WO1990005579A1 - Oxidation process and catalyst - Google Patents
Oxidation process and catalyst Download PDFInfo
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- WO1990005579A1 WO1990005579A1 PCT/US1989/004955 US8904955W WO9005579A1 WO 1990005579 A1 WO1990005579 A1 WO 1990005579A1 US 8904955 W US8904955 W US 8904955W WO 9005579 A1 WO9005579 A1 WO 9005579A1
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- Prior art keywords
- catalyst
- process according
- platinum
- platinum group
- group metal
- Prior art date
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- 239000003054 catalyst Substances 0.000 title claims abstract description 95
- 238000000034 method Methods 0.000 title claims description 20
- 230000003647 oxidation Effects 0.000 title description 15
- 238000007254 oxidation reaction Methods 0.000 title description 15
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical group [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims abstract description 53
- 229910052751 metal Inorganic materials 0.000 claims abstract description 33
- 239000002184 metal Substances 0.000 claims abstract description 33
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims abstract description 26
- 229930195733 hydrocarbon Natural products 0.000 claims abstract description 21
- 150000002430 hydrocarbons Chemical class 0.000 claims abstract description 21
- 230000001590 oxidative effect Effects 0.000 claims abstract description 18
- 239000002912 waste gas Substances 0.000 claims abstract description 17
- PNEYBMLMFCGWSK-UHFFFAOYSA-N Alumina Chemical compound [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims abstract description 16
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 14
- MCMNRKCIXSYSNV-UHFFFAOYSA-N Zirconium dioxide Chemical compound O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 claims abstract description 11
- 229910021536 Zeolite Inorganic materials 0.000 claims abstract description 10
- 239000010457 zeolite Substances 0.000 claims abstract description 10
- 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 7
- 239000000377 silicon dioxide Substances 0.000 claims abstract description 5
- 239000010948 rhodium Substances 0.000 claims description 17
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 claims description 15
- 239000000203 mixture Substances 0.000 claims description 14
- 239000007789 gas Substances 0.000 claims description 13
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 12
- 239000003546 flue gas Substances 0.000 claims description 12
- 229910052697 platinum Inorganic materials 0.000 claims description 12
- 229910052703 rhodium Inorganic materials 0.000 claims description 9
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 claims description 9
- 229910052763 palladium Inorganic materials 0.000 claims description 6
- 239000002803 fossil fuel Substances 0.000 claims description 4
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 abstract description 14
- 229910052717 sulfur Inorganic materials 0.000 abstract description 14
- 239000011593 sulfur Substances 0.000 abstract description 14
- 230000001747 exhibiting effect Effects 0.000 abstract 1
- 238000006243 chemical reaction Methods 0.000 description 21
- ATUOYWHBWRKTHZ-UHFFFAOYSA-N Propane Chemical compound CCC ATUOYWHBWRKTHZ-UHFFFAOYSA-N 0.000 description 14
- 239000000969 carrier Substances 0.000 description 8
- 229910002091 carbon monoxide Inorganic materials 0.000 description 7
- 239000001294 propane Substances 0.000 description 7
- 238000005470 impregnation Methods 0.000 description 6
- -1 platinum group metals Chemical class 0.000 description 6
- 239000002002 slurry Substances 0.000 description 6
- 239000000758 substrate Substances 0.000 description 6
- 239000000919 ceramic Substances 0.000 description 5
- 238000001354 calcination Methods 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 150000003464 sulfur compounds Chemical class 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- 239000004215 Carbon black (E152) Substances 0.000 description 3
- 239000002253 acid Substances 0.000 description 3
- 229910052500 inorganic mineral Inorganic materials 0.000 description 3
- 150000002739 metals Chemical class 0.000 description 3
- 239000011707 mineral Substances 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- 239000010970 precious metal Substances 0.000 description 3
- 230000010718 Oxidation Activity Effects 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 239000012876 carrier material Substances 0.000 description 2
- 239000011888 foil Substances 0.000 description 2
- 150000007524 organic acids Chemical class 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 238000000518 rheometry Methods 0.000 description 2
- OTMSDBZUPAUEDD-UHFFFAOYSA-N Ethane Chemical compound CC OTMSDBZUPAUEDD-UHFFFAOYSA-N 0.000 description 1
- KJTLSVCANCCWHF-UHFFFAOYSA-N Ruthenium Chemical compound [Ru] KJTLSVCANCCWHF-UHFFFAOYSA-N 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 229910007735 Zr—Si Inorganic materials 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 239000011149 active material Substances 0.000 description 1
- 239000003570 air Substances 0.000 description 1
- 229910045601 alloy Inorganic materials 0.000 description 1
- 239000000956 alloy Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 230000009849 deactivation Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 238000010304 firing Methods 0.000 description 1
- 238000009472 formulation Methods 0.000 description 1
- 229910052809 inorganic oxide Inorganic materials 0.000 description 1
- 229910052741 iridium Inorganic materials 0.000 description 1
- GKOZUEZYRPOHIO-UHFFFAOYSA-N iridium atom Chemical compound [Ir] GKOZUEZYRPOHIO-UHFFFAOYSA-N 0.000 description 1
- 150000007522 mineralic acids Chemical class 0.000 description 1
- 230000000877 morphologic effect Effects 0.000 description 1
- 229910052762 osmium Inorganic materials 0.000 description 1
- SYQBFIAQOQZEGI-UHFFFAOYSA-N osmium atom Chemical compound [Os] SYQBFIAQOQZEGI-UHFFFAOYSA-N 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 229910052707 ruthenium Inorganic materials 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 238000004441 surface measurement Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/38—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
- B01J23/40—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals of the platinum group metals
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/944—Simultaneously removing carbon monoxide, hydrocarbons or carbon making use of oxidation catalysts
Definitions
- This invention relates to an improved process and catalyst for the oxidative removal of CO and hydrocarbons from waste gas streams which can also contain sulfur compounds.
