US20100196237A1 - Templated catalyst composition and associated method - Google Patents

Templated catalyst composition and associated method Download PDF

Info

Publication number
US20100196237A1
US20100196237A1 US12/362,533 US36253309A US2010196237A1 US 20100196237 A1 US20100196237 A1 US 20100196237A1 US 36253309 A US36253309 A US 36253309A US 2010196237 A1 US2010196237 A1 US 2010196237A1
Authority
US
United States
Prior art keywords
composition
percent
degrees celsius
silver
templated
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.)
Abandoned
Application number
US12/362,533
Inventor
Ming Yin
Larry Neil Lewis
Dan Hancu
Oltea Puica Siclovan
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
General Electric Co
Original Assignee
General Electric Co
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by General Electric Co filed Critical General Electric Co
Priority to US12/362,533 priority Critical patent/US20100196237A1/en
Assigned to GENERAL ELECTRIC COMPANY reassignment GENERAL ELECTRIC COMPANY ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: HANCU, DAN, LEWIS, LARRY NEIL, SICLOVAN, OLTEA PUICA, YIN, MING
Publication of US20100196237A1 publication Critical patent/US20100196237A1/en
Priority to US14/160,379 priority patent/US9463439B2/en
Abandoned legal-status Critical Current

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/48Silver or gold
    • B01J23/50Silver
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8621Removing nitrogen compounds
    • B01D53/8625Nitrogen oxides
    • B01D53/8628Processes characterised by a specific catalyst
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/92Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9404Removing only nitrogen compounds
    • B01D53/9409Nitrogen oxides
    • B01D53/9413Processes characterised by a specific catalyst
    • B01D53/9418Processes characterised by a specific catalyst for removing nitrogen oxides by selective catalytic reduction [SCR] using a reducing agent in a lean exhaust gas
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J21/00Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
    • B01J21/02Boron or aluminium; Oxides or hydroxides thereof
    • B01J21/04Alumina
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/56Platinum group metals
    • B01J23/60Platinum group metals with zinc, cadmium or mercury
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/66Silver or gold
    • B01J23/68Silver or gold with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/683Silver or gold with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium with chromium, molybdenum or tungsten
    • B01J23/687Silver or gold with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium with chromium, molybdenum or tungsten with tungsten
    • B01J35/30
    • B01J35/56
    • B01J35/61
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/03Precipitation; Co-precipitation
    • B01J37/031Precipitation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/10Noble metals or compounds thereof
    • B01D2255/102Platinum group metals
    • B01D2255/1021Platinum
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/10Noble metals or compounds thereof
    • B01D2255/102Platinum group metals
    • B01D2255/1025Rhodium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/10Noble metals or compounds thereof
    • B01D2255/104Silver
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/209Other metals
    • B01D2255/2092Aluminium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/90Physical characteristics of catalysts
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts

Abstract

A composition includes a templated metal oxide, at least 3 weight percent of silver, and at least one catalytic metal. A method of making and a method of using are included.

Description

    BACKGROUND
  • 1. Technical Field
  • The invention includes embodiments that relate to a catalyst composition. The invention includes embodiments that relate to a method of making the catalyst composition and a method of using the catalyst composition for reducing nitrogen oxides.
  • 2. Discussion of Art
  • Currently, lean NOx traps may be used in exhaust gas treatment systems. In these, NOx reduction catalysts and methods include the alkali and alkali earth metal in the catalyst composition where the alkali metal or the alkali metal absorbs the NOx and the reductant reduces NOx to nitrogen. This type of reaction may not have desirable kinetics.
  • Silver-containing alumina is known for selective catalytic reduction (SCR) of NOx using linear hydrocarbon reductants. However, reductants containing aromatics like those present in Diesel fuel, lead to poor NOx reduction with concomitant carbon deposition.
  • Therefore, it may be desirable to have a catalyst composition with properties and characteristics that differ from those properties of currently available compositions or catalysts. It may be desirable to have a method that differs from those methods currently available.
  • BRIEF DESCRIPTION
  • In one embodiment, a composition includes a templated metal oxide substrate having a plurality of pores and a catalyst material. The catalyst material includes silver and a catalyst metal. The silver is present in an amount that is at least about three weight percent based on a total weight of the substrate.
  • In one embodiment, a method of using the said catalyst composition is by introducing a gas stream in a chamber having a composition including a templated metal oxide substrate having a plurality of pores, a catalyst material includes silver and a catalyst metal. The silver is present in an amount of at least about three weight percent based on a total weight of the substrate. The nitrogen oxide present in the gas stream is reduced at a temperature in the range from about 275 degrees to about 350 degrees Celsius in the chamber.
  • BRIEF DESCRIPTION OF DRAWINGS
  • FIG. 1 is a graph of low angle X-Ray Diffraction (XRD) scan;
  • FIG. 2 is an image of scanning electron microscope (SEM) for Ag-Templated Alumina;
  • FIG. 3 is an image of scanning electron microscope (SEM) for SBA alumina 200 from SASOL;
  • FIG. 4 is an image of scanning electron microscope (SEM) for Norton Alumina;
  • FIG. 5 is a visible-ultra-violet spectrum of a catalytic material;
  • FIG. 6 is a visible-ultra-violet spectrum of a catalytic material;
  • FIGS. 7 and 8 are graphical representations of NOx conversion;
  • FIGS. 9 and 10 are graphical representations of NOx conversion;
  • FIGS. 11 and 12 are graphical representations of NOx conversion;
  • FIGS. 13 and 14 are graphical representations of NOx conversion;
  • FIGS. 15 and 16 are graphical representations of NOx conversion;
  • FIGS. 17 and 18 are graphical representations of NOx conversion;
  • FIG. 19 is a graphical representation of NOx conversion;
  • FIG. 20 is a graphical representation of NOx conversion; and
  • FIG. 21 is a graphical representation of NOx conversion.
  • DETAILED DESCRIPTION
  • The systems and methods described herein include embodiments that relate to a catalyst composition, embodiments that relate to a method of making the catalyst composition, and a method of using the catalyst composition for reducing nitrogen oxides. Generally, disclosed is a NOx reduction catalyst and NOx reduction system for reducing NOx in exhaust gas discharged from a combustion device. Suitable combustion devices may include furnaces, ovens or engines.
  • As used herein, a catalyst is a substance that can cause a change in the rate of a chemical reaction without itself being consumed in the reaction. A slurry is a mixture of a liquid and finely divided particles. A sol is a colloidal solution. A powder is a substance including finely dispersed solid particles. Templating refers to a controlled patterning; and, templated refers to determined control of an imposed pattern and may include molecular self-assembly. A monolith may be a ceramic block having a number of channels, and may be made by extrusion of clay, binders and additives that are pushed through a dye to create a structure. Approximating language, as used herein throughout the specification and claims, may be applied to modify any quantitative representation that could permissibly vary without resulting in a change in the basic function to which it is related. Accordingly, a value modified by a term such as “about” is not to be limited to the precise value specified. In some instances, the approximating language may correspond to the precision of an instrument for measuring the value. Similarly, “free” may be used in combination with a term, and may include an insubstantial number, or trace amounts, while still being considered free of the modified term.
  • In one embodiment, the composition includes a templated metal oxide substrate having a plurality of pores, and a catalyst material includes both silver and a catalyst metal. The silver is present in an amount that is at least about three weight percent based on a total weight of the substrate.
