EP2175968A1 - VERFAHREN ZUR ENTFERNUNG VON CO, H2 UND/ODER CH4 AUS DEM ANODENABGAS EINER BRENNSTOFFZELLE MIT MISCHOXIDKATALYSATOREN UMFASSEND Cu, Mn UND GEGEBENENFALLS MINDESTENS EIN SELTENERDMETALL - Google Patents
VERFAHREN ZUR ENTFERNUNG VON CO, H2 UND/ODER CH4 AUS DEM ANODENABGAS EINER BRENNSTOFFZELLE MIT MISCHOXIDKATALYSATOREN UMFASSEND Cu, Mn UND GEGEBENENFALLS MINDESTENS EIN SELTENERDMETALLInfo
- Publication number
- EP2175968A1 EP2175968A1 EP08786651A EP08786651A EP2175968A1 EP 2175968 A1 EP2175968 A1 EP 2175968A1 EP 08786651 A EP08786651 A EP 08786651A EP 08786651 A EP08786651 A EP 08786651A EP 2175968 A1 EP2175968 A1 EP 2175968A1
- Authority
- EP
- European Patent Office
- Prior art keywords
- fuel cell
- rare earth
- earth metal
- optionally
- catalysts
- 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.)
- Withdrawn
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Classifications
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- 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
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/864—Removing carbon monoxide or hydrocarbons
-
- 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
-
- 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
- B01J23/70—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
- B01J23/76—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
- B01J23/84—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
- B01J23/889—Manganese, technetium or rhenium
- B01J23/8892—Manganese
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M8/00—Fuel cells; Manufacture thereof
- H01M8/06—Combination of fuel cells with means for production of reactants or for treatment of residues
- H01M8/0662—Treatment of gaseous reactants or gaseous residues, e.g. cleaning
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M8/00—Fuel cells; Manufacture thereof
- H01M8/06—Combination of fuel cells with means for production of reactants or for treatment of residues
- H01M8/0662—Treatment of gaseous reactants or gaseous residues, e.g. cleaning
- H01M8/0668—Removal of carbon monoxide or carbon dioxide
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/206—Rare earth metals
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/2073—Manganese
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20761—Copper
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0208—Other waste gases from fuel cells
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M8/00—Fuel cells; Manufacture thereof
- H01M8/10—Fuel cells with solid electrolytes
- H01M8/12—Fuel cells with solid electrolytes operating at high temperature, e.g. with stabilised ZrO2 electrolyte
- H01M2008/1293—Fuel cells with solid oxide electrolytes
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- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M8/00—Fuel cells; Manufacture thereof
- H01M8/14—Fuel cells with fused electrolytes
- H01M2008/147—Fuel cells with molten carbonates
-
- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M2250/00—Fuel cells for particular applications; Specific features of fuel cell system
- H01M2250/40—Combination of fuel cells with other energy production systems
- H01M2250/405—Cogeneration of heat or hot water
-
- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M8/00—Fuel cells; Manufacture thereof
- H01M8/04—Auxiliary arrangements, e.g. for control of pressure or for circulation of fluids
- H01M8/04082—Arrangements for control of reactant parameters, e.g. pressure or concentration
- H01M8/04089—Arrangements for control of reactant parameters, e.g. pressure or concentration of gaseous reactants
- H01M8/04097—Arrangements for control of reactant parameters, e.g. pressure or concentration of gaseous reactants with recycling of the reactants
-
- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M8/00—Fuel cells; Manufacture thereof
- H01M8/06—Combination of fuel cells with means for production of reactants or for treatment of residues
- H01M8/0606—Combination of fuel cells with means for production of reactants or for treatment of residues with means for production of gaseous reactants
- H01M8/0612—Combination of fuel cells with means for production of reactants or for treatment of residues with means for production of gaseous reactants from carbon-containing material
- H01M8/0618—Reforming processes, e.g. autothermal, partial oxidation or steam reforming
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02B—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO BUILDINGS, e.g. HOUSING, HOUSE APPLIANCES OR RELATED END-USER APPLICATIONS
- Y02B90/00—Enabling technologies or technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02B90/10—Applications of fuel cells in buildings
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/30—Hydrogen technology
- Y02E60/50—Fuel cells
Definitions
- the present invention relates to fuel cell assemblies and systems, comprising a catalytic exhaust gas burner for combustion of a mixture of anode residual gas, air and / or other admixed gases (eg cathode exhaust gas), wherein a mixed oxide catalyst comprising Cu and Mn is used as the catalyst in the exhaust gas burner, and a method and a use for this.