- this invention relates to supported platinum group metal catalysts that exhibit superior performance for the oxidative removal of CO and hydrocarbons from waste gas streams by conversion of CO and hydrocarbons to innocuous materials such as flue gases from engines combusting fossil fuels.
- this invention relates to a low temperature oxidative process for the removal of CO and hydrocarbons from waste gas streams by contacting with a catalyst comprising a platinum group metal and at least one sulfur tc rant carrier.
- Ideal catalysts should be stable and durable in the presence of SO, in the flue gas.
- the present invention avoids the problems of the prior art by providing improved oxidation catalyst compositions having good activity and durability for the treatment of sulfur-containing flue gas streams.
- the present invention provides catalyst compositions comprising carriers which interact favorably with platinum-group metals and which are resistant to reaction with oxides of sulfur and exhibit superior performance for low temperature oxidative removal of CO and hydrocarbons from waste gas streams.
- an object of the invention is to provide improved platinum- group metal catalysts.
- Another object of this invention is to provide a commercially effective process and catalyst for the oxidative removal of CO and hydrocarbons from sulfur-containing waste gas streams.
- a further object of the invention is to provide platinum-group metal catalysts having good activity, durability, and long catalyst life in the treatment of sulfur-containing waste gas streams.
- a still further object is to provide a catalyst and process effective for the oxidative removal of CO and hydrocarbons from waste gas streams at low temperatures.
- a catalyst and process are provided for the oxidative removal of CO and hydrocarbons from waste gas streams by contacting same at relatively low temperatures with a catalytically effective amount of an oxidation catalyst comprising catalyst carriers which interact favorably with platinum group metals and are resistant to reaction with oxides of sulfur that can be present in such streams.
- a process for the oxidative removal of CO and hydrocarbons from either S0 x -containing or SO x -free waste streams which comprises contacting said waste gas stream in an oxidizing atmosphere under oxidizing conditions at a temperature below about
- an effective oxidation catalyst comprising at least one platinum group metal supported on at least one of silica, zirconia, titania, zeolite, and alpha alumina or combinations thereof.
- the present catalysts maintain their oxidation activity in the presence of sulfur-containing flue gases and, therefore, these catalysts can be effectively utilized commercially for oxidation of gas streams that are either S0 x -containing or S0 x -free.
- the invention comprises a platinum group metal catalyst supported on carriers that are resistant to reaction with oxides of sulfur and to a process for the oxidation of CO and hydrocarbons in gas streams which can contain sulfur compounds in the presence of the invention platinum group metal catalyst.
- the catalyst of the invention comprises at least one platinum group metal and at least one of silica, zirconia, titania, zeolite, and low surface area alpha-phase alumina in any combination.
- platinum group metals that can be used include platinum, palladium, rhodium, ruthenium, osmium and iridium and mixtures thereof. Presently preferred are one or more of platinum, palladium and rhodium.
- the amount of platinum group metal present in the catalyst composition is an oxidative catalytically effective amount. Generally, the total amount of platinum metal present ranges from about 0.005 to about 2 weight percent of the catalyst composition. A mixture of platinum group metals can be used in any ratio of one platinum group metal to another.
- the carriers that can be used that interact favorably with platinum group metals and which are resistant to reaction with oxides of sulfur include one or more of silica, zirconia, titania, zeolite, and low surface area alpha-phase alumina. Other than the alumina, "the other carriers are high surface are materials. The surface area of these carriers generally is in the range of about 20 m 2 /g to about 1000 m 2 /g as measured by Brunauer, Emmett and Teller surface measurement technique.