  • In addition to being templated, the substrate may have a macro-shape that is, for example, a ceramic honeycomb. With regard to the templating, the substrate material may have a plurality of pores that may have specific dimensions and periodicity. That is, the templated metal oxide may have periodically arranged templated pores of determined dimensions. The dimensions can include pore diameter, degrees of curvature, uniformity of the inner surface, and the like. The average diameter of the pores may be greater than about 2 nanometers. The average diameter of the pores may be less than about 100 nanometers. The average diameter of the pores may be in a range from about 2 nanometers to about 20 nanometers, from about 20 nanometers to about 40 nanometers, from about 40 nanometers to about 60 nanometers, from about 60 nanometers to about 80 nanometers, or from about 80 nanometers to about 100 nanometers. The pores may have a periodicity greater than about 50 Angstroms. The pores may have a periodicity less than about 130 Angstroms. The pores may have a periodicity in the range of from about 50 Angstroms to about 80 Angstroms, from about 80 Angstroms to about 100 Angstroms, from about 100 Angstroms to about 120 Angstroms, or from about 120 Angstroms to about 150 Angstroms. Low angle XRD, FIG. 1, for Ag-Templated Alumina comprising 3 percent or 5 percent silver prepared via sol gel or incipient wetness (IW) method. All samples calcinated at 600 degrees Celsius, show that Ag-Templated Alumina (TA) has pore dimensions of from 75-95 Angstroms depending on the method of preparation. FIG. 1 shows graph 10 that has peak 12 that denotes the average pore-to-pore correlation of about 75 Angstroms and peak 14 denotes the average pore-to-pore correlation of about 95 Angstroms. In one embodiment, the addition of a catalyst metal to the silver does not affect the properties of the templated metal oxide substrate.
  • The templated porous metal oxide substrate may have a surface area that is greater than about 0.5 meter2/gram. In one embodiment, the surface area is in a range of from about 0.5 meter2/gram to about 10 meter2/gram, from about 10 meter2/gram to about 100 meter2/gram, from about 100 meter2/gram to about 200 meter2/gram, or from about 200 meter2/gram to about 1200 meter2/gram. In one embodiment, the porous substrate has a surface area that is in a range of from about 0.5 meter2/gram to about 200 meter2/gram. In one embodiment, the porous substrate has a surface area in a range of from about 200 meter2/gram to about 250 meter2/gm, from about 250 meter2/gram to about 500 meter2/gm, from about 500 meter2/gram to about 750 meter2/gm, from about 750 meter2/gram to about 1000 meter2/gm, from about 1000 meter2/gram to about 1250 meter2/gm, from about 1250 meter2/gram to about 1500 meter2/gm, from about 1500 meter2/gram to about 1750 meter2/gm, from about 1750 meter2/gram to about 2000 meter 2/gm, or greater than about 2000 meter2/gm.
  • SEM analysis of Ag-Templated Alumina (TA), FIG. 2, appears to show the high surface area and may show the pore structure. The SEM picture in FIG. 2 is contrasted in FIG. 3 for SBA 200 alumina with lower surface area and lower activity than Ag-TA and similarly for Norton alumina in FIG. 4.
  • The templated porous metal oxide substrate may be present in the catalyst composition in an amount that is greater than about 50 mole percent. In one embodiment, the amount of templated metal oxide substrate may be in a range of from about 50 mole percent to about 60 mole percent, from about 60 mole percent to about 70 mole percent, from about 70 mole percent to about 80 mole percent, from about 80 mole percent to about 90 mole percent, from about 90 mole percent to about 95 mole percent, from about 95 mole percent to about 98 mole percent, based on the total weight of the catalyst composition.
  • In one embodiment, the metal oxide is an aluminum oxide. Other support materials may be suitable. These other support materials may include one or more of silicon, titanium or zirconium. Suitable support materials may include, for example, aluminosilicates, aluminophosphates, hexaaluminates, zirconates, titanosilicates, titanates, or a combination of two or more thereof. In other embodiments, other substrates or support materials may be suitable and can be selected based on end-use parameters.
  • The composition may also have a promoter for the catalytic reaction of nitrogen oxide reduction. Non-limiting examples of the catalyst may include various metals or metal oxides. The promoter may include one or more of indium, gallium, tin, silver, manganese, molybdenum, chromium, germanium, cobalt, nickel, gold, copper, iron, and their oxides. In one embodiment, the promoter includes silver.
  • In one embodiment, the catalyst material is free of one or both of alkali metal and alkaline earth metal. In one embodiment, the composition reduces NOx without absorbing the NOx on the catalyst material. In this embodiment, the catalytic action is distinct from the actions of a lean NOx trap.
  • In one embodiment, the catalyst composition may be made by reacting a metal alkoxide with a silver composition, a catalyst metal and a templating agent to form a reaction product. The templating agent may be a surfactant, a cyclodextrin, a crown ether, or mixtures thereof.
  • The reaction product may hydrolyze to form a hydrolyzed reaction product. The hydrolyzed reaction product may condense to form a templated substrate. The catalyst material loading of the templated substrate may be controlled by controlling the reacting, hydrolyzing and condensing steps. With particular reference to the hydrolyzing step, the rate of hydrolysis can be controlled to affect the reaction product properties, efficacy and function. While completion of the hydrolysis process is a goal, the process by which the hydrolysis is accomplished may be a factor in the reaction product properties, efficacy and function. Slowing the addition rate, and therefore the rate at which the hydrolysis can proceed to completion, is one way to control the final result. While it may be possible to add the reactants together in seconds, improved results may accompany an addition rate of slow and steady addition that is greater than about 1 hour. In one embodiment, the addition is in a time range to completion of from about 1 hour to about 3 hours. In one embodiment, the addition time occurs in an amount of from about 1 hour to about 2 hours, or from about 2 hours to about 3 hours. Adding the reactants in a continuous flow has a different effect relative to adding aliquots in a stepwise fashion over the addition period.
  • In one embodiment, the silver composition may be selected from a group consisting of silver salt of inorganic acids, silver salt of organic acids, and silver oxides. The silver may be present in an amount of at least about three weight percent based on a total weight of the substrate in one embodiment. In other embodiment, the silver may be present in an amount of less than or equal to about ten weight percent of a total weight of the substrate.
  • In one embodiment, the catalyst metal is selected from gallium, indium, iron, zirconium zinc, rhodium, platinum, or tungsten. The catalyst metal may be in elemental form, a complex, or as an oxide or equivalent form. For example, the catalyst metal may include tungstate or zirconate. In one embodiment, rather than an oxide form, the complex may include a nitride, carbide, silicide, boride, or aluminide. In one embodiment, the catalyst metal includes both gallium (Ga) and indium (In). In one embodiment, the catalyst metal consists essentially of iron. In one embodiment, the catalyst metal consists essentially of zirconium. In one embodiment, the catalyst metal consists essentially of zinc. In one embodiment, the catalyst metal consists essentially of rhodium. In one embodiment, the catalyst metal consists essentially of platinum. In one embodiment, the catalyst metal consists essentially of tungsten. The choice of catalyst material, the amount, and the combination (if any) or ratio of the combined materials has a direct effect on the function and properties of the resultant product.
  • In one method of making the catalyst, a metal alkoxide, a silver composition, a catalyst metal and a templating agent are mixed in a vessel with a suitable solvent to form a reaction product. Initially, the reaction product may be in the form of a sol. The sol may be converted to a gel by the sol gel process. The gel may be subject to one or more of filtration, washing, drying and calcinating to yield a solid catalyst composition that includes the catalytic metal disposed on a porous substrate.
  • The effect of iron on Ag-Templated Alumina catalytic activity is tested by varying the method by which silver is added to templated alumina (TA). The alternative method for introducing silver or any other element is called incipient wetness method whereby the precursor is added to the hydrolyzed and condensed templated alumina as an aqueous solution that wets the alumina followed by calcination. Templated alumina with sol gel silver had superior activity for NOx reduction than templated alumina with incipient wetness (IW) silver. There are alternative methods of adding silver or any other element in the templated alumina and those methods are known as impregnation methods. In one embodiment, the incipient wetness method is a type of impregnation method.
  • During the calcination process, the silver composition may be reduced to a catalytic metal. The calcination may be conducted at a temperatures in a range of from about 350 degrees Celsius to about 400 degrees Celsius, from about 400 degrees Celsius to about 500 degrees Celsius, from about 500 degrees Celsius to about 600 degrees Celsius, from about 600 degrees Celsius to about 700 degrees Celsius, or from about 700 degrees Celsius to about 800 degrees Celsius. In one embodiment, the calcination may be conducted at a temperature of about 550 degrees Celsius. The calcination may be conducted for a period of from about 10 minutes to about 30 minutes, from about 30 minutes to about 60 minutes, from about 60 minutes to about 1 hour, from about 1 hour to about 10 hours, from about 10 hours to about 24 hours, or from about 24 hours to about 48 hours.