- a catalytic exhaust gas burner for combustion of a mixture of anode residual gas, air and / or other admixed gases (eg cathode exhaust gas)
- a mixed oxide catalyst comprising Cu and Mn is used as the catalyst in the exhaust gas burner
- Fuel cells offer the possibility of generating electricity from the controlled combustion of hydrogen at high efficiency. At present, however, there is no infrastructure for the future energy source hydrogen. Therefore, there is a need to extract hydrogen from the well-available energy sources natural gas, gasoline, diesel or other hydrocarbons such as biogas, methanol, etc.
- Methane - the predominant component of natural gas - can be used to generate hydrogen, for example by steam reforming.
- the resulting gas contains traces of unreacted methane and water, essentially hydrogen, carbon dioxide and carbon monoxide.
- This gas can be used as fuel gas for a fuel cell. In order to shift the equilibrium in the steam reforming on the side of the hydrogen, this is carried out at temperatures of about 500 0 C - 1000 0 C, wherein for a constant composition of the fuel gas, this temperature range should be maintained as accurately as possible.
- sulfur compounds present in the fuel gas are removed prior to delivery to the fuel cell because most of the fuel cell catalysts used are susceptible to sulfur.
- a fuel cell arrangement in which the fuel gas produced from methane and water can be used to generate energy is described for example in DE 197 43 075 A1.
- Such an arrangement includes a number of fuel cells disposed in a fuel cell stack within a closed protective housing.
- fuel gas Via an anode gas inlet fuel gas is supplied to the fuel cell, which consists essentially of hydrogen, carbon dioxide, carbon monoxide and residues of methane and water.
- the Fuel gas is generated either in an upstream external reformer or in an internal reformer of methane and water. Internal reforming reactions are often used in high-temperature fuel cells such.
- MCFC Molten Carbonate Fuel Cell
- SOFC Solid Oxide Fuel Cell
- the anode exhaust gas contains, in addition to the reaction products carbon dioxide and water, portions of hydrogen, carbon monoxide and methane gas, depending on the operating state and operating time.
- the anode exhaust gas is first mixed with air and then fed to a catalytic exhaust gas burner, in which the remaining methane and traces of hydrogen burned to water and carbon dioxide become.
- a catalytic exhaust gas burner in which the remaining methane and traces of hydrogen burned to water and carbon dioxide become.
- B. cathode exhaust gas are admixed.
- the released thermal energy can be used in various ways.
- precious metals such as platinum and / or palladium
- This catalytic combustion has the advantage that it is very uniform and without temperature peaks.
- the combustion of palladium catalysts proceeds at temperatures ranging from about 450 to 550 0 C.
- the equilibrium shifts Pd / PdO favor of palladium metal whereby the activity of the catalyst decreases (see Catalysis Today 47 (1999) 29-44).
- a loss of activity is also observed by the occurrence of sintering or the caking of the catalyst particles.
- noble metal catalysts have the disadvantage of very high raw material prices.
- EP 0 270 203 A1 discloses heat-stable catalysts for the catalytic combustion of, for example, methane. These are based on alkaline earth hexaaluminates which contain fractions of Mn, Co, Fe, Ni, Cu or Cr. These catalysts are characterized by a high activity and resistance even at temperatures of more than 1200 0 C. However, the activity of the catalyst is relatively low at lower temperatures. In order to be able to provide sufficient catalytic activity even at lower temperatures, small amounts of platinum metals are added, for example Pt, Ru, Rh or Pd.