- a ceramic or metallic monolith is used as a support material.
- the metal monolith consists of alternate layers of flat and corrugated foil strips stacked to form a honeycomb structure.
- the foil is typically 0.002 inches thick and can be any of several ferritic stainless steels or other alloys. Cell densities of 100, 200, and 400 cell/sq. in. are obtained by varying the spacing and depth of the corrugations.
- the carrier materials are well known in the art and can be prepared by methods known in the art. One method that can be used for the preparation of the carriers is to mix the desired oxide with water to form the inorganic oxide material. The morphological and rheological properties of the oxide-water mixture can be adjusted by adding organic or inorganic acids or base. The oxide-water mixture can be applied to metal or ceramic monoliths, dried and then fired at 250 to 650*C. The firing step is optional.
- a catalytically active material from the precious metal groups is deposited by impregnation, for example, on the carrier material.
- the catalyst composition after deposition of the platinum metal on the carrier can be calcined at a temperature of about 300- 500°C. This calcination is also optional.
- the catalysts of the invention can be formed into any shape desired and used in fixed bed, moving b i, fluidized bed or other known types of contacting with the stream to be oxidatively treated.
- the invention comprises the oxidative removal of CO and hydrocarbons from either S0_-containing or S0 x -free gas streams in an oxidizing atmosphere under effective oxidation conditions of temperature, pressure, contact time and space velocity in the presence of the platinum group metal catalyst defined above.
- the invention is applicable to the treatment of any gas stream containing CO and hydrocarbons, especially lower hydrocarbons, such as ethane, propane, and the like. These streams include waste gases exhausted from engines combusting fossil fuels which may or may not contain sulfur compounds.
- the catalyst In actual operation of an oxidation system, the catalyst is installed at a place in the gas flow path at which the temperature is below about 500*C, usually about 150 to about 500 * C.
- the gas hourly space velocity (GHSV) of the gas stream in contact with the catalyst ranges from about 10,000 to 200,000 hr" 1 .
- the gas streams treated generally contain sufficient oxygen to provide a suitable oxidizing atmosphere for removal of CO and hydrocarbons. However, if sufficient oxygen is not present in the gas stream being treated additional amounts can be added to the process at any point desired.
- CO conversions greater than 90% and propane conversion greater than 50% are achieved at oxidizing temperatures below 500"C in the presence of flue gases containing sulfur compounds by contacting with the invention platinum group metal catalysts.
- Specific Examples The following examples are representative of the invention.
- a control catalyst representative of present commercial operation was prepared and compared with the invention catalysts.
- Example 1 A slurry containing gamma alumina (surface area about 120 m 2 /g) is co-mingled with organic acid and reduced in particle size to less than 10 microns.
- the alumina slurry is applied to a metallic honeycomb substrate, dried and calcined at 400 to 600 * C.
- a solution containing platinum and rhodium is impregnated onto the alumina containing monolith.
- the catalyst is dried, calcination is optional. This catalyst will be designated Catalyst A.
- Catalyst A is used in commercial application to reduce carbon monoxide and hydrocarbons in flue gas from engines combusting fossil fuels.
- Example 2 A slurry containing 85% Zr0 2 and 15% Si0 2 (surface area about 20-40 m/g) is co- mingled and reduced to a particle size of less than 10 microns. Mineral acid and/or base is added to control rheology of the slurry during application onto a metal or ceramic substrate. Following calcination at 500*C in air, platinum and rhodium are supported onto the Zr0_/Si0 2 carrier by impregnation from a solution containing platinum and rhodium. The platinum and rhodium supported on ZrOj/SiO . . was calcined at 400*C for 1 hour. This catalyst is designated Catalyst B.
- Example 3 A commercially available Y-zeolite (surface area about 750 m 2 /g) powder is reduced in size to less than 10 microns.
- the zeolite powder is co-mingled with Si0 2 and slurried in water.
- Organic or mineral acids are used to control rheology during application of the zeolite carrier to a metal or ceramic substrate.
- the coated substrate is dried and fired at 500*C in air.
- a platinum and palladium catalyst is supported onto the Y-zeolite/Si0 2 carrier by impregnation.
- the finished catalyst was calcined at 400 ⁇ C for 1 hour. This catalyst is designated C.