  • Suitable solvents may include aprotic polar solvents, polar protic solvents, and non-polar solvents. Suitable aprotic polar solvents may include propylene carbonate, ethylene carbonate, butyrolactone, acetonitrile, benzonitrile, nitromethane, nitrobenzene, sulfolane, dimethylformamide, N-methylpyrrolidone, or the like. Suitable polar protic solvents may include water, nitromethane, acetonitrile, and short chain alcohols. Suitable short chain alcohols may include one or more of methanol, ethanol, propanol, isopropanol, butanol, or the like. Suitable non-polar solvents may include benzene, toluene, methylene chloride, carbon tetrachloride, hexane, diethyl ether, or tetrahydrofuran. Co-solvents may also be used. Ionic liquids may be used as solvents during gelation. Exemplary solvents may include short-chain alcohols, such as 2-butanol and 2-propanol.
  • Selection of the type(s) and amounts of the templating agent may affect or control the pore characteristics of the resultant templated substrate. Suitable templating agents may include one or more surfactants. Suitable surfactants may include cationic surfactants, anionic surfactants, non-ionic surfactants, or Zwitterionic surfactants. In one embodiment, the templating agent may include one or more cyclic species. Examples of such cyclic species may include cyclodextrin and crown ether.
  • Suitable cationic surfactants may include cetyltrimethyl ammonium bromide (CTAB), cetylpyridinium chloride (CPC), polyethoxylated tallow amine (POEA), benzalkonium chloride (BAC), and benzethonium chloride (BZT). Other suitable cationic surfactants may include those having a chemical structure denoted by CH3(CH2)15N(CH3)3-Br, CH3(CH2)15-(PEO)n-OH where n=2 to 20 and where PEO is polyethylene oxide, CH3(CH2)14COOH and CH3(CH2)15NH2. Other suitable cationic surfactants may include one or more fluorocarbon surfactants, such as C3F7O(CFCF3CF2O)2CFCF3—CONH(CH2)3N(C2H5)2CH3I), which is commercially available as FC-4.
  • Suitable anionic surfactants may include one or more of sodium dodecyl sulfate (SDS), ammonium lauryl sulfate, alkyl sulfate salts, sodium laureth sulfate also known as sodium lauryl ether sulfate (SLES), alkyl benzene sulfonate, soaps, fatty acid salts, or sodium dioctyl sulfonate (AOT). Suitable Zwitterionic surfactants may include dodecyl betaine, dodecyl dimethylamine oxide, cocamidopropyl betaine, or coco ampho-glycinate.
  • Nonionic surfactants may have polyethylene oxide molecules as hydrophilic groups. Suitable ionic surfactants may include alkyl poly(ethylene oxide), copolymers of poly(ethylene oxide) and poly(propylene oxide) commercially called Poloxamers or Poloxamines and commercially available under the trade name PLURONICS from the BASF company.
  • Suitable non-ionic surfactants may include one or more alkyl polyglucosides, octylphenol ethoxylate, decyl maltoside, fatty alcohols, cetyl alcohol, oleyl alcohol, cocamide monoethanolamine, cocamide diethanolamine, cocamide triethanolamine, 4-(1,1,3,3-tetramethyl butyl)phenyl-poly (ethylene glycol), polysorbitan monooleate, or amphiphilic poly (phenylene ethylene) (PPE). Suitable poly glucosides may include octyl glucoside. Other suitable non-ionic surfactants may include long-chain alkyl amines, such as primary alkylamines and N,N-dimethyl alkylamines. Suitable primary alkylamines may include dodecylamine and hexadecylamine. Suitable N,N-dimethyl alkylamines may include N,N-dimethyl dodecylamine or N,N-dimethyl hexadecylamine. Suitable non-ionic surfactant may include (1,1,3,3-Tetramethylbutyl)phenyl-polyethylene glycol, which is commercially available as TRITON X-114 from the Sigma-Aldrich company.
  • In one embodiment, the templating agent may include cyclodextrin. Cyclodextrins may include cyclic oligosaccharides that include five or more α-D-glucopyranoside units linked 1 to 4, as in amylose (a fragment of starch). Suitable cyclodextrins in the templating agent may include 5-membered to about 150-membered cyclic oligosaccharides. Exemplary cyclodextrins include a number of glucose monomers ranging from six to eight units in a ring. Suitable cyclodextrins are α-cyclodextrin, a six membered sugar ring molecule; β-cyclodextrin, a seven sugar ring molecule; γ-cyclodextrin, an eight sugar ring molecule; or the like.
  • As noted above, the templating agent may include crown ethers. Crown ethers are heterocyclic chemical compounds that include a ring containing several ether groups. Suitable crown ethers may include oligomers of ethylene oxide, the repeating unit being ethyleneoxy, i.e., —CH2CH2O—. Useful members of this series may include the tetramer (n=4), the pentamer (n=5), and the hexamer (n=6). Crown ethers derived from catechol may be used in the templating agent. Crown ethers that strongly bind certain types of cations to form complexes may be included in the templating agents. The oxygen atoms in the crown ether may coordinate with a cation located at the interior of the ring, whereas the exterior of the ring may be hydrophobic. For example, 18-crown-6 has high affinity for potassium cation, 15-crown-5 for sodium cation, and 12-crown-4 for lithium cation.
  • In one embodiment, a method of using the said catalyst composition may be by introducing a gas stream in a chamber having a composition comprising a templated metal oxide substrate having a plurality of pores, a catalyst material comprising silver. The silver may be present in an amount of at least about three weight percent based on a total weight of the substrate. The nitrogen oxide present in the gas stream may be reduced at a temperature of about 275 degrees Celsius or greater. In one embodiment, the reduction may occur at a temperature range of from about 275 degrees Celsius to about 300 degrees Celsius, from about 300 degrees Celsius to about 325 degrees Celsius, or from about 325 degrees Celsius to about 350 degrees Celsius. The nitrogen oxide present in the gas stream may be reduced at a temperature of less than about 350 degrees Celsius in the chamber.
  • As noted in the disclosure, the composition can include a templated mesoporous metal oxide substrate, catalyst metal, and an amount silver. The composition can be entirely free of alkaline earth metal, and may reduce NOx without absorbing the NOx on the catalyst material surface. Further, possibly owing to the method of formation, the templated metal oxide and silver may have a distinguishable visible-ultra-violet (VIS-UV) absorbance intensity that is at least 20 percent less than a standard silver alumina catalyst (Ag STD) at a wavelength in a range of from about 350 nm to about 500 nm, at under H2 at 30 degrees Celsius. The standard silver alumina has alumina as Norton alumina, and which have the same amount of silver by weight. One difference affecting the absorbance may be the form, size and distribution of the silver relative to the templated metal oxide. The addition of the catalyst metal may further affect the efficacy, performance and function of the final reaction product.
  • EXAMPLES Example 1
  • A process for templated alumina includes the preparation of the following solutions. Solution 1 is ethyl acetoacetate (26.5 g, 0.2 mol), TRITON X-114 (85 g, ca. 0.15 mol) and 2-butanol (500 mL), which are combined in a 5-liter, 3-neck flask equipped with an addition funnel, a condenser a mechanical stirrer. Solution 2 is Al(O-secBu)3 (500 g, 2 mol) and 2-BuOH (2 L). Solution 3 is water (75 mL, 4 mol) and 2-BuOH (850 mL).
  • Solution 1 is added to Solution 2 with stirring, and the combined volume is held at ambient temperature for 30 minutes. Solution 3 is added to the combined solutions 1 and 2 via an addition funnel over 90 minutes. Mechanical stirring continues at ambient temperature for 3 hours, and the contents are heated to reflux for about 20 to 24 hours.