- the ideal temperature range for operating a high temperature fuel cell is in the range of about 400 to 1000 ° C.
- the heat generated during anode-off-gas combustion can be used in various applications, for example, to evaporate water for steam reforming, providing heat energy for endothermic steam reforming , Heat utilization in cogeneration applications or the like.
- the completely oxidized anode exhaust gas which in particular no longer contains hydrogen gas, can be fed to the cathode as cathode gas after it leaves the burner. This is described for example in DE 197 43 075 A1
- a low cost, active and long term stable fuel cell array catalyst including a catalytic exhaust gas combustor for combusting a mixture of residual anode gas, air, and optionally other gases, such as cathode gases, for the methane, CO, and H 2 oxidation in the exhaust gas combustor Temperatures of 400 to 1 100 0 C is stable and active.
- oxidation catalysts comprising mixed oxides of copper, manganese and optionally one or more rare earth metal (s) are particularly suitable for this purpose.
- these catalysts enable domestic heat recovery to produce CO 2 for a recycle system of the molten carbonate fuel cell (MCFC) fuel cell type and reduce environmental emissions.
- MCFC molten carbonate fuel cell
- the present invention therefore provides a process for removing CO, H 2 and / or CH 4 from the anode exhaust gas of a fuel cell with mixed oxide catalysts comprising Cu, Mn and optionally at least one rare earth metal.
- the present invention furthermore relates to the use of mixed oxide catalysts comprising Cu, Mn and optionally at least one Rare earth metal for removing CO, H 2 and / or CH 4 from the anode exhaust gas of a fuel cell.
- Suitable catalysts are described for example in EP 1 197 259, the disclosure of which is hereby incorporated by reference into the present invention.
- Such catalysts include mixed oxides of Cu, Mn, and rare earth metal (s) in which the metals may assume multiple valence states, which may represent a wt%
- the rare earth metals in the lowest valence state 60% as MnO, 35-40% as CuO and 2-15% as La 2 O 3 and / or as oxides of the rare earth metals in the lowest valence state.
- the rare earth metals in the lowest valence state 60% as MnO, 35-40% as CuO and 2-15% as La 2 O 3 and / or as oxides of the rare earth metals in the lowest valence state.
- Composition 50-60% MnO, 35-40% CuO, 10-12% La 2 O 3 .
- the individual metals can also assume different oxidation states than those mentioned above.
- manganese may also be present as MnO 2 .
- compositions are generally possible, the percentages being percentages by weight, based on the total mass of Mn, Cu and optionally rare earth metals: Mn 80-20%, Cu 20-60%, rare earth metals 0-20%, preferably Mn 75-30 %, Cu 20 - 55%, rare earth metals 5 - 15%.
- the mass ratio of copper to manganese (calculated as mass Cu to mass Mn) on the finished catalyst may be, for example, 0.4 to 0.9, preferably 0.5 to 0.75.
- rare earth metals are lanthanum (La), cerium (Ce), praseodymium (Pr), neodymium (Nd), promethium (Pm), samarium (Sm), europium (Eu), gadolinium (Gd), terbium (Tb), dysprosium ( Dy), Holmium (Ho), Erbium (Er), Thulium (Tm), Ytterbium (Yb), Lutetium (Lu). Preference is given to La and Ce.
- the oxides are supported, for example, on porous inorganic supports such as alumina, silica, silica-alumina, titania or magnesia.
- the oxides are used in an amount of generally 5 to 50% by weight, preferably 5 to 30 wt .-%, based on the total mass of the catalyst and the oxides carried.
- the rare earth metal may already be present in the carrier.
- the predominant role of the rare earth metal is to stabilize the BET surface area of the porous inorganic support.
- An example known to a person skilled in the art is lanthanum-stabilized aluminum oxide.
- the catalyst may be prepared by first impregnating the support with a solution of a salt of lanthanum or cerium or other rare earth metal, drying it and then calcining it at a temperature of about 600 ° C. If the carrier already contains a rare earth metal due to the production, this step may be unnecessary. Examples are lanthanum stabilized aluminas.
