium Inorganic materials 0.000 description 9
- DSAJWYNOEDNPEQ-UHFFFAOYSA-N barium atom Chemical compound [Ba] DSAJWYNOEDNPEQ-UHFFFAOYSA-N 0.000 description 8
- 239000000126 substance Substances 0.000 description 8
- 229910052712 strontium Inorganic materials 0.000 description 7
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 6
- 239000001301 oxygen Substances 0.000 description 6
- 229910052760 oxygen Inorganic materials 0.000 description 6
- 238000002360 preparation method Methods 0.000 description 6
- CIOAGBVUUVVLOB-UHFFFAOYSA-N strontium atom Chemical compound [Sr] CIOAGBVUUVVLOB-UHFFFAOYSA-N 0.000 description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 5
- 238000001035 drying Methods 0.000 description 4
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 3
- 239000011230 binding agent Substances 0.000 description 3
- 230000003197 catalytic effect Effects 0.000 description 3
- 239000003638 chemical reducing agent Substances 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 239000001257 hydrogen Substances 0.000 description 3
- 229910052739 hydrogen Inorganic materials 0.000 description 3
- 238000005342 ion exchange Methods 0.000 description 3
- 238000000465 moulding Methods 0.000 description 3
- 150000003839 salts Chemical class 0.000 description 3
- 239000002002 slurry Substances 0.000 description 3
- 238000003756 stirring Methods 0.000 description 3
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonia chloride Chemical compound [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 2
- 229910021529 ammonia Inorganic materials 0.000 description 2
- WDIHJSXYQDMJHN-UHFFFAOYSA-L barium chloride Chemical compound [Cl-].[Cl-].[Ba+2] WDIHJSXYQDMJHN-UHFFFAOYSA-L 0.000 description 2
- 229910001626 barium chloride Inorganic materials 0.000 description 2
- 239000002734 clay mineral Substances 0.000 description 2
- UFMZWBIQTDUYBN-UHFFFAOYSA-N cobalt dinitrate Chemical compound [Co+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O UFMZWBIQTDUYBN-UHFFFAOYSA-N 0.000 description 2
- ZBYYWKJVSFHYJL-UHFFFAOYSA-L cobalt(2+);diacetate;tetrahydrate Chemical compound O.O.O.O.[Co+2].CC([O-])=O.CC([O-])=O ZBYYWKJVSFHYJL-UHFFFAOYSA-L 0.000 description 2
- XTVVROIMIGLXTD-UHFFFAOYSA-N copper(II) nitrate Chemical compound [Cu+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O XTVVROIMIGLXTD-UHFFFAOYSA-N 0.000 description 2
- OPQARKPSCNTWTJ-UHFFFAOYSA-L copper(ii) acetate Chemical compound [Cu+2].CC([O-])=O.CC([O-])=O OPQARKPSCNTWTJ-UHFFFAOYSA-L 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- -1 rhodium ions Chemical class 0.000 description 2
- VXNYVYJABGOSBX-UHFFFAOYSA-N rhodium(3+);trinitrate Chemical group [Rh+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O VXNYVYJABGOSBX-UHFFFAOYSA-N 0.000 description 2
- 239000005995 Aluminium silicate Substances 0.000 description 1
- 239000004113 Sepiolite Substances 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 150000001242 acetic acid derivatives Chemical class 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 229910001420 alkaline earth metal ion Inorganic materials 0.000 description 1
- 229910001583 allophane Inorganic materials 0.000 description 1
- 235000012211 aluminium silicate Nutrition 0.000 description 1
- 235000019270 ammonium chloride Nutrition 0.000 description 1
- 150000003863 ammonium salts Chemical class 0.000 description 1
- 229960000892 attapulgite Drugs 0.000 description 1
- 239000002585 base Substances 0.000 description 1
- 239000000440 bentonite Substances 0.000 description 1
- 229910000278 bentonite Inorganic materials 0.000 description 1
- SVPXDRXYRYOSEX-UHFFFAOYSA-N bentoquatam Chemical compound O.O=[Si]=O.O=[Al]O[Al]=O SVPXDRXYRYOSEX-UHFFFAOYSA-N 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 229910052878 cordierite Inorganic materials 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- GUJOJGAPFQRJSV-UHFFFAOYSA-N dialuminum;dioxosilane;oxygen(2-);hydrate Chemical compound O.[O-2].[O-2].[O-2].[Al+3].[Al+3].O=[Si]=O.O=[Si]=O.O=[Si]=O.O=[Si]=O GUJOJGAPFQRJSV-UHFFFAOYSA-N 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