  • The contents are cooled and are filtered on #50 filter paper. The contents are washed with ethanol. The obtained white solid is dried in a vacuum oven at 80 degrees Celsius. The solid is subjected to Soxhlet extraction with ethanol for 20-24 h. The solid is dried in a vacuum oven at 80 degrees Celsius, and yields 164 grams. The dry material is heated under N2 in a tube furnace from room temperature to 550 degrees Celsius at a heating rate of 2 degrees Celsius/minute, maintained at 550 degrees Celsius for 1 hr and finally calcined in a flow of air at 550 degrees Celsius for 5 hours.
  • A process for forming templated metal oxide with silver includes the following. A 5-liter, 3-necked flask equipped with a mechanical stirrer, a reflux condenser, and an addition funnel is charged with TRITON X114 (68.7 g, 0.16 mol) and ethylacetoacetate (13.2 g, 0.1 mol) in 250 mL of 2-propanol. An amount of Al(OsecBu)3 (249.8 g, 1.02 mol) that is dissolved or suspended in 1-liter of 2-propanol is added to the flask. The contents are stirred for 30 minutes. An amount of silver nitrate (AgNO3) is dissolved in water (37 mL, 2.06 mol). The silver nitrate solution is changed/varied as noted below to create a number of reaction products. The silver nitrate solution is combined with 500 mL of 2-propanol and is charged to an addition funnel. The contents of the addition funnel are added to a 5-liter flask over the course of 75 minutes. The stirred solution is refluxed for 24 hours.
  • After cooling, the contents are filtered and washed with about 250 mL of ethanol to obtain a semi-dried mass. The semi-dried mass is subjected to Soxhlet extraction with ethanol for 24 hours and oven-vacuum dried at 30 mmHg for 24 hours to obtain a solid. The obtained brown solid is condensed, which here is calcined, under nitrogen in a tube furnace to 550 degrees Celsius at a heating rate of 2 degrees Celsius/minute to obtain a reaction product.
  • A series of Catalyst Products are formed. The amount of AgNO3 (2.6 g, 0.0158 mol) for Catalyst Product 1, results in 3 percent silver templated alumina catalyst composition. The amount of AgNO3 (3.463 g, 0.0204 mol) for Catalyst Product 2, results in 4 percent silver templated alumina catalyst composition. The amount of AgNO3 (4.407 g, 0.0259 mol) for Catalyst Product 3, results in 5 percent silver templated alumina catalyst composition. The amount of AgNO3 (5.383 g, 0.0317 mol) for Catalyst Product 4, results in 6 percent silver templated alumina catalyst composition. The amount of AgNO3 (6.391 g, 0.0376 mol) for Catalyst Product 5, results in 7 percent silver templated alumina catalyst composition. The amount of AgNO3 (7.49 g, 0.0441 mol) for Catalyst Product 6, results in 8 percent silver templated alumina catalyst composition. The amount of AgNO3 (8.443 g, 0.0497 mol) for Catalyst Product 7, results in 9 percent silver templated alumina catalyst composition.
  • Catalyst Product 8—Templated Alumina with 8 percent Silver having a different solvent: A 5 L 3-neck round bottom flask equipped with a mechanical stirrer, reflux condenser, and addition funnel is charged with ethyl acetoacetate (13.26 g, 0.1019 mol), TRITON X114 (69.73 g, 0.1117 mol) and 250 mL of 2-Butanol. The stirrer is turned on low. Aluminum sec-butoxide (250.96 g, 1.0188 mol) is dissolved in 1 Liter of 2-BuOH and transferred to the 5 L flask. This reaction mixture is stirred under ambient conditions for 30 minutes. AgNO3 (7.49 g, 0.0441 mol) is dissolved in 37.5 mL of distilled H2O and combined with 425 mL of 2-BuOH to produce a transparent, clear solution. This solution is added via dropping funnel to the 5 L flask. The stir speed is adjusted to account for changing viscosity of the fluid, water addition occurred over the course of 2-3 hours. The mixture is aged at 95 degrees Celsius for 24 hours.
  • Two different processes are carried out with portions of the obtained slurry. 1.) Alumina-water slurry. Distilled water (1.47 L) is added to the flask in order to remove butanol via azeotropic distillation (bp ca. 87 degrees Celsius) and to yield a water slurry of 5 percent solids. 2.) Extracted Solid. The obtained slurry described above is filtered through a #50 filter paper on a Buchner funnel, washed with ethanol and the obtained solid is extracted with ethanol in a Soxhlet apparatus. The solid is dried in a vacuum oven at 80 degrees Celsius, yielding 164 grams. The dry material is heated under N2 in a tube furnace from room temperature to 550 degrees Celsius at a heating rate of 2 degrees Celsius/min, maintained at 550 degrees Celsius for 1 hr and calcined in a flow of air at 550 degrees Celsius for 5 hours to get Catalyst Product 8.
  • FIG. 5 is a graph that plots VIS-UV absorbance intensity at different wavelengths. The plot compares the Comparative Ag STD, Ag TA (sol-gel) and Ag TA (impregnated), all having the same Ag percent. The test conditions are under H2 at 30 degrees Celsius (spectra have been subtracted with the ones from fresh catalyst under He at 30 degrees Celsius). The Ag TA (sol-gel) is a silver templated alumina catalyst made by the sol gel process and Ag TA (impregnated) is a silver templated alumina catalyst made by the impregnation process. Particularly, Curve 16 is a comparative plot for 8 percent Ag with standard Norton alumina under H2 at 30 degrees Celsius. Curve 18 is a plot for 8 percent Ag with templated alumina made by sol gel method under H2 at 30 degrees Celsius (Catalyst Product 8). Curve 20 is a plot for 8 percent Ag with templated alumina made by impregnation method under H2 at 30 degrees Celsius. In FIG. 5, curve 16 indicates the amount of silver ion (Ag+) agglomeration, the peak is identified with reference number 22, silver (Ag) cluster agglomeration, peak 24, and Ag particles agglomeration, peak 26.
  • FIG. 6 is a graph that plots VIS-UV absorbance intensity at different wavelengths. Curve 28 is a comparative plot for 8 percent Ag with standard Norton alumina under H2 at 300 degrees Celsius. Curve 30 is a plot for 8 percent Ag with templated alumina made by sol gel method under H2 at 300 degrees Celsius (Catalyst Product 6). Curve 32 is a plot for 8 percent Ag with templated alumina made by impregnation method under H2 at 300 degrees Celsius. For the standard silver alumina catalyst (curve 18) the agglomeration is very high whereas for the silver templated alumina catalyst the agglomeration is low, showing the relatively different properties with regard to the silver templated alumina catalyst.
  • With respect to FIG. 6 the graph that shows the Catalyst Product 6 is having a VIS-UV absorbance intensity that is at least 20 percent less than a comparative silver alumina catalyst (Ag STD). The standard alumina is Norton alumina, and which has the same amount of silver by weight, at a wavelength in a range of from about 350 nm to about 500 nm, under H2 at 30 degrees Celsius.
  • Catalyst Product 6 has a visible-ultra-violet (VIS-UV) absorbance intensity that is at least 20 percent less than a standard silver alumina catalyst (Ag STD), under H2 at 30 degrees Celsius and at a wavelength that is in a range of from about 350 nanometers (nm) to about 500 nm. The standard alumina is Norton alumina, and has the same amount of silver by weight as the instant composition. FIGS. 5 and 6 indicate an amount of silver (Ag) agglomeration (Ag particles and mainly Ag clusters) and silver ion (Ag+) agglomeration. For the standard silver alumina catalyst, the agglomeration is relatively high, whereas for the silver templated alumina catalyst the agglomeration is relatively low. The agglomeration level affects, and possibly controls, the function and efficacy of the corresponding material.
  • Example 2 Zirconium
  • In the following examples, at least one compositional species is shown in detail. Compositional variations are performed for the purpose of examining larger data sets, but are not included in detail for the sake of clarity. Example 2 includes the preparation of 3 percent Ag-templated alumina (TA)+0.25 percent Zr as Zr(O(CH2)3CH3)4—CH3(CH2)3OH replacing Alumina. A 1000 mL 3-neck round bottom flask is set-up in an oil bath with stir bar and equipped with a mechanical stirrer, reflux condenser and addition funnel. A dropping funnel for hydrolysis later replaces the addition funnel.