- the support is then impregnated with a solution of a copper and manganese salt, then dried at 120 to 200 0 C and calcined at up to 450 0 C.
- Any soluble salt of the metals can be used.
- salts are nitrates, formates and acetates.
- Lanthanum is preferably used as lanthanum nitrate La (NC> 3) 3
- copper and manganese are preferably used as nitrates, namely Cu (NO 3 ) 2 and Mn (NO 3 ) 3 .
- the preferred impregnation method is dry impregnation, using an amount of solution that is equal to or less than the pore volume of the support.
- the initial temperature of the catalyst it may be necessary for the initial temperature of the catalyst to be less than 250 ° C. That is, the catalyst should be able to convert H 2 and CO at a temperature below about 250 ° C. to achieve an exothermic effect needed to initiate the methane combustion reaction. Since the H 2 and CO conversion activity of the catalysts used in this invention is low, doping with small amounts of noble metals may be advantageous. Suitable for this for example platinum (Pt) and / or palladium (Pd). For example, the catalyst may be doped with 0.1 wt% Pt.
- hopkalite catalysts can be used in the context of the present invention. These are mixed catalysts consisting mainly of manganese dioxide and copper (II) oxide. In addition, you can contain other metal oxides, such as cobalt oxides and silver (l) oxide.
- the present invention further relates to a fuel cell assembly comprising an exhaust gas burner, wherein the exhaust gas burner comprises mixed oxide catalysts comprising Cu, Mn and optionally at least one rare earth metal.
- the invention relates to molten carbonate fuel cell (MCFC) or solid oxide fuel cell (SOFC) type fuel cells in which the exhaust gas combustor comprises mixed oxide catalysts comprising Cu, Mn and optionally at least one rare earth metal.
- the exhaust gas burner of the fuel cell assembly according to the invention preferably comprises as oxidation oxide catalysts oxidation catalysts comprising mixed oxides of copper, manganese and one or more rare earth metal (s), which metals can assume multiple valence states containing a weight percentage composition in terms of CuO, MnO and rare earth metal oxides in which the rare earth metal has the lowest valence, from 35 to 40%, 50 to 60% and 2 to 15%, respectively.
- oxidation oxide catalysts comprising mixed oxides of copper, manganese and one or more rare earth metal (s), which metals can assume multiple valence states containing a weight percentage composition in terms of CuO, MnO and rare earth metal oxides in which the rare earth metal has the lowest valence, from 35 to 40%, 50 to 60% and 2 to 15%, respectively.
- the exhaust gas burner may in principle comprise mixed oxides of all the above-mentioned compositions, in particular 20-60% Cu, 80-20% Mn and 0-20% rare earth metal (% by weight, based on the total weight of the stated metals).
- Fig. 1 shows a steady state test in which the temperature of the catalyst bed is plotted over time. In this case, no reaction gas was passed over the catalyst bed.
- Figure 2 shows the absolute CH 4 concentration as a function of time-on-stream (TOS) for various Pt / Pd catalyst types on 600 cpsi metal monoliths.
- TOS time-on-stream
- Fig. 3 shows the absolute CH 4 concentration as a function of TOS for Cu / La / Mn catalysts.
- Figure 5 shows CO conversion as a function of catalyst inflow temperature for fresh and aged Cu / La / Mn catalysts.
- Figure 6 shows H 2 conversion as a function of catalyst inflow temperature for fresh and aged Cu / La / Mn catalysts.
- FIG. 7 shows the CO, H 2 shows - and CH 4 -conversion as a function of Katalysatoreinströmtemperatur for fresh Cu / La / Mn catalysts, which are doped with 0.1% Pt.
- Fig. 8 shows a schematic representation of the test setup.
- test gas mixture is used that is similar to an anode exhaust after mixing with air:
- the catalytic activity for the anode exhaust gas oxidation of various catalysts is tested in a conventional tubular reactor at atmospheric pressure.