- 238000011156 evaluation Methods 0.000 description 1
- 229910001657 ferrierite group Inorganic materials 0.000 description 1
- 150000003840 hydrochlorides Chemical class 0.000 description 1
- 150000002431 hydrogen Chemical class 0.000 description 1
- 238000005470 impregnation Methods 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- NLYAJNPCOHFWQQ-UHFFFAOYSA-N kaolin Chemical compound O.O.O=[Al]O[Si](=O)O[Si](=O)O[Al]=O NLYAJNPCOHFWQQ-UHFFFAOYSA-N 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 239000011707 mineral Chemical class 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 229910052901 montmorillonite Inorganic materials 0.000 description 1
- 229930014626 natural product Natural products 0.000 description 1
- 150000002823 nitrates Chemical class 0.000 description 1
- 150000003891 oxalate salts Chemical class 0.000 description 1
- 229910052763 palladium Inorganic materials 0.000 description 1
- 229910052625 palygorskite Inorganic materials 0.000 description 1
- 229910052697 platinum Inorganic materials 0.000 description 1
- 239000012495 reaction gas Substances 0.000 description 1
- 229910052624 sepiolite Inorganic materials 0.000 description 1
- 235000019355 sepiolite Nutrition 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 229910001631 strontium chloride Inorganic materials 0.000 description 1
- AHBGXTDRMVNFER-UHFFFAOYSA-L strontium dichloride Chemical compound [Cl-].[Cl-].[Sr+2] AHBGXTDRMVNFER-UHFFFAOYSA-L 0.000 description 1
- 150000004685 tetrahydrates Chemical class 0.000 description 1
- 229910052723 transition metal Inorganic materials 0.000 description 1
- 150000003624 transition metals Chemical class 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Landscapes
- Catalysts (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Abstract
Description
【0001】0001
【産業上の利用分野】本発明は、自動車エンジン等の内
燃機関から排出される排ガス中の窒素酸化物、一酸化炭
素及び炭化水素を除去する排ガス浄化用触媒に関し、特
に、酸素過剰の排ガスの窒素酸化物を浄化する触媒及び
その使用方法に関するものである。[Field of Industrial Application] The present invention relates to an exhaust gas purifying catalyst for removing nitrogen oxides, carbon monoxide, and hydrocarbons from exhaust gas emitted from internal combustion engines such as automobile engines, and in particular, to The present invention relates to a catalyst for purifying nitrogen oxides and a method for using the same.
【0002】0002
【従来の技術】内燃機関から排出される排ガス中の有害
物質である窒素酸化物、一酸化炭素及び炭化水素は、例
えばPt,Rh,Pd等を担体上に担持させた三元触媒
により除去されている。しかしながら、ディーゼルエン
ジン排ガスについては、排ガス中に酸素が多く含まれて
いるために、窒素酸化物を除去するのに有効な触媒がな
く、触媒による排ガス浄化は行われていない。[Prior Art] The harmful substances nitrogen oxides, carbon monoxide, and hydrocarbons in the exhaust gas emitted from internal combustion engines are removed by a three-way catalyst in which, for example, Pt, Rh, Pd, etc. are supported on a carrier. ing. However, since diesel engine exhaust gas contains a large amount of oxygen, there is no effective catalyst for removing nitrogen oxides, and exhaust gas purification by catalysts has not been carried out.
【0003】また、近年のガソリンエンジンにおいては
、低燃費化及び排出炭酸ガスの低減の目的で希薄燃焼さ
せることが必要となってきている。しかし、希薄燃焼ガ
ソリンエンジンの排ガスは酸素過剰雰囲気であるため、
上記のような従来の三元触媒は使用できず、有害成分特
に窒素酸化物を除去する方法は実用化されていない。[0003] Furthermore, in recent years, it has become necessary for gasoline engines to perform lean combustion for the purpose of improving fuel efficiency and reducing carbon dioxide emissions. However, since the exhaust gas of a lean-burn gasoline engine is an oxygen-rich atmosphere,
Conventional three-way catalysts such as those described above cannot be used, and methods for removing harmful components, particularly nitrogen oxides, have not been put to practical use.
【0004】このような酸素過剰の排ガス中の特に窒素
酸化物を除去する方法として、アンモニア等の還元剤を
添加する方法、窒素酸化物をアルカリに吸収除去する方
法等が知られているが、移動発生源である自動車に用い
るには有効な方法ではなく、適用が限定される。[0004] As a method for removing nitrogen oxides from such oxygen-excess exhaust gas, there are known methods such as adding a reducing agent such as ammonia, and removing nitrogen oxides by absorption with alkali. It is not an effective method for use in automobiles, which are mobile sources, and its application is limited.