  • An amount of 50.81 g (0.2063 mol) of Aluminum sec-butoxide (Al(OsecBu)3) are dissolved in 200 mL of 2-Butanol (2-BuOH) and added to the flask. The 2-BuOH is divided in half, one used to transfer the Al(OsecBu)3 and the other the rinse the remaining portion from the container walls. After addition to the flask, the mechanical stirrer is turned on using a low setting. 2.674 g (0.0205 mol) of Ethyl acetoacetate (EA), 14.084 g (0.02257 mol) Triton X-114, and 60 mL 2-BuOH are combined and added to the flask with the Al(OsecBu)3 solution. This solution is allowed to stir under ambient conditions for 30 minutes. 0.243 g (5.308E-04 moles) Zr(O(CH2)3CH3)4—CH3(CH2)3OH are dissolved in 2-BuOH for transfer and added to the flask. The mixture is stirred for additional time at a medium pace. AgNO3 (0.5356 g, 0.00315 mol) is dissolved in 7.5 mL H2O and is combined with 85 mL of 2-BuOH. This solution is added to the dropping funnel, which is put in place of the addition funnel. After approximately 45 minutes elapsed, the dropping funnel is turned on and allowed to drip at a controlled pace. Controlling the addition rate and operating parameters affects the hydrolysis rate, and therefore the properties and function of the reaction product.
  • After the hydrolysis is complete, the stirrer is turned up to account for the gaining viscosity of the mixture and a stopper replaced the dropping funnel. The mixture is stirred under ambient conditions for approximately 3 hours following the completion of hydrolysis. After 3 hours, the reaction mixture is aged at 95 degrees Celsius for 24 hours with stirring. The resulting gel is filtered overnight and extracted using Soxhlet Extraction with ethanol (EtOH) for 24 hours. The extracted solid is dried in a vacuum oven at 50 degrees Celsius overnight.
  • Several samples are prepared, each having 3 percent Ag TA and each having a differing level of zirconia. Some of these new materials show enhanced catalytic activity, and are shown compared to 3 percent Ag TA alone. FIGS. 7 and 8 are graphical representations of average NOx Conversion, and standard deviation, at 325 degrees Celsius (FIG. 7) and 375 degrees Celsius (FIG. 8) for 3 percent Ag-TA (far left); 3 percent Ag-TA with 1 percent zirconia (middle); and 3 percent Ag-TA 10 percent zirconia (far right). As shown with reference to FIGS. 7 and 8, the improved activity occurred with a 1 percent but not with 10 percent framework substitution of aluminum with zirconium. Unexpectedly, adding more catalyst metal had the reverse effect on efficacy.
  • FIGS. 9 and 10 are graphical representations of average NOx Conversion and standard deviation at 325 degrees Celsius (FIG. 9) and 375 degrees Celsius (FIG. 10) for differing values of catalyst metal. As shown in FIGS. 9 and 10, catalytic activity for NOx reduction varies as a function of zirconia loading and of temperature. A 0.5 to 1 mol percent zirconia has the highest activity compared to the other zirconia-containing compositions in the experiment. Simply adding more catalyst metal does not increase efficacy.
  • Example 3 Iron
  • Example 3 includes the preparation of 3 percent Ag-Templated alumina (TA) with 0.5 percent iron (Fe) as Fe(NO3)2.9H2O supported by Al2O3. A 1-liter, 3-neck round bottom flask is set-up in an oil bath with stir bar and equipped with a mechanical stirrer, reflux condenser and addition funnel. A dropping funnel for hydrolysis later replaced the addition funnel. After the set-up is complete, 50.9 g (0.2066 mol) of Aluminum sec-butoxide (Al(OsecBu)3) are dissolved in 200 mL of 2-Butanol (2-BuOH) and added to the flask. The 2-BuOH is divided in half, one used to transfer the Al(OsecBu)3 and the other to remove the remaining portion from the container walls. Following the addition to the flask, the mechanical stirrer is turned on using a low setting. 2.648 g (0.0203 mol) of Ethyl acetoacetate (EA), 14.150 g (0.02268 mol) Triton X-114, and 60 mL 2-BuOH are combined and added to the flask with the Al(OsecBu)3 solution. The mixture is stirred for 30 minutes at a medium pace. During the 30-minute ambient stir period, 0.5345 g (0.003147 mol) of AgNO3 are dissolved in 7.6 mL H2O and combined with 85 mL of 2-BuOH. This solution is added to the dropping funnel, which is put in place of the addition funnel. After the 30 minutes elapsed, the dropping funnel is turned on and allowed to drip at a medium pace. After the hydrolysis is complete, the stirrer is turned up to gain viscosity of the mixture and a stopper replaces the dropping funnel.
  • The mixture is stirred under ambient conditions for approximately 3 hours following the completion of hydrolysis. After 3 hours, the reaction mixture is aged at 95 degrees Celsius for 24 hours with stirring. Approximately 30 minutes before the completion of the aging period, 0.2062 g (5.104E-04 mol) of Fe(NO3)2-9H2O is dissolved in just enough deionized H2O and added to the flask. The mixture is allowed to stir for an extra hour. The resulting gel is filtered overnight and extracted using Soxhlet Extraction with ethanol (EtOH) for 24 hours. The extracted solid is dried in a vacuum oven at 50 degrees Celsius overnight.
  • FIGS. 11 and 12 are graphical representations of average NOx conversion, and standard deviation, at 325 degrees Celsius (FIG. 11) and 375 degrees Celsius (FIG. 12) for (from left to right) 3 percent Ag-TA sol gel; 3 percent Ag-TA IW; 3 percent Ag-TA with 1 percent iron IW; 3 percent Ag-TA with 0.5 percent iron IW; and 3 percent Ag-TA with 0.1 percent iron IW. As shown in FIGS. 11 and 12, TA with sol gel silver had superior activity for NOx reduction than TA with incipient wetness (IW) silver. However, it is unexpected that the level of activity that is achievable with the sol-gel method can be achieved using incipient wetness method, by the addition of a transition metal as a catalyst—in this instance iron. Some TA with IW silver and IW iron of various levels displayed catalytic activity similar to that for Ag-TA sol gel. Also, unexpectedly, there is an inflexion point such that there is not a proportional relationship between the amount of catalyst material and the efficacy. That is, merely adding more catalyst does not increase catalytic activity. At the higher test temperature, the indicated trend is that adding less iron increases the catalytic activity until some point where no iron is present, and at which point the efficacy plummets.
  • Example 4 Gallium and Indium
  • Example 4 includes the preparation of 3 percent Ag-Templated Alumina with a combination of 2 percent gallium and 0.5 percent indium. A 1-liter, 3-necked flask equipped with a mechanical stirrer and an addition funnel is charged with Al(OsecBu)3 (97.5 g, 0.396 mol) and dissolved in 400 ml 2-butanol. Ga(OiPr)3 (2.0054 g, 0.00812 moles) is added to the stirring reaction mixture as a solid. In(OiPr)3 (11.86 ml solution 5 percent w/v, 0.00203 moles) is also added to the reaction mixture via a syringe. The flask is charged with ethyl acetoacetate (5.3 grams, 0.04 mol) and TRITON X-114 (28 grams) in 120 ml 2-butanol. The reaction mixture is stirred until all the Ga(OiPr)3 is dissolved (about 2 hrs) at room temperature. A solution composed of 170 ml 2-butanol, 15 ml H2O, AgNO3 (1.0398 g, 0.0061moles) is added drop wise from a dropping funnel to the reaction mixture under continuous stirring from an overhead stirrer. After addition of the entire amount of the water solution, the resulting reaction mixture is stirred at room temperature for 3 hours, and is aged for 24 hours at 95 degrees Celsius. The resulting gel is filtered overnight. The excess surfactant is removed by Soxhlet extraction with ethanol for 24 hours. The obtained solid is dried in a vacuum oven at 50 degrees Celsius overnight.