- the tube reactor has an inside diameter of about 19.05 mm and a heated length of 600 mm and consists of a Ni-based austenitic stainless steel. Above and below the catalyst the gas inlet and gas outlet temperatures are measured during the test.
- Feedstock and product gas are analyzed online with an IR analyzer: ABB; continuous gas analyzer AO2000; Series: Infrared Analyzer module Uras 14 for CO, CO 2 , H 2 , CH 4 ; OxygenAnalyzer module Magnos 106 for O 2 .
- This gas analyzer was calibrated with appropriate certified test gases prior to testing.
- a Pt / Pd catalyst is used for the comparative experiments.
- the 400 or 600 cpsi metal honeycombs are coated with washcoat according to US 4,900,712, Example 3 (solids content 40-50%) (target load 90 g / l).
- the coated honeycomb are dried in a drying oven at 120 0 C for two hours and calcined at 550 0 C for three hours (ramp 2 ° C / min).
- the honeycombs are left in the dip solution overnight (at least 12 hours) to ensure that all Pt is taken up.
- the honeycombs are then blown out and dried at 120 0 C for two hours in a drying oven and then calcined at 550 0 C for three hours (ramp 2 ° C / min).
- the dried honeycombs are immersed in the solution for 20 seconds, blown out to the mass of water uptake and weighed. They are then dried at 120 0 C for two hours in a drying oven and then calcined at 550 0 C for three hours (ramp 2 ° C / min).
- the Cu / Mn / La catalyst to be used in the context of the present invention is first prepared according to EP 1 197 259 A1, Example 1. Afterwards this can be impregnated with Pt.
- the obtained Triholes coated with Cu / La / Mn (grains with a three-lobed cross-section with mutual holes in the same distance in the lobes, the holes were parallel to the axis of the lobes) into granules with 1 - 2 mm diameter crushed. 20 g of the granules are doped with 0.1% Pt.
- thermostability of the catalysts to be used in the invention was surprisingly high and the activity of methane conversion at higher temperatures was good.
- Methane conversion of fresh and aged catalyst is good compared to aged noble metal catalysts.
- the methane conversion is very stable even after hydrothermal aging and hydrothermal potassium aging.
- the fresh catalysts have a methane conversion rate of 50% at 490 0 C and a conversion of> 95% at about 650 0 C inflow temperature.
- Both aged samples show little deactivation in methane oxidation activity but are still very active. In the temperature range above 600 0 C inflow temperature, the deactivation is negligible. The additional influence of potassium on the catalytic activity over 65 hours TOS is negligible.
- the catalysts to be used in the present invention because of their excellent cost / benefit ratio and their good hydrothermal stability compared to noble metal catalysts are ideally suited for the oxidative treatment of anode exhaust gases in fuel cells.
- H 2 activity decreases after hydrothermal aging.