【0005】近年、遷移金属をイオン交換したゼオライ
ト触媒は、アンモニア等の特別な還元剤を添加しなくて
も酸素過剰な排ガス中の窒素酸化物を除去できることが
報告されている。例えば特開昭63−283727号公
報や特開平1−130735号公報には、未燃焼の一酸
化炭素及び炭化水素等の還元剤が微量に含まれている酸
素過剰な排ガス中でも窒素酸化物を選択的に還元させる
ことが出来るゼオライト系触媒が提案されている。[0005] In recent years, it has been reported that a zeolite catalyst in which transition metals are ion-exchanged can remove nitrogen oxides from oxygen-excess exhaust gas without adding a special reducing agent such as ammonia. For example, in JP-A-63-283727 and JP-A-1-130735, nitrogen oxides are selected even in oxygen-excess exhaust gas that contains trace amounts of reducing agents such as unburned carbon monoxide and hydrocarbons. A zeolite-based catalyst has been proposed that can reduce the
【0006】しかし、これらの従来提案に係わる触媒は
、長時間の高温下での使用による活性の劣化が著しく、
耐久性、触媒性能等の点で改善する必要があった。However, the activity of these conventionally proposed catalysts deteriorates significantly when used at high temperatures for long periods of time.
Improvements were needed in terms of durability, catalytic performance, etc.
【0007】そこで、これらの問題点を解決する触媒と
して、SiO2/Al2O3モル比が少なくとも15以
上のゼオライトであり、かつコバルトおよびアルカリ土
類金属を含有することを特徴とする排ガス浄化触媒が提
案されている(特願平1−337249号)。[0007] Therefore, as a catalyst to solve these problems, an exhaust gas purification catalyst has been proposed, which is a zeolite with a SiO2/Al2O3 molar ratio of at least 15 and contains cobalt and an alkaline earth metal. (Patent Application No. 1-337249).
【0008】[0008]
【発明が解決しようとする課題】しかしながら、特願平
1−337249号で提案された排ガス浄化触媒は、耐
久性は改善されたが、窒素酸化物を浄化できる温度域は
比較的高温で狭いため、内燃機関、特に自動車の排気ガ
ス浄化用の触媒としては、更に低温でのより高い窒素酸
化物浄化能が要求される。[Problems to be Solved by the Invention] However, although the exhaust gas purification catalyst proposed in Japanese Patent Application No. 1-337249 has improved durability, the temperature range in which nitrogen oxides can be purified is relatively high and narrow. Catalysts for purifying exhaust gas from internal combustion engines, particularly automobiles, are required to have even higher nitrogen oxide purification ability at lower temperatures.
【0009】本発明の目的は、以上のような従来技術の
問題点を解消するためになされたものであり、自動車等
の内燃機関から排出される排ガスから、窒素酸化物、一
酸化炭素及び炭化水素を同時に除去し、更に熱劣化を起
こしにくく耐久性に優れ、触媒性能の高い触媒を提供す
るところにある。[0009] The purpose of the present invention was to solve the problems of the prior art as described above. The aim is to provide a catalyst that simultaneously removes hydrogen, is less prone to thermal deterioration, has excellent durability, and has high catalytic performance.
【0010】また本発明の別の目的は、このような触媒
を用いた排ガスの浄化方法を提供することにある。Another object of the present invention is to provide a method for purifying exhaust gas using such a catalyst.
【0011】[0011]
【課題を解決するための手段】本発明者等は、上記問題
点について鋭意検討した結果、先に提案されたSiO2
/Al2O3モル比が少なくとも15以上のゼオライト
であり、かつコバルト及びアルカリ土類金属を含有する
排ガス浄化触媒に更に銅及び/又はロジウムを含有させ
ることにより低温での窒素酸化物浄化能が向上すること
を見出し、本発明を完成するに至った。[Means for Solving the Problems] As a result of intensive study on the above-mentioned problems, the present inventors have developed the previously proposed SiO2
/Al2O3 molar ratio is at least 15 or more, and the nitrogen oxide purification ability at low temperatures is improved by further containing copper and/or rhodium in the exhaust gas purification catalyst containing cobalt and alkaline earth metals. They discovered this and completed the present invention.
【0012】すなわち本発明は、窒素酸化物、一酸化炭
素及び炭化水素を含む酸素過剰の排ガスから、窒素酸化
物、一酸化炭素及び炭化水素を除去するゼオライト触媒
であって、SiO2/Al2O3モル比が少なくとも1
5以上のゼオライトであり、かつコバルト及びアルカリ
土類金属並びに銅及び/又はロジウムを含有することを
特徴とする排ガス浄化触媒、及び該排ガス浄化触媒に、
窒素酸化物、一酸化炭素及び炭化水素を含む燃焼排ガス
を接触させることを特徴とする排ガス中の窒素酸化物、
一酸化炭素及び炭化水素を除去する方法を提供するもの
である。That is, the present invention provides a zeolite catalyst for removing nitrogen oxides, carbon monoxide, and hydrocarbons from oxygen-excess exhaust gas containing nitrogen oxides, carbon monoxide, and hydrocarbons, the catalyst having a SiO2/Al2O3 molar ratio. is at least 1
An exhaust gas purification catalyst characterized by being a zeolite of 5 or more and containing cobalt and alkaline earth metals and copper and/or rhodium, and the exhaust gas purification catalyst,
Nitrogen oxides in exhaust gas, characterized by contacting combustion exhaust gases containing nitrogen oxides, carbon monoxide and hydrocarbons,
A method for removing carbon monoxide and hydrocarbons is provided.