  • FIGS. 13 and 14 are graphical representations of average NOx conversion, and standard deviation, at 325 degrees Celsius (FIG. 13) and 375 degrees Celsius (FIG. 14) for 3 percent Ag-TA with (from left to right): 2 percent gallium and 1 percent indium; 5 percent gallium and 0.5 percent indium; 2 percent gallium and 0.5 percent indium; 5 percent gallium and 1 percent indium; and (far right) a 3 percent Ag-TA only control. FIGS. 13 and 14 show relatively improved NOx conversion at 375 degrees Celsius for the 3 percent Ag-TA materials with 2 percent gallium and 1 percent indium, 5 percent gallium 0.5 percent indium and 2percent gallium 0.5 percent indium. There is no improvement observed for the 3 percent Ag-TA with 5 percent gallium and 1 percent indium. Lower levels of gallium and indium, alone or in combination, or differing ratio's could have relatively better catalytic activity for NOx reduction. There appears to be a range of improved activity at a ratio of Ga:In of greater than 2:1.
  • Example 5 Tungsten
  • Example 5 includes the preparation of 3 percent Ag-Templated Alumina 1.5 percent silver tungstate. A 1-liter, 3-necked flask equipped with a mechanical stirrer and an addition funnel is charged with Al(OsecBU)3 (100 g, 0.40568 mol) and dissolved in 400 ml 2-butanol. The flask is next charged with ethyl acetoacetate (5.3 g, 0.04 mol) and TRITON X-114 (28 g) in 120 ml 2-Butanol. The reaction mixture is stirred for 30 minutes at room temperature. A solution composed of 170 ml 2-butanol and 15 ml H2O is added drop-wise from a dropping funnel to the reaction mixture under continuous stirring by an overhead stirrer. After addition of the entire amount of water and 2-butanol solution, the resulting reaction mixture is allowed to stir at room temperature for 3 hours, and is aged for approximately 12 hours at 95 degrees Celsius.
  • A solution prepared by dissolving Ag2WO4 (1.4331 g) in the minimum amount of water and NH40H is added drop-wise, under strong stirring to the reaction mixture. The resulting mixture is allowed to age for another 12 hours at 95 degrees Celsius, it is filtered overnight. The excess surfactant is removed by Soxhlet extraction with ethanol for 24 hours. The obtained solid is dried in a vacuum oven at 50 degrees Celsius overnight.
  • FIGS. 15 and 16 are graphical representations of average NOx Conversion and standard deviation at 325 degrees Celsius (FIG. 15) and 375 degrees Celsius (FIG. 16) for (left to right): 3 percent Ag-TA sol gel; 3 percent Ag-TA IW; 3 percent Ag2WO4-TA sol gel; 3 percent Ag2WO4 TA IW; 2 percent Ag and 0.5 percent Ag2WO4 sol gel (note enhanced activity); 2 percent Ag and 0.5 percent Ag2WO4 IW; 1.5 percent Ag2WO4 sol gel; and 1.5 percent Ag2WO4IW. In FIGS. 15 and 16, at 375 degrees Celsius an enhancement of activity with 0.5 percent Ag2WO4 and 2 percent silver is noted. An equivalent, or better effect, is possible with a lesser total amount of silver.
  • Example 6 Zinc
  • Example 6 includes the preparation of 3 percent Ag-Templated Alumina with 0.5 percent zinc. A 1-liter, 3-neck round bottom flask equipped with a mechanical stirrer, reflux condenser and addition funnel is charged with Al(OsecBU)3 (49.95 g, 0.2028 mol). 200 mL of 2-Butanol (2-BuOH) are added to the flask. The 2-BuOH is divided in half, one used to transfer the Al(OsecBU)3 and the other the rinse the remaining portion from the container walls.
  • Following the addition to the flask, the mechanical stirrer is turned on using a low setting and the flask is charged with ethyl acetoacetate (2.655 g, 0.0204 mol), TRITON X-114 (14.05 g, 0.0225 mol) and 60 mL 2-BuOH. This solution is stirred under ambient conditions for 30 minutes. During this time, of AgNO3 (0.5352 g, 0.00315 mol) and Zn(NO3)2.6H2O (0.1539 g, 5.1735E-04 mol) are dissolved in 7.5 mL H2O and combined with 85 mL of 2-BuOH. This solution is added to the addition funnel. After 30 minutes have elapsed, the addition funnel is turned on and allowed to drip at a controlled pace. The drip rate controls the rate of hydrolysis, which in turn can affect the property and function of the reaction product.
  • After the hydrolysis is complete, the stirrer is turned up to account for the gaining viscosity of the mixture and a stopper replaced the dropping funnel. The mixture is allowed to stir under ambient conditions for approximately 3 hours following the completion of hydrolysis. After the 3 hours of stirring, the reaction mixture is aged at 95 degrees Celsius for 24 hours with stirring to form a gel. The resulting gel is filtered and extracted using Soxhlet extraction with ethanol for 24 hours to form a solid. The extracted solid is dried in a vacuum oven at 50 degrees Celsius overnight.
  • FIGS. 17 and 18 are graphical representations of average NOx Conversion and standard deviation at 325 degrees Celsius and 375 degrees Celsius for (left to right) 3 percent Ag-TA; 3 percent Ag-TA with 1 percent zinc sol gel; 3 percent Ag-TA with 1 percent zinc IW; 3 percent Ag-TA with 0.5 percent zinc IW; and 3 percent Ag-TA with 0.1 percent zinc IW. FIGS. 17 and 18 show that several levels of zinc at temperatures 325 degrees Celsius and 375 degrees Celsius gave improved catalytic activity for NOx conversion compared with 3 percent Ag-TA alone.
  • Example 7 Platinum
  • Example 7 includes the preparation of 3 percent Ag-Templated Alumina with 0.05 percent platinum. A 1-liter, 3-neck round bottom flask equipped with a mechanical stirrer, reflux condenser and addition funnel is charged with Al(OsecBU)3) (50.025 g, 0.203 mol). An aliquot of 200 mL of 2-Butanol (2-BuOH) is added to the flask. The 2-BuOH is divided in half, one used to transfer the Al(OsecBU)3 and the other the rinse the remaining portion from the container walls. Following the addition to the flask, the mechanical stirrer is turned on using a low setting and the flask is charged with ethyl acetoacetate (2.655 g, 0.0204 mol), TRITON X-114 (14.099 g, 0.0226 mol) and 60 mL 2-BuOH. Platinum (II) acetylacetonate (0.0210 g, 5.34E-05 mol) is added to the flask. The solution is allowed to stir under ambient conditions for 30 minutes. During this time, of AgNO3 (0.5352 g, 0.00315 mol) is dissolved in 7.5 mL H2O and combined with 85 mL of 2-BuOH. This solution is added to the addition funnel. After 30 minutes had elapsed, the addition funnel is turned on and allowed to drip at a medium pace.
  • After the hydrolysis is complete, the stirrer is turned on to gain viscosity of the mixture and a stopper replaced the dropping funnel. The mixture is stirred under ambient conditions for approximately 3 hours following the completion of hydrolysis. After 3 hours, the reaction mixture is aged at 95 degrees Celsius for 24 hours with stirring. The resulting gel is filtered and extracted using Soxhlet extraction with ethanol for 24 hours. The extracted solid is dried in a vacuum oven at 50 degrees Celsius overnight.
  • FIG. 19 is a graphical representation of average NOx conversion and standard deviation for (left to right) each at 275 degrees Celsius, 325 degrees Celsius and 375 degrees Celsius: 3 percent Ag-TA; 3 percent Ag-TA with 0.01 percent Platinum; 3 percent Ag-TA; and 3 percent Ag-TA with 0.05 percent iridium.