- the potassium-aged catalyst performs better than the normal-aged catalysts in CO and H 2 conversion. Since a permanent inflow temperature below about 250 0 C is necessary, a catalyst is doped with 0.1 wt .-% Pt. The whole
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Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE102007037796A DE102007037796A1 (de) | 2007-08-10 | 2007-08-10 | Verfahren zur Entfernung von CO, H2 und/oder CH4 aus dem Anodenabgas einer Brennstoffzelle mit Mischoxidkatalysatoren umfassend Cu, Mn und gegebenenfalls mindestens ein Seltenerdmetall |
PCT/EP2008/060024 WO2009021850A1 (de) | 2007-08-10 | 2008-07-30 | VERFAHREN ZUR ENTFERNUNG VON CO, H2 UND/ODER CH4 AUS DEM ANODENABGAS EINER BRENNSTOFFZELLE MIT MISCHOXIDKATALYSATOREN UMFASSEND Cu, Mn UND GEGEBENENFALLS MINDESTENS EIN SELTENERDMETALL |
Publications (1)
Publication Number | Publication Date |
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EP2175968A1 true EP2175968A1 (de) | 2010-04-21 |
Family
ID=39791458
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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EP08786651A Withdrawn EP2175968A1 (de) | 2007-08-10 | 2008-07-30 | VERFAHREN ZUR ENTFERNUNG VON CO, H2 UND/ODER CH4 AUS DEM ANODENABGAS EINER BRENNSTOFFZELLE MIT MISCHOXIDKATALYSATOREN UMFASSEND Cu, Mn UND GEGEBENENFALLS MINDESTENS EIN SELTENERDMETALL |
Country Status (8)
Country | Link |
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US (1) | US20110207003A1 (ko) |
EP (1) | EP2175968A1 (ko) |
JP (1) | JP5266323B2 (ko) |
KR (1) | KR101410856B1 (ko) |
CN (1) | CN101784330B (ko) |
CA (1) | CA2694774A1 (ko) |
DE (1) | DE102007037796A1 (ko) |
WO (1) | WO2009021850A1 (ko) |
Families Citing this family (5)
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US10792647B2 (en) * | 2009-04-21 | 2020-10-06 | Johnson Matthey Public Limited Company | Base metal catalysts for the oxidation of carbon monoxide and volatile organic compounds |
US7818969B1 (en) | 2009-12-18 | 2010-10-26 | Energyield, Llc | Enhanced efficiency turbine |
JP5863819B2 (ja) * | 2010-11-18 | 2016-02-17 | クラリアント コーポレイション | 燃料電池のアノード排ガスからco、h2、及びch4を除去する方法並びにこれらのガスを除去するのに有用な触媒 |
ITMI20112387A1 (it) | 2011-12-27 | 2013-06-28 | Getters Spa | Combinazione di materiali getter e dispositivo getter contenente detta combinazione di materiali getter |
US11173451B1 (en) * | 2020-10-29 | 2021-11-16 | Air Products And Chemicals, Inc. | Removal of hydrogen impurity from gas streams |
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US3914389A (en) * | 1974-03-22 | 1975-10-21 | American Cyanamid Co | Lanthanum oxidation catalyst and method for utilizing the same |
DE3770920D1 (de) * | 1986-12-03 | 1991-07-25 | Catalyst And Chemicals Inc Far | Feuerfester katalysator und verfahren zu seiner herstellung. |
US4900712A (en) | 1988-09-30 | 1990-02-13 | Prototech Company | Catalytic washcoat and method of preparation of the same |
ES2100877T5 (es) * | 1989-12-27 | 2004-03-16 | The Standard Oil Company | Reactores electroquimicos y membranas de varios componentes utiles para reacciones de oxidacion. |
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-
2007
- 2007-08-10 DE DE102007037796A patent/DE102007037796A1/de not_active Ceased
-
2008
- 2008-07-30 US US12/671,737 patent/US20110207003A1/en not_active Abandoned
- 2008-07-30 EP EP08786651A patent/EP2175968A1/de not_active Withdrawn
- 2008-07-30 JP JP2010519438A patent/JP5266323B2/ja not_active Expired - Fee Related
- 2008-07-30 CN CN200880102851XA patent/CN101784330B/zh not_active Expired - Fee Related
- 2008-07-30 CA CA2694774A patent/CA2694774A1/en not_active Abandoned
- 2008-07-30 KR KR1020107005231A patent/KR101410856B1/ko active IP Right Grant
- 2008-07-30 WO PCT/EP2008/060024 patent/WO2009021850A1/de active Application Filing
Also Published As
Publication number | Publication date |
---|---|
CN101784330B (zh) | 2013-03-06 |
US20110207003A1 (en) | 2011-08-25 |
KR20100051854A (ko) | 2010-05-18 |
CA2694774A1 (en) | 2009-02-19 |
JP2010535612A (ja) | 2010-11-25 |
WO2009021850A1 (de) | 2009-02-19 |
KR101410856B1 (ko) | 2014-06-24 |
DE102007037796A1 (de) | 2009-02-12 |
JP5266323B2 (ja) | 2013-08-21 |
CN101784330A (zh) | 2010-07-21 |
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