- Example 4 A slurry of titania (Ti0 2 ) (surface area about 30-60 m 2 /g) is prepared and the particle size is reduced to less than lO ⁇ m. Mineral acid and/or base is added to control rheological properties of the slurry during application onto a metal or ceramic substrate. Following calcination at 400°C, platinum and palladium are supported onto the Ti0 2 carrier by impregnation. The platinum and palladium was dried and fired at 400°C. This catalyst is designated Catalyst D.
- Example 5 A catalyst prepared as in Example
- the precious metal impregnation consists of a mixture of platinum and rhodium on titania. This catalyst is designated Catalyst E.
- Catalysts A-F prepared as described in the above examples were evaluated for oxidation activity by contacting with a simulated flue gas.
- Catalyst samples of 2.75 in 3 substrate volume were aged at 370°C in a continuous-flow laboratory reactor using 60 ppm sulfur for up to 1430 hours.
- Catalyst samples were tested in a simulated flue gas consisting of 45 ppm CO, 30 ppm C 3 H,, 40 ppm NO, 10 ppm S0 2 , 4.5% C0 2/ 15% 0 2 , 5% H 2 0 and the balance N 2 .
- a volume of gas measured at 25 ' C and one atmosphere corresponding to 110,000 volumes of catalyst per hour is flowed over the catalyst.
- the carbon monoxide and propane conversion are measured as the temperature of the inlet gas is increased.
- the CO and C 3 H » removal efficiencies are presented in Table I.
- the data demonstrate the superior performance of sulfur-resistant catalyst carriers compared with that of a commercial high surface area alumina for oxidation catalyst operation in a SOx-containing environment.
- Catalyst E (Pt/Rh/titania) shows the advantage of titania over Catalyst A (Pt/Rh/alumina) especially after 1330 hours exposure.
- Hydrocarbon conversion for Catalyst E is 40% and CO conversion is 90% at 400°C oxidation temperature whereas Catalyst A under the same conditions having only 730 hours of operation has lost all hydrocarbon activity and over half of CO conversion activity.
- Catalyst D (Pt/Pd/titania) shows advantage over Catalyst E (Pt/Rh/titania) and Catalyst A (Pt/Rh/alumina) especially after 1330 hours exposure.
- Catalyst D exhibits even greater performance characteristics than Catalyst E since propane conversion is 53% and CO conversion 93%.
- both Catalysts D and E are considerably more active after 1330 hours than Catalyst A after 730 hours exposure.
- Catalyst B (Pt/Rh/Zr-Si)
- Catalyst A (Pt/Rh/alumina)
- Catalyst F (Pt/Rh/zeolite-Si) shows better CO conversion at 400 ⁇ C after 100 hours than Catalyst A and Catalyst C (Pt/Pd/zeolite-Si) shows additional advantage of Pt/Pd over Pt/Rh of Catalyst F under the same conditions.
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Abstract
Improved sulfur tolerant platinum group metal catalysts exhibiting superior performance for the oxidative removal of CO and hydrocarbons from waste gas streams at low temperatures. The catalyst comprises at least one platinum group metal and at least one of silica, titania, zirconia, zeolite, and alpha-alumina.
Description
OXIDATION PROCESS AND CATALYST
This invention relates to an improved process and catalyst for the oxidative removal of CO and hydrocarbons from waste gas streams which can also contain sulfur compounds. In accordance with one aspect, this invention relates to supported platinum group metal catalysts that exhibit superior performance for the oxidative removal of CO and hydrocarbons from waste gas streams by conversion of CO and hydrocarbons to innocuous materials such as flue gases from engines combusting fossil fuels. In a further aspect, this invention relates to a low temperature oxidative process for the removal of CO and hydrocarbons from waste gas streams by contacting with a catalyst comprising a platinum group metal and at least one sulfur tc rant carrier.
Background of the Invention A number of catalysts have been developed and/or used in an effort to oxidatively remove CO and hydrocarbons from waste gas streams, especially sulfur- containing waste gas streams. Many of the known catalyst systems have met with failure and/or poor performance when placed in commercial operations. As an example of the above problem, a known oxidation catalyst consisting of
platinum-group metals on a high surface area alumina carrier deactivates rapidly in sulfur-containing flue gases at temperatures below about 460*C. The deactivation is due to alumina sulfate formation and subsequent loss of catalyst carrier surface area. Therefore, oxidation catalysts containing high surface area alumina cannot be used commercially for the treatment of sulfur- containing flue gases below about 460βC. Ideal catalysts should be stable and durable in the presence of SO, in the flue gas. The present invention avoids the problems of the prior art by providing improved oxidation catalyst compositions having good activity and durability for the treatment of sulfur-containing flue gas streams. The present invention provides catalyst compositions comprising carriers which interact favorably with platinum-group metals and which are resistant to reaction with oxides of sulfur and exhibit superior performance for low temperature oxidative removal of CO and hydrocarbons from waste gas streams.