【0013】以下、本発明を詳細に説明する。The present invention will be explained in detail below.
【0014】本発明にかかる排ガス浄化触媒は、コバル
ト及びアルカリ土類金属並びに銅及び/又はロジウムを
含有させたSiO2/Al2O3モル比が少なくとも1
5であるゼオライトである。The exhaust gas purification catalyst according to the present invention contains cobalt and alkaline earth metals and copper and/or rhodium and has a SiO2/Al2O3 molar ratio of at least 1.
It is a zeolite with a rating of 5.
【0015】上記ゼオライトは一般的にはxM2/nO
・Al2O3・ySiO2・zH2O(ただしnは陽イ
オンMの原子価、xは0.8〜1.2の範囲の数、yは
2以上の数、zは0以上の数である)の組成を有するも
のであるが、本発明において用いられるゼオライトはこ
のうち、SiO2/Al2O3モル比が15以上のもの
である。SiO2/Al2O3モル比はその上限は特に
限定されるものではないが、SiO2/Al2O3モル
比が15未満であるとゼオライト自体の耐熱性、耐久性
が低いため、触媒の十分な耐熱性、耐久性が得られない
。一般的にはSiO2/Al2O3モル比が15〜10
00程度のものが用いられる。[0015] The above zeolite generally has xM2/nO
・The composition of Al2O3・ySiO2・zH2O (where n is the valence of the cation M, x is a number in the range of 0.8 to 1.2, y is a number of 2 or more, and z is a number of 0 or more) Among them, the zeolite used in the present invention has a SiO2/Al2O3 molar ratio of 15 or more. The upper limit of the SiO2/Al2O3 molar ratio is not particularly limited, but if the SiO2/Al2O3 molar ratio is less than 15, the heat resistance and durability of the zeolite itself will be low. is not obtained. Generally, the SiO2/Al2O3 molar ratio is 15 to 10.
A value of about 00 is used.
【0016】本発明の触媒を構成するゼオライトは天然
品、合成品の何れであってもよく、これらゼオライトの
製造方法は特に限定されるものではないが、代表的には
フェリエライト、Y、ZSM−5、ZSM−11、ZS
M−12、ZSM−20等のゼオライトが使用できる。
また、これらのゼオライトは、そのままあるいはアンモ
ニウム塩、鉱酸等で処理してNH4型あるいはH型にイ
オン交換してから本発明の触媒として使用することもで
きる。The zeolite constituting the catalyst of the present invention may be either a natural product or a synthetic product, and the method for producing these zeolites is not particularly limited, but typically ferrierite, Y, ZSM -5, ZSM-11, ZS
Zeolites such as M-12 and ZSM-20 can be used. Further, these zeolites can be used as the catalyst of the present invention either as they are or after being ion-exchanged into NH4 type or H type by treatment with ammonium salts, mineral acids, etc.
【0017】本発明で用いるゼオライトは、コバルト及
びアルカリ土類金属並びに銅及び/又はロジウムを含有
する。銅とロジウムは同時に含有していてもよいが,ど
ちらか一方を含有していればよい。ゼオライトにコバル
ト及びアルカリ土類金属並びに銅及び/又はロジウムを
含有させる方法としては、特に限定されず、一般には、
水溶性の塩を用いてイオン交換や含浸担持法、蒸発乾固
法等により含有させることができる。含有させる際、各
々の元素は順次含有させてもかまわないし、一度に含有
させてもかまわない。The zeolite used in the present invention contains cobalt and alkaline earth metals as well as copper and/or rhodium. Copper and rhodium may be contained at the same time, but only one of them may be contained. The method for incorporating cobalt and alkaline earth metals and copper and/or rhodium into zeolite is not particularly limited, and generally,
It can be contained using a water-soluble salt by ion exchange, an impregnation support method, an evaporation-drying method, or the like. When containing each element, each element may be contained sequentially or all at once.
【0018】コバルト及びアルカリ土類金属並びに銅及
び/又はロジウムを含有させる際の水溶液中のコバルト
、アルカリ土類金属,銅及び/又はロジウムイオンの濃
度は、目的とする触媒のイオン交換率によって任意に設
定することができる。アルカリ土類金属イオンとしては
、Ca,Mg,Sr,Ba等が使用できる。また、コバ
ルト及びアルカリ土類金属並びに銅及び/又はロジウム
イオンは可溶性の塩の形で使用でき、可溶性の塩として
は、硝酸塩、酢酸塩、シュウ酸塩、塩酸塩等が好適に使
用できる。[0018] The concentration of cobalt, alkaline earth metal, copper and/or rhodium ions in the aqueous solution when containing cobalt and alkaline earth metals and copper and/or rhodium can be determined arbitrarily depending on the ion exchange rate of the target catalyst. Can be set to . As the alkaline earth metal ion, Ca, Mg, Sr, Ba, etc. can be used. Further, cobalt and alkaline earth metals and copper and/or rhodium ions can be used in the form of soluble salts, and nitrates, acetates, oxalates, hydrochlorides, etc. can be preferably used as the soluble salts.