  • Example 8 Rhodium
  • Example 8 includes the preparation of 3 percent Ag-Templated Alumina 0.05 percent rhodium. A 1-liter, 3-neck round bottom flask equipped with a mechanical stirrer, reflux condenser and addition funnel is charged with Al(OsecBU)3) (50.025 g, 0.203 mol). 200 mL of 2-Butanol (2-BuOH) is added to the flask. The 2-BuOH is divided in half, one used to transfer the Al(OsecBU)3 and the other the rinse the remaining portion from the container walls. Following the addition to the flask, the mechanical stirrer is turned on using a low setting and the flask is charged with ethyl acetoacetate (2.655 g, 0.0204 mol), TRITON X-114 (14.099 g, 0.0226 mol) and 60 mL 2-BuOH. Rhodium (III) acetylacetonate (0.0201 g, 5.02E-05 mol) is added to the flask. This solution is allowed to stir under ambient conditions for 30 minutes. During this time, of AgNO3 (0.5352 g, 0.00315 mol) is dissolved in 7.5 mL H2O and combined with 85 mL of 2-BuOH. The solution is added to the addition funnel. After 30 minutes had elapsed, the addition funnel is turned on and allowed to drip at a medium pace. After the hydrolysis is complete, the stirrer is turned on to gain viscosity of the mixture and a stopper replaced the dropping funnel. The mixture is stirred under ambient conditions for approximately 3 hours following the completion of hydrolysis. After 3 hours, the reaction mixture is aged at 95 degrees Celsius for 24 hours with stirring. The resulting gel is filtered and extracted using Soxhlet extraction with ethanol for 24 hours. The extracted solid is dried in a vacuum oven at 50 degree Celsius overnight.
  • FIG. 20 is a graphical representation of average NOx conversion and standard deviation at four temperatures (left to right) 275 degrees Celsius, 325 degrees Celsius, 375 degrees Celsius and 425 degrees Celsius. For each temperature (left to right) 3 percent Ag-TA; 3 percent Ag-TA with 0.01 percent rhodium; and 3 percent Ag-TA with 0.05 percent rhodium. FIG. 20 shows that depending on the temperature the 0.01 percent rhodium and the 0.05 percent rhodium (each added to 3 percent Ag-TA) had superior catalytic activity compared to 3 percent Ag-TA alone.
  • FIG. 21 is a graphical representation of average NOx conversion and standard deviation at four temperatures (left to right) 275 degrees Celsius, 325 degrees Celsius, 375 degrees Celsius and 425 degrees Celsius. For each temperature (left to right) 3 percent with Ag-TA with 0.005 percent rhodium; 3 percent Ag-TA with 0.01 percent rhodium; and 3 percent Ag-TA alone. As shown in FIG. 21, at the four temperatures tested, rhodium appeared to give catalytic activity enhancement compared to the 3 percent Ag-TA alone.
  • Additional Examples and samples are created and formed by affected the following parameters: the type of solvent, the amount of solvent, the hydrolysis rate, the reaction temperature, the amount of catalytic metal in addition to the silver, the amount of silver, the combination of the various catalytic metals (with or without silver), and the templated alumina support. These samples are tested for efficacy in the same manner as the above-disclosed samples.
  • Testing Procedures:
  • The reactor mixes gases (using mass flow controllers—MFCs, Brooks and MKS) and up to two liquids (usually water and a liquid reductant) are vaporized. The water and liquid reductant are pumped in under pressure. The gas mixture enters the heated (˜115 degrees Celsius) top box and goes into a manifold that contains 32 capillary exit tubes. The gas is restricted in the manifold and the pressure builds up to −60 psi. Backpressure indicates the same amount of gas is flowing out of each capillary. The capillaries (stainless steel) open up into tubes (INCONEL, stainless steel) where the catalyst is positioned. This zone is a copper block that can be temperature controlled.
  • The catalyst powders (25-50 mg) are held in place by quartz wool that has been wedged into the tube. Each tube can be individually sampled by controlling the two switching valves. The flow of the outlet stream is measured and recorded. The flow can be diverted through a deep oxidation catalysts (Pt/Al2O3 from Johnson Matthey) to determine N2 selectivity. The flow passes through a diluter (CAI, Model 701) that takes 25 m/min from the reactor (which generally puts out ˜35-40 mL/min) and mixes it with 1000 ml/min of N2 (˜25:1 dilution). The diluted sample is pulled though the CO/CO2 detector (CAI) by a pump in the NOx detector (CAI, Model 600 HCLD). In generally only the NOx value is recorded. It is possible to record the NO and NO2 values separately. A LABVIEW program controls many features of the reactor system. The software does not control the MFCs but their settings are recorded. The software controls the temperature of the reactor block and the switching of the values. The software records, CO, CO2 and NOx from the analyzers. After the feed is completely combusted over the Deep Oxidation Catalyst (DOC) the reductant delivery is checked by measuring CO2 level.
  • The screening conditions are as follows: gas composition: 12 percent O2, 600 ppm NO, 7 percent H2O, 1 ppm SO2 and the balance N2. The catalysts are pretreated with 7 percent H2O and 50 ppm SO2, 12 percent O2 for 7 hours at 450 degrees Celsius to “age” or sulfur soak the catalysts. The reductant used is a liquid mixture composed of: 2,2,4,Trimethylpentane (64 weight percent), octane (7 weight percent) and toluene (29 weight percent), also known as Moctane. Another liquid reductant used in a few experiments is a distillation cut (<210 degrees Celsius) of ultra low sulfur diesel (ULSD) fuel. For all the experiments mentioned using the HTS reactor, the C1:NO ratio used is 8 (C1:NO is defined as the number of carbon atoms in the reductant stream per number of NO molecules). Each run examines the catalysts at 3 different temperatures 275 degrees Celsius, 375 degrees Celsius and 425 degrees Celsius and the catalysts are usually tested in triplicates. Data is presented as percent NOx conversion by measuring the NOx concentration through tube #1 with no catalyst present and measuring the NOx concentration over the other tubes with catalysts and determining the percent change.
  • The catalysts screened in the 32-tube reactor are prepared by incipient wetness impregnation of the sized support (425-710 nanometers) with a AgNO3 solution. The volume of the AgNO3 solution used is twice the pore volume of the support and contained the correct number of moles of Ag to hit the target mole percent. The pore volume of the support is obtained from the BET measurement report. The catalysts containing 2 mole percent Ag on Norton alumina is called AgSTD and is present in every run as a control. The impregnated materials are dried in a vacuum oven at 80 degrees Celsius and calcinated in air at 600 degrees Celsius for 6 hours in a box furnace. The prepared catalysts are weighed out (˜50 mg) and placed in 2 ml GC vials until used in the reactor. The exact weight of each catalyst is measured using a Bohdan weighing robot.
  • Scale-up Reactor
  • The experimental setup is as follows. The catalyst to be tested is installed in a quartz-tube reactor (19 mm I.D.) located inside a furnace. Temperature, pressure, space velocity over the catalyst, and gas composition at the inlet of the reactor are controlled. This reactor is fully automated and experimental test matrix can be run over an extended period of time (days or weeks). Analytical lines allow for the measurement of NO, NO2 (chemiluminescence detector), CO, CO2 (IR detector), and SO2 (UV-Vis detector). Also, a deep oxidation catalytic bed located before the analytical lines can be either flown through or by-passed. When by-passed, the NOx concentration measured (NO+NO2) is referred to as “NOx concentration”. When flown through the Deep Oxidation Catalyst (DOC, Johnson-Matthey catalyst, Pt/Al2O3, SV<20000 hr−1, T=450 degrees Celsius), the NOx concentration measured (NO+NO2) is referred to as “NOt concentration”. Therefore, the difference between those two values (NOx concentration−NOt concentration) corresponds to the quantity of NOx species that reacted in the quartz-tube reactor to form new chemicals, which are oxidized back to NO or NO2 in the DOC. These nitrogen-containing species are called RONOs. RONOs are unidentified by-products of the SCR reaction of NOx to nitrogen.
  • Catalysts are tested under experimental conditions reported in Table 1. The total powder catalyst weight is 2.7 grams. The total volumetric flow rate over the catalyst is 3 SLPM.