Objects of the Invention Accordingly, an object of the invention is to provide improved platinum- group metal catalysts.
Another object of this invention is to provide a commercially effective process and catalyst for the oxidative removal of CO and hydrocarbons from sulfur-containing waste gas streams.
A further object of the invention is to provide platinum-group metal catalysts having good activity, durability, and long catalyst life in the treatment of sulfur-containing waste gas streams.
A still further object is to provide a catalyst and process effective for the oxidative removal of CO and hydrocarbons from waste gas streams at low temperatures.
Other objects, aspects, as well as the several advantages of the invention will be apparent to those skilled in this art upon reading the specification and appended claims.
Summary of the I mention According to the invention, a catalyst and process are provided for the oxidative removal of CO and hydrocarbons from waste gas streams by contacting same at relatively low temperatures with a catalytically effective amount of an oxidation catalyst comprising catalyst carriers which interact favorably with platinum group metals and are resistant to
reaction with oxides of sulfur that can be present in such streams.
In accordance with one embodiment of the invention, a process is provided for the oxidative removal of CO and hydrocarbons from either S0x-containing or SOx-free waste streams which comprises contacting said waste gas stream in an oxidizing atmosphere under oxidizing conditions at a temperature below about
500°C in the presence of a metal catalyst the active component being at least one platinum group metal supported on a sulfur-resistant carrier. In accordance with another embodiment of the invention, an effective oxidation catalyst is provided comprising at least one platinum group metal supported on at least one of silica, zirconia, titania, zeolite, and alpha alumina or combinations thereof.
The present catalysts maintain their oxidation activity in the presence of sulfur-containing flue gases and, therefore, these catalysts can be effectively utilized commercially for oxidation of gas streams that are either S0x-containing or S0x-free.
Detailed Description As disclosed above, the invention comprises a platinum group metal catalyst supported on carriers that are resistant
to reaction with oxides of sulfur and to a process for the oxidation of CO and hydrocarbons in gas streams which can contain sulfur compounds in the presence of the invention platinum group metal catalyst.
The catalyst of the invention comprises at least one platinum group metal and at least one of silica, zirconia, titania, zeolite, and low surface area alpha-phase alumina in any combination.
Representative examples of platinum group metals that can be used include platinum, palladium, rhodium, ruthenium, osmium and iridium and mixtures thereof. Presently preferred are one or more of platinum, palladium and rhodium.
The amount of platinum group metal present in the catalyst composition is an oxidative catalytically effective amount. Generally, the total amount of platinum metal present ranges from about 0.005 to about 2 weight percent of the catalyst composition. A mixture of platinum group metals can be used in any ratio of one platinum group metal to another.
It is often desirable for economic reasons due to the cost of one of the platinum group metals to use two or more metals. As demonstrated by the specific working examples, mixtures of the platinum groups metals are effective oxidation
catalysts. It should be noted further from the specific working examples that the instant catalysts exhibit improved catalyst performance in terms of stability over prior-art catalyst formulations.
The carriers that can be used that interact favorably with platinum group metals and which are resistant to reaction with oxides of sulfur include one or more of silica, zirconia, titania, zeolite, and low surface area alpha-phase alumina. Other than the alumina," the other carriers are high surface are materials. The surface area of these carriers generally is in the range of about 20 m2/g to about 1000 m2/g as measured by Brunauer, Emmett and Teller surface measurement technique. In one embodiment of the invention a ceramic or metallic monolith is used as a support material. The metal monolith consists of alternate layers of flat and corrugated foil strips stacked to form a honeycomb structure. The foil is typically 0.002 inches thick and can be any of several ferritic stainless steels or other alloys. Cell densities of 100, 200, and 400 cell/sq. in. are obtained by varying the spacing and depth of the corrugations. The carrier materials are well known in the art and can be prepared by methods known in the art.
One method that can be used for the preparation of the carriers is to mix the desired oxide with water to form the inorganic oxide material. The morphological and rheological properties of the oxide-water mixture can be adjusted by adding organic or inorganic acids or base. The oxide-water mixture can be applied to metal or ceramic monoliths, dried and then fired at 250 to 650*C. The firing step is optional. A catalytically active material from the precious metal groups is deposited by impregnation, for example, on the carrier material. The catalyst composition after deposition of the platinum metal on the carrier can be calcined at a temperature of about 300- 500°C. This calcination is also optional. The catalysts of the invention can be formed into any shape desired and used in fixed bed, moving b i, fluidized bed or other known types of contacting with the stream to be oxidatively treated. The invention comprises the oxidative removal of CO and hydrocarbons from either S0_-containing or S0x-free gas streams in an oxidizing atmosphere under effective oxidation conditions of temperature, pressure, contact time and space velocity in the presence of the platinum group metal catalyst defined above.