【0019】コバルト及びアルカリ土類金属並びに銅及
び/又はロジウムの含有量としては、ゼオライト中のア
ルミナモル数に対するモル比で、コバルトは0.1〜1
.5倍、アルカリ土類金属は0.1〜1倍、銅あるいは
ロジウムは0.05〜1.5倍が好ましく、コバルト及
びアルカリ土類金属並びに銅及び/又はロジウムの量を
合計して1.0〜2.5倍が好ましい。The content of cobalt and alkaline earth metals and copper and/or rhodium is 0.1 to 1 in terms of molar ratio to the number of moles of alumina in the zeolite.
.. 5 times, preferably 0.1 to 1 times for alkaline earth metals, and 0.05 to 1.5 times for copper or rhodium, and the total amount of cobalt and alkaline earth metals and copper and/or rhodium is 1. 0 to 2.5 times is preferable.
【0020】コバルト及びアルカリ土類金属並びに銅及
び/又はロジウムを含有させた試料は、一般に、固液分
離、洗浄、乾燥して使用される。また、必要に応じて焼
成してから用いることもできる。Samples containing cobalt and alkaline earth metals and copper and/or rhodium are generally used after solid-liquid separation, washing and drying. Moreover, it can also be used after baking if necessary.
【0021】本発明の排ガス浄化触媒は、粘土鉱物等の
バインダーと混合し成形して使用することもできる。ま
た、予めゼオライトを成形し、その成形体にコバルト及
びアルカリ土類金属並びに銅及び/又はロジウムを含有
させることもできる。ゼオライトを成形する際に用いら
れるバインダーとしては、特に制限はないが、カオリン
、アタパルガイト、モンモリロナイト、ベントナイト、
アロフェン、セピオライト等の粘土鉱物やシリカ、アル
ミナ等が使用できる。あるいは、バインダーを用いずに
成形体を直接合成したバインダレスゼオライト成形体で
あっても良い。また、コージェライト製あるいは金属製
のハニカム状基材にゼオライトをウォッシュコートして
用いることもできる。The exhaust gas purification catalyst of the present invention can also be used by mixing it with a binder such as clay minerals and molding the mixture. Alternatively, zeolite can be molded in advance and the molded product can contain cobalt, alkaline earth metals, and copper and/or rhodium. There are no particular restrictions on the binder used when molding zeolite, but examples include kaolin, attapulgite, montmorillonite, bentonite,
Clay minerals such as allophane and sepiolite, silica, alumina, etc. can be used. Alternatively, it may be a binderless zeolite molded product that is directly synthesized without using a binder. Moreover, zeolite can be wash-coated onto a cordierite or metal honeycomb base material.
【0022】酸素過剰排ガスの窒素酸化物、一酸化炭素
、炭化水素の除去は、本発明の排ガス浄化触媒と該排ガ
スを接触させることにより行うことができる。本発明が
対象とする酸素過剰の排ガスとは、排ガス中に含まれる
一酸化炭素、炭化水素及び水素を完全に酸化するのに必
要な酸素量よりも過剰な酸素が含まれている排ガスをい
い、このような排ガスとしては例えば、自動車等の内燃
機関から排出される排ガス、特に空燃費が大きい状態(
所謂リーン領域)での排ガス等が具体的に例示される。[0022] Removal of nitrogen oxides, carbon monoxide, and hydrocarbons from oxygen-excess exhaust gas can be carried out by bringing the exhaust gas into contact with the exhaust gas purification catalyst of the present invention. The oxygen-excessive exhaust gas that is the object of the present invention refers to exhaust gas that contains oxygen in excess of the amount of oxygen required to completely oxidize carbon monoxide, hydrocarbons, and hydrogen contained in the exhaust gas. Examples of such exhaust gas include exhaust gas emitted from internal combustion engines such as automobiles, especially when air and fuel consumption is high (
A specific example is exhaust gas in a so-called lean region.
【0023】なお上記排ガス触媒は、一酸化炭素、炭化
水素及び水素を含み酸素過剰でない排ガスの場合に適用
されても、何等その性能が変化することはない。[0023] Even if the above exhaust gas catalyst is applied to exhaust gas containing carbon monoxide, hydrocarbons and hydrogen and not in excess of oxygen, its performance will not change in any way.