The invention is applicable to the treatment of any gas stream containing CO and hydrocarbons, especially lower hydrocarbons, such as ethane, propane, and the like. These streams include waste gases exhausted from engines combusting fossil fuels which may or may not contain sulfur compounds.
In actual operation of an oxidation system, the catalyst is installed at a place in the gas flow path at which the temperature is below about 500*C, usually about 150 to about 500*C. The gas hourly space velocity (GHSV) of the gas stream in contact with the catalyst ranges from about 10,000 to 200,000 hr"1. The gas streams treated generally contain sufficient oxygen to provide a suitable oxidizing atmosphere for removal of CO and hydrocarbons. However, if sufficient oxygen is not present in the gas stream being treated additional amounts can be added to the process at any point desired. As demonstrated by the specific working examples that follow, CO conversions greater than 90% and propane conversion greater than 50% are achieved at oxidizing temperatures below 500"C in the presence of flue gases containing sulfur compounds by contacting with the invention platinum group metal catalysts.
Specific Examples The following examples are representative of the invention. A control catalyst representative of present commercial operation was prepared and compared with the invention catalysts.
Example 1 A slurry containing gamma alumina (surface area about 120 m2/g) is co-mingled with organic acid and reduced in particle size to less than 10 microns. The alumina slurry is applied to a metallic honeycomb substrate, dried and calcined at 400 to 600*C. A solution containing platinum and rhodium is impregnated onto the alumina containing monolith. The catalyst is dried, calcination is optional. This catalyst will be designated Catalyst A. Catalyst A is used in commercial application to reduce carbon monoxide and hydrocarbons in flue gas from engines combusting fossil fuels.
Example 2 A slurry containing 85% Zr02 and 15% Si02 (surface area about 20-40 m/g) is co- mingled and reduced to a particle size of less than 10 microns. Mineral acid and/or base is added to control rheology of the slurry during application onto a metal or ceramic substrate. Following calcination at 500*C in air, platinum and rhodium are supported onto the Zr0_/Si02 carrier by impregnation from a solution containing platinum and rhodium. The platinum and rhodium supported on ZrOj/SiO.. was calcined at 400*C for 1 hour. This catalyst is designated Catalyst B.
Example 3 A commercially available Y-zeolite (surface area about 750 m2/g) powder is reduced in size to less than 10 microns. The zeolite powder is co-mingled with Si02 and slurried in water. Organic or mineral acids are used to control rheology during application of the zeolite carrier to a metal or ceramic substrate. The coated substrate is dried and fired at 500*C in air. A platinum and palladium catalyst is supported onto the Y-zeolite/Si02 carrier by impregnation. The finished catalyst was calcined at 400βC for 1 hour. This catalyst is designated C.
Example 4 A slurry of titania (Ti02) (surface area about 30-60 m2/g) is prepared and the particle size is reduced to less than lOμm. Mineral acid and/or base is added to control rheological properties of the slurry during application onto a metal or ceramic substrate. Following calcination at 400°C, platinum and palladium are supported onto the Ti02 carrier by impregnation. The platinum and palladium was dried and fired at 400°C. This catalyst is designated Catalyst D.
Example 5 A catalyst prepared as in Example
4, but in this example the precious metal impregnation consists of a mixture of platinum and rhodium on titania. This catalyst is designated Catalyst E.
Example 6
A catalyst prepared as in Example 3, but in this example the precious metal impregnation consists of a mixture of platinum and rhodium on Y-zeolite. This catalyst is designated Catalyst F.
The catalysts designated Catalysts A-F prepared as described in the above examples were evaluated for oxidation activity by contacting with a simulated flue gas.
Catalyst samples of 2.75 in3 substrate volume were aged at 370°C in a continuous-flow laboratory reactor using 60 ppm sulfur for up to 1430 hours. Catalyst samples were tested in a simulated flue gas consisting of 45 ppm CO, 30 ppm C3H,, 40 ppm NO, 10 ppm S02, 4.5% C02/ 15% 02, 5% H20 and the balance N2. A volume of gas measured at 25 ' C and one atmosphere corresponding to 110,000 volumes of catalyst per hour is flowed over the catalyst. The carbon monoxide and propane conversion are measured as the temperature of the inlet gas is increased. The CO and C3H» removal efficiencies are presented in Table I. The data demonstrate the superior performance of sulfur-resistant catalyst carriers compared with that of a commercial high surface area alumina for oxidation catalyst operation in a SOx-containing environment.
The results of these evaluations are set forth in the following Table.
Table I Propane and carbon monoxide conversions for oxidation Catalysts A-F.
Hours Exposure to Temperature Conversion % Catalyst Flue σas •C Propane Monoxide
A fresh 300 15 88 350 45 97 400 68 99
A 100 300 02 51 350 07 65 400 25 70
A 200 300 02 56 350 06 71 400 14 79
A 730 300 00 20 350 00 33 400 00 41
A 1430 300 00 31 350 00 45 400 00 41
B fresh 300 53 94 400 84 99
100 300 57 95 400 73 98
C fresh 300 13 87 400 42 94
100 300 25 98 400 48 99
D fresh 300 23 96 350 48 98 400 67 99
100 300 26 96 350 50 98 400 68 99
630
1330
fresh
100
630
1330
fresh
The results in Table 1 show clearly that Catalyst A deteriorates with time of exposure to flue gas and has lost all hydrocarbon conversion after 730 hours and over half of carbon monoxide conversion.
Catalyst E (Pt/Rh/titania) shows the advantage of titania over Catalyst A (Pt/Rh/alumina) especially after 1330 hours exposure. Hydrocarbon conversion for Catalyst E is 40% and CO conversion is 90% at 400°C oxidation temperature whereas Catalyst A under the same conditions having only 730 hours of operation has
lost all hydrocarbon activity and over half of CO conversion activity.
Catalyst D (Pt/Pd/titania) shows advantage over Catalyst E (Pt/Rh/titania) and Catalyst A (Pt/Rh/alumina) especially after 1330 hours exposure. Catalyst D exhibits even greater performance characteristics than Catalyst E since propane conversion is 53% and CO conversion 93%. However, both Catalysts D and E are considerably more active after 1330 hours than Catalyst A after 730 hours exposure.
Comparing Catalyst B (Pt/Rh/Zr-Si) with Catalyst A (Pt/Rh/alumina) , it will be observed at 100 hrs and 400βC contact temperature that propane conversion is 73% and CO conversion is 98% for catalyst B whereas the conversions are 25% and 70%, respectively, for Catalyst A.
Catalyst F (Pt/Rh/zeolite-Si) shows better CO conversion at 400βC after 100 hours than Catalyst A and Catalyst C (Pt/Pd/zeolite-Si) shows additional advantage of Pt/Pd over Pt/Rh of Catalyst F under the same conditions.
Claims
1. A process for the oxidative removal of CO and hydrocarbons from SOx-containing and S0x-free waste gases which comprises contacting said waste gas in an oxidizing atmosphere at a relatively low temperature below about 500βC in the presence of an effective amount of a catalyst comprising at least one platinum group metal supported on at least one of silica, zirconia, titania, zeolite and alpha alumina.
2. A process according to claim 1 wherein said contacting is effected at a temperature ranging from about 150 to about 500βC.
3. A process according to claim 1 wherein said contacting is effective at a gas hourly space velocity (GHSV-STP) of about 10,000 to about 200,000 hr"'.
4. A process according to claim 1 wherein said catalyst comprises at least one of platinum, palladium and rhodium supported on titania.
5. A process according to claim 4 wherein the total amount of platinum group metal in the catalyst ranges from about 0.005 to about 2% by weight of the catalyst composition in any ratio of one platinum group metal to another.