【0024】[0024]
【実施例】以下、本発明を実施例により更に詳細に説明
するが、本発明はこれら実施例に限定されるものではな
い。[Examples] The present invention will be explained in more detail with reference to Examples below, but the present invention is not limited to these Examples.
【0025】比較例1 <比較触媒1の調製>特開昭
59−54620号公報実施例5の方法に従ってZSM
−5類似ゼオライトを合成した。無水ベースにおける酸
化物のモル比で表わして、次の化学組成を有していた。Comparative Example 1 <Preparation of Comparative Catalyst 1> ZSM was prepared according to the method of Example 5 of JP-A-59-54620.
-5 similar zeolite was synthesized. It had the following chemical composition, expressed as molar ratios of oxides on an anhydrous basis.
【0026】
1.1Na2O・Al2O3・40SiO2これを塩化
アンモニウム水溶液でイオン交換して調製したアンモニ
ウム型ZSM−5;200gを、濃度1.09mol/
lの塩化バリウムの水溶液1800mlに投入し、80
℃で16時間攪拌した。固液分離後、充分水洗し、続け
て0.23mol/lの酢酸コバルト(II)4水和物
の水溶液700mlに投入し、80℃で16時間攪拌し
た。スラリ−を固液分離後、ゼオライトケ−キを再度調
製した上記組成の水溶液に投入して同様な操作を行った
。固液分離後、充分水洗し、110℃で10時間乾燥し
、比較触媒1を得た。この触媒のバリウムおよびコバル
ト含有量を化学分析で調べたところ、ゼオライトのAl
2O3モル数に対して、バリウムは0.58倍、コバル
トは2価として0.49倍含まれていた。1.1Na2O・Al2O3・40SiO2 Ammonium type ZSM-5 prepared by ion exchange with ammonium chloride aqueous solution;
of barium chloride in 1,800 ml of an aqueous solution of 80
Stirred at ℃ for 16 hours. After solid-liquid separation, the mixture was thoroughly washed with water, then poured into 700 ml of an aqueous solution of 0.23 mol/l cobalt (II) acetate tetrahydrate, and stirred at 80° C. for 16 hours. After solid-liquid separation of the slurry, the zeolite cake was added to the prepared aqueous solution having the above composition and the same operation was performed. After solid-liquid separation, it was thoroughly washed with water and dried at 110°C for 10 hours to obtain Comparative Catalyst 1. When the barium and cobalt contents of this catalyst were investigated by chemical analysis, it was found that the Al of the zeolite
The amount of barium was 0.58 times the number of moles of 2O3, and the amount of cobalt was 0.49 times as divalent.
【0027】実施例1<触媒1の調製>比較例1で得た
アンモニウム型ZSM−5;200gを、濃度1.09
mol/lの塩化バリウムの水溶液1800mlに投入
し、80℃で16時間攪拌した。固液分離後、充分水洗
し、続けて0.23mol/lの硝酸コバルト(II)
4水和物の水溶液1800mlに投入し、80℃で16
時間攪拌した。スラリ−を固液分離後、ゼオライトケ−
キを再度調製した上記組成の水溶液に投入して同様な操
作を行った。固液分離後、充分水洗し、110℃で20
時間乾燥し、コバルト及びバリウム含有ZSM−5を得
た。得られたコバルト及びバリウム含有ZSM−5;1
5gを、濃度0.05mol/lの酢酸銅水溶液43m
lに投入し、撹拌しながら減圧乾燥し、更に110℃で
16時間乾燥し、触媒1を得た。この触媒のバリウム、
コバルト及び銅の含有量を化学分析で調べたところ、ゼ
オライトのAl2O3モル数に対して、バリウムは0.
52倍、コバルトは2価として0.32倍、銅は0.4
倍含まれていた。Example 1 <Preparation of Catalyst 1> 200 g of ammonium type ZSM-5 obtained in Comparative Example 1 was prepared at a concentration of 1.09.
The mixture was poured into 1800 ml of a mol/l barium chloride aqueous solution and stirred at 80° C. for 16 hours. After solid-liquid separation, it was thoroughly washed with water, and then 0.23 mol/l of cobalt(II) nitrate was added.
Pour into 1800 ml of an aqueous solution of tetrahydrate and heat at 80°C for 16
Stir for hours. After solid-liquid separation of slurry, zeolite cake
The same operation was carried out by putting the sample into the aqueous solution having the above composition prepared again. After solid-liquid separation, wash thoroughly with water and incubate at 110°C for 20
After drying for hours, ZSM-5 containing cobalt and barium was obtained. Obtained cobalt and barium containing ZSM-5;1
5g to 43ml of copper acetate aqueous solution with a concentration of 0.05mol/l.
1, and dried under reduced pressure while stirring, and further dried at 110° C. for 16 hours to obtain catalyst 1. This catalyst barium,
When the content of cobalt and copper was investigated by chemical analysis, it was found that barium was 0.0% compared to the number of moles of Al2O3 in zeolite.
52 times, cobalt is 0.32 times as divalent, copper is 0.4
twice included.
【0028】実施例2 <触媒2の調製>酢酸銅を硝
酸ロジウムに変えたこと以外は実施例1と同様な操作で
触媒2を調製した。この触媒のバリウム、コバルト及び
ロジウムの含有量を化学分析で調べたところ、ゼオライ
トのAl2O3モル数に対して、バリウムは0.52倍
、コバルトは2価として0.32倍、ロジウムは0.4
倍含まれていた。Example 2 <Preparation of Catalyst 2> Catalyst 2 was prepared in the same manner as in Example 1 except that copper acetate was replaced with rhodium nitrate. When the content of barium, cobalt and rhodium in this catalyst was investigated by chemical analysis, it was found that barium is 0.52 times, cobalt is 0.32 times as divalent, and rhodium is 0.4 times the number of moles of Al2O3 in the zeolite.
twice included.
【0029】比較例2 <比較触媒2の調製>比較例
1で得たアンモニウム型ZSM−5;200gを、濃度
1.09mol/lの塩化ストロンチウムの水溶液18
00mlに投入し、80℃で16時間攪拌した。固液分
離後、充分水洗し、続けて0.23mol/lの酢酸コ
バルト(II)4水和物の水溶液1800mlに投入し
、80℃で16時間攪拌した。スラリ−を固液分離後、
ゼオライトケ−キを再度調製した上記組成の水溶液に投
入して同様な操作を行った。固液分離後、充分水洗し、
110℃で10時間乾燥し、比較触媒2を得た。この触
媒のストロンチウムおよびコバルト含有量を化学分析で
調べたところ、ゼオライトのAl2O3モル数に対して
、ストロンチウムは0.23倍およびコバルトは2価と
して1.12倍含まれていた。Comparative Example 2 <Preparation of Comparative Catalyst 2> 200 g of the ammonium type ZSM-5 obtained in Comparative Example 1 was added to an aqueous solution of strontium chloride with a concentration of 1.09 mol/l.
00ml and stirred at 80°C for 16 hours. After solid-liquid separation, the mixture was thoroughly washed with water, then poured into 1800 ml of an aqueous solution of 0.23 mol/l cobalt (II) acetate tetrahydrate, and stirred at 80° C. for 16 hours. After solid-liquid separation of slurry,
The zeolite cake was again put into the aqueous solution having the above composition and the same operation was performed. After solid-liquid separation, wash thoroughly with water,
Comparative catalyst 2 was obtained by drying at 110° C. for 10 hours. When the strontium and cobalt contents of this catalyst were investigated by chemical analysis, it was found that strontium was contained 0.23 times and cobalt was contained 1.12 times as divalent relative to the number of moles of Al2O3 in the zeolite.
【0030】実施例3 <触媒3の調製>比較例2で
調製した比較触媒2;15gを、濃度0.05mol/
lの硝酸銅水溶液43mlに投入し、撹拌しながら減圧
乾燥し、更に110℃で16時間乾燥し、触媒3を得た
。
この触媒のストロンチウム、コバルト及び銅の含有量を
化学分析で調べたところ、ゼオライトのAl2O3モル
数に対して、ストロンチウムは0.23倍、コバルトは
2価として1.12倍、銅は0.4倍含まれていた。
実施例4 <触媒4の調製>硝酸銅を硝酸ロジウム
に変えたこと以外は実施例3と同様な操作で触媒4を調
製した。この触媒のストロンチウム、コバルト及びロジ
ウムの含有量を化学分析で調べたところ、ゼオライトの
Al2O3モル数に対して、ストロンチウムは0.23
倍、コバルトは2価として1.12倍、ロジウムは0.
4倍含まれていた。Example 3 <Preparation of Catalyst 3> 15 g of Comparative Catalyst 2 prepared in Comparative Example 2 was added to a concentration of 0.05 mol/
The catalyst was poured into 43 ml of aqueous copper nitrate solution, dried under reduced pressure while stirring, and further dried at 110° C. for 16 hours to obtain catalyst 3. When the content of strontium, cobalt and copper in this catalyst was investigated by chemical analysis, strontium was 0.23 times the Al2O3 mole of zeolite, cobalt was 1.12 times as divalent, and copper was 0.4 times. twice included.
Example 4 <Preparation of Catalyst 4> Catalyst 4 was prepared in the same manner as in Example 3 except that copper nitrate was replaced with rhodium nitrate. When the content of strontium, cobalt and rhodium in this catalyst was investigated by chemical analysis, it was found that strontium was 0.23% of the number of moles of Al2O3 in the zeolite.
Cobalt is 1.12 times as divalent, Rhodium is 0.