6. A process according to claim 1 wherein said waste gas is flue gas from engines combusting fossil fuels.
7. A process according to claim 1 wherein said waste gas is a SO -containing gas.
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
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US27001188A | 1988-11-14 | 1988-11-14 | |
US270,011 | 1988-11-14 |
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WO1990005579A1 true WO1990005579A1 (en) | 1990-05-31 |
Family
ID=23029527
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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PCT/US1989/004955 WO1990005579A1 (en) | 1988-11-14 | 1989-11-14 | Oxidation process and catalyst |
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AU (1) | AU4527189A (en) |
WO (1) | WO1990005579A1 (en) |
Cited By (6)
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EP0494591A1 (en) * | 1991-01-07 | 1992-07-15 | Nippon Shokubai Co., Ltd. | Diesel engine exhaust gas-purifying catalyst |
WO1992017268A1 (en) * | 1991-04-08 | 1992-10-15 | Engelhard Corporation | Oxidation catalyst resistant to sulfation |
EP0612689A1 (en) * | 1993-02-22 | 1994-08-31 | Leuna-Werke Gmbh | Process and catalyst for purifying carbon dioxide |
US6342192B1 (en) | 1992-04-10 | 2002-01-29 | Johnson Matthey Plc | Device for cleaning exhaust fumes |
FR2887469A1 (en) * | 2005-06-27 | 2006-12-29 | Rhodia Chimie Sa | GAS TREATMENT PROCESS FOR CATALYTIC OXIDATION OF CARBON MONOXIDE AND HYDROCARBONS USING A METAL-BASED ZIRCONY-BASED COMPOSITION COMPRISING SILICA |
CN103945920A (en) * | 2011-11-17 | 2014-07-23 | 庄信万丰股份有限公司 | Supported noble metal catalyst for treating exhaust gas |
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US4197217A (en) * | 1977-08-05 | 1980-04-08 | Johnson, Matthey & Co., Limited | Intermetallic catalyst |
US4212854A (en) * | 1977-03-18 | 1980-07-15 | Matsushita Electric Industrial Co., Ltd. | Method for purification of air containing carbon monoxide |
US4440874A (en) * | 1982-04-14 | 1984-04-03 | Engelhard Corporation | Catalyst composition and method for its manufacture |
US4624940A (en) * | 1985-04-12 | 1986-11-25 | Engelhard Corporation | High temperature catalyst compositions for internal combustion engine |
US4727052A (en) * | 1986-06-27 | 1988-02-23 | Engelhard Corporation | Catalyst compositions and methods of making the same |
-
1989
- 1989-11-14 WO PCT/US1989/004955 patent/WO1990005579A1/en unknown
- 1989-11-14 AU AU45271/89A patent/AU4527189A/en not_active Abandoned
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US4157316A (en) * | 1975-08-27 | 1979-06-05 | Engelhard Minerals & Chemicals Corporation | Polyfunctional catalysts |
US4212854A (en) * | 1977-03-18 | 1980-07-15 | Matsushita Electric Industrial Co., Ltd. | Method for purification of air containing carbon monoxide |
US4197217A (en) * | 1977-08-05 | 1980-04-08 | Johnson, Matthey & Co., Limited | Intermetallic catalyst |
US4440874A (en) * | 1982-04-14 | 1984-04-03 | Engelhard Corporation | Catalyst composition and method for its manufacture |
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Cited By (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0494591A1 (en) * | 1991-01-07 | 1992-07-15 | Nippon Shokubai Co., Ltd. | Diesel engine exhaust gas-purifying catalyst |
US5208203A (en) * | 1991-01-07 | 1993-05-04 | Nippon Shokubai Co., Ltd. | Diesel engine exhaust gas-purifying catalyst |
WO1992017268A1 (en) * | 1991-04-08 | 1992-10-15 | Engelhard Corporation | Oxidation catalyst resistant to sulfation |
US6342192B1 (en) | 1992-04-10 | 2002-01-29 | Johnson Matthey Plc | Device for cleaning exhaust fumes |
EP0612689A1 (en) * | 1993-02-22 | 1994-08-31 | Leuna-Werke Gmbh | Process and catalyst for purifying carbon dioxide |
WO2007000514A2 (en) * | 2005-06-27 | 2007-01-04 | Rhodia Chimie | Gas processing method for catalytically oxidising carbon monoxide and hydrocarbons using a compound based on a metal and a silica-containing zirconia |
FR2887469A1 (en) * | 2005-06-27 | 2006-12-29 | Rhodia Chimie Sa | GAS TREATMENT PROCESS FOR CATALYTIC OXIDATION OF CARBON MONOXIDE AND HYDROCARBONS USING A METAL-BASED ZIRCONY-BASED COMPOSITION COMPRISING SILICA |
WO2007000514A3 (en) * | 2005-06-27 | 2007-02-22 | Rhodia Chimie Sa | Gas processing method for catalytically oxidising carbon monoxide and hydrocarbons using a compound based on a metal and a silica-containing zirconia |
JP2008546532A (en) * | 2005-06-27 | 2008-12-25 | ロディア・シミ | Gas treatment method for catalytic oxidation of carbon monoxide and hydrocarbons utilizing metal and silica containing zirconia based compositions |
KR100996042B1 (en) * | 2005-06-27 | 2010-11-22 | 로디아 쉬미 | Gas treatment method for catalytic oxidation of carbon monoxide using metal and silica containing zirconia based compositions |
US7892507B2 (en) | 2005-06-27 | 2011-02-22 | Rhodia Chimie | Gas processing for catalytically oxidizing carbon monoxide and hydrocarbons in the presence of a metal/silica-containing zirconia catalyst |
CN103945920A (en) * | 2011-11-17 | 2014-07-23 | 庄信万丰股份有限公司 | Supported noble metal catalyst for treating exhaust gas |
CN103945920B (en) * | 2011-11-17 | 2017-10-31 | 庄信万丰股份有限公司 | Noble metal catalyst for handling waste gas |
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