It contained 4 times more.
【0031】実施例5 <触媒の活性評価>触媒1〜
4および比較触媒1、2を各々プレス成形後破砕して1
2〜20メッシュに整粒し、その1gを常圧固定床反応
管に充填した。下記に示す組成のガス(以下、反応ガス
という)を1000ml/min.で流通しながら、5
00℃まで昇温し、0.5時間保持し前処理とした。そ
の後、250℃から450℃の間、50℃毎に温度を一
定に保ち、各温度における触媒活性を測定した。各温度
で定常に達した後のNO浄化率を表1に示す。NO浄化
率とは、次式により求めた値である。Example 5 <Evaluation of catalyst activity> Catalyst 1~
4 and Comparative Catalysts 1 and 2 were crushed after press molding to obtain 1.
The particles were sized to 2 to 20 mesh, and 1 g of the particles was filled into an atmospheric fixed bed reaction tube. A gas having the composition shown below (hereinafter referred to as reaction gas) was supplied at a rate of 1000 ml/min. While circulating in 5
The temperature was raised to 00° C. and held for 0.5 hours as a pretreatment. Thereafter, the temperature was kept constant at every 50°C between 250°C and 450°C, and the catalytic activity at each temperature was measured. Table 1 shows the NO purification rate after reaching steady state at each temperature. The NO purification rate is a value determined by the following formula.
【0032】[0032]
【数1】
なお、比較触媒では、一酸化炭素は450℃以上で、炭
化水素は400℃以上でほとんど検出されなかったが、
実施例触媒では、一酸化炭素は400℃以上で、炭化水
素は350℃以上でほとんど検出されなかった。[Formula 1] Note that with the comparative catalyst, carbon monoxide was hardly detected at temperatures above 450°C and hydrocarbons were hardly detected at temperatures above 400°C.
In the example catalyst, carbon monoxide was hardly detected at temperatures of 400°C or higher, and hydrocarbons were hardly detected at temperatures of 350°C or higher.
【0033】[0033]
【0034】[0034]
【表1】[Table 1]
【0035】[0035]
【発明の効果】表1より、本発明の触媒は、比較触媒よ
りも、酸素過剰排ガスの排ガス浄化能、特に低温での窒
素酸化物の浄化能が高い。従って、本発明の触媒を排ガ
スと接触させることにより、酸素過剰の排ガスであって
も、より低温で排ガスを浄化することができる。Effects of the Invention From Table 1, the catalyst of the present invention has a higher ability to purify oxygen-excess exhaust gas, especially nitrogen oxides at low temperatures, than the comparative catalyst. Therefore, by bringing the catalyst of the present invention into contact with exhaust gas, even if the exhaust gas contains excess oxygen, the exhaust gas can be purified at a lower temperature.
Claims (1)
15であるゼオライトにコバルト及びアルカリ土類金属
並びに銅及び/又はロジウムを含むことを特徴とする、
窒素酸化物、一酸化炭素及び炭化水素を含む酸素過剰の
排ガスから、窒素酸化物、一酸化炭素及び炭化水素を除
去する排ガス浄化触媒。1. A zeolite with a SiO2/Al2O3 molar ratio of at least 15 containing cobalt and alkaline earth metals and copper and/or rhodium,
An exhaust gas purification catalyst that removes nitrogen oxides, carbon monoxide, and hydrocarbons from oxygen-excess exhaust gas containing nitrogen oxides, carbon monoxide, and hydrocarbons.
Priority Applications (7)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2411255A JPH04219144A (en) | 1990-12-18 | 1990-12-18 | Exhaust gas purification catalyst |
US07/805,956 US5208198A (en) | 1990-12-18 | 1991-12-12 | Catalyst for purifying exhaust gas |
AU89787/91A AU650701B2 (en) | 1990-12-18 | 1991-12-16 | Catalyst for purifying exhaust gas |
CA002057702A CA2057702C (en) | 1990-12-18 | 1991-12-16 | Catalyst for purifying exhaust gas |
EP91121618A EP0491359B1 (en) | 1990-12-18 | 1991-12-17 | Catalyst for purifying exhaust gas |
DE69104969T DE69104969T2 (en) | 1990-12-18 | 1991-12-17 | Catalytic converter for cleaning exhaust gases. |
US08/218,294 US5382416A (en) | 1990-12-18 | 1994-03-28 | Method for purifying exhaust gas |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2411255A JPH04219144A (en) | 1990-12-18 | 1990-12-18 | Exhaust gas purification catalyst |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH04219144A true JPH04219144A (en) | 1992-08-10 |
Family
ID=18520282
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2411255A Pending JPH04219144A (en) | 1990-12-18 | 1990-12-18 | Exhaust gas purification catalyst |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH04219144A (en) |
-
1990
- 1990-12-18 JP JP2411255A patent/JPH04219144A/en active Pending
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