  • The powder bed is placed at least 24″ from the inlet of the quartz tube to allow for preheating of the feed gas. The powder bed is packed between two 0.5 grams plugs of quartz wool.
  • TABLE 1
    Experimental Conditions
    X's values
    (NO) (ppm) 475, 610, 690
    (O2) percent 12 
    C1:NO 6
    H2:NO ratio 0, 3:1
    (H2O) percent 7
    Temperature 275, 375, 430
    (degrees Celsius)
    (SO2) (ppm) 0
    CO (ppm) 250 
    CO2 (percent) 0
  • Moctane, Ethylene+Propylene (C2_C3), Ultra Low Sulfur Diesel (ULSD) and Diesel Fraction 1 are used as reductants. Liquid reductants are pumped by a HPLC pump (ASI model 500 G) and vaporized/diluted at 300 degrees Celsius with nitrogen before being injected in the reactor. Gaseous reductants are metered and delivered with Mass Flow Controllers (MFCs). The amount of reductant injected is quantified by deep oxidation on Pt/Al2O3 catalyst at 450 degrees Celsius (space velocity below 20,000 hr−1) followed by the measurement of CO2 concentration in the gas stream. The assumption that full catalytic combustion of the reductants took place is validated by the fact that very low CO concentrations are measured. In addition, deep oxidation of reductants provided the C1 (ppm of molecular carbon) equivalent number (equal to CO2 concentration, in ppm), which allows for the computation of the C1/NO ratio.
  • As used herein, the terms “may” and “may be” indicate a possibility of an occurrence within a set of circumstances; a possession of a specified property, characteristic or function; and/or qualify another verb by expressing one or more of an ability, capability, or possibility associated with the qualified verb. Accordingly, usage of “may” and “may be” indicates that a modified term is apparently appropriate, capable, or suitable for an indicated capacity, function, or usage, while taking into account that in some circumstances the modified term may sometimes not be appropriate, capable, or suitable.
  • Reference is made to substances, components, or ingredients in existence at the time just before first contacted, formed in situ, blended, or mixed with one or more other substances, components, or ingredients in accordance with the present disclosure. A substance, component or ingredient identified as a reaction product, resulting mixture, or the like may gain an identity, property, or character through a chemical reaction or transformation during the course of contacting, in situ formation, blending, or mixing operation if conducted in accordance with this disclosure with the application of common sense and the ordinary skill of one in the relevant art (e.g., chemist). The transformation of chemical reactants or starting materials to chemical products or final materials is a continually evolving process, independent of the speed at which it occurs. Accordingly, as such a transformative process is in progress there may be a mix of starting and final materials, as well as intermediate species that may be, depending on their kinetic lifetime, easy or difficult to detect with current analytical techniques known to those of ordinary skill in the art.
  • Reactants and components referred to by chemical name or formula in the specification or claims hereof, whether referred to in the singular or plural, may be identified as they exist prior to coming into contact with another substance referred to by chemical name or chemical type (e.g., another reactant or a solvent). Preliminary and/or transitional chemical changes, transformations, or reactions, if any, that take place in the resulting mixture, solution, or reaction medium may be identified as intermediate species, master batches, and the like, and may have utility distinct from the utility of the reaction product or final material. Other subsequent changes, transformations, or reactions may result from bringing the specified reactants and/or components together under the conditions called for pursuant to this disclosure. In these other subsequent changes, transformations, or reactions the reactants, ingredients, or the components to be brought together may identify or indicate the reaction product or final material.
  • In describing, the products of the instant invention as a reaction product of initial materials reference is made to the initial species recited and it is to be noted that additional materials may be added to the initial mixture of synthetic precursors. These additional materials may be reactive or non-reactive. The defining characteristic of the instant invention is that the reaction product is obtained from the reaction of at least the components listed as disclosed. Non-reactive components may be added to the reaction mixture as diluents or to impart additional properties unrelated to the properties of the composition prepared as a reaction product. Thus for example finely divided solids such as pigments may be dispersed into the reaction mixture, before during or after reaction to produce a reaction product composition that additionally comprises the non-reactive component, e.g. the pigment. Additional reactive components may also be added; such components may react with the initial reactants or they may react with the reaction product; the phrase “reaction product” is intended to include those possibilities as well as including the addition of non-reactive components.
  • The embodiments described herein are examples of composition, articles, systems and methods having elements corresponding to the elements of the invention recited in the claims. This written description may enable those of ordinary skill in the art to make and use embodiments having alternative elements that likewise correspond to the elements of the invention recited in the claims. The scope of the invention thus includes articles, systems and methods that do not differ from the literal language of the claims, and further includes other articles, systems and methods with insubstantial differences from the literal language of the claims. While only certain features and embodiments have been illustrated and described herein, many modifications and changes may occur to one of ordinary skill in the relevant art. The appended claims cover all such modifications and changes.

Claims (24)

1. A composition, comprising:
a templated metal oxide substrate material having a plurality of pores; and
a catalyst material comprising a catalyst metal and silver; and the silver is present in an amount of at least about three weight percent based on a total weight of the substrate material.
2. The composition as defined in claim 1, wherein the templated metal oxide is alumina or silica-alumina.
3. The composition as defined in claim 1, wherein the templated metal oxide has periodically arranged templated pores, wherein the average diameter of the pores is in a range of from about 2 nanometers to about 100 nanometers and the pores have a periodicity in a range of from about 50 Angstrom to about 130 Angstrom.
4. The composition as defined in claim 1, wherein the templated metal oxide has a surface area greater than about 0.5 meter2/gram; wherein the templated metal oxide is present in an amount greater than about 50 mole percent of the composition; or wherein the silver is present in an amount of less than or equal to ten weight percent of a total weight of the substrate material.
5. The composition as defined in claim 1, wherein the catalyst metal comprises one or more material selected from group consisting of zirconium, iron, gallium, indium, tungsten, zinc, platinum, and rhodium.
6. The composition as defined in claim 5, wherein the catalyst metal is zirconium.
7. The composition as defined in claim 5, wherein the catalyst metal comprises iron.
8. The composition as defined in claim 5, wherein the catalyst metal comprises gallium, indium, or both gallium and indium.
9. The composition as defined in claim 8, wherein the catalyst metal comprises both gallium and indium, and they are present in a ratio such that gallium is present more than 2:1 relative to indium.
10. The composition as defined in claim 5, wherein the catalyst metal is tungsten.
11. The composition as defined in claim 5, wherein the catalyst metal is zinc.
12. The composition as defined in claim 5, wherein the catalyst metal is platinum.
13. The composition as defined in claim 5, wherein the catalyst metal is rhodium.
14. The composition as defined in claim 5, wherein the catalyst metal comprises an oxide.
15. The composition as defined in claim 1, wherein the catalyst metal is present in an amount in a range of from about 0.1 weight percent to about 3 weight percent, based on the total weight of the composition.
16. The composition as defined in claim 1, wherein the composition is free of alkaline earth metal.
17. The composition as defined in claim 1, wherein the composition is capable of reducing NOx in reactive proximity therewith without absorbing the NOx on a catalyst material surface.
18. The composition as defined in claim 1, wherein the composition has capability of reducing nitrogen oxide greater than 40 percent by volume at a temperature of about 325 degrees Celsius.
19. A method, comprising:
introducing a gas stream in a chamber that includes the composition as defined in claim 1; and
reducing nitrogen oxide present in the gas stream at a temperature that is greater than about 275 degrees Celsius.
20. The method as defined in claim 19, wherein the reducing nitrogen oxide comprises maintaining a temperature in the chamber that is greater than about 275 degrees Celsius and that is less than about 325 degrees Celsius.
21. A method, comprising:
reacting a metal alkoxide, a silver composition, a catalyst metal composition and a templating agent to form a reaction product;
hydrolyzing the reaction product to form a hydrolyzed reaction product;
condensing the hydrolysed reaction product to form a templated substrate; and
controlling the reacting, hydrolysing and condensing step to control the silver loading of the templated substrate.
22. The method as defined in claim 21, controlling the silver loading so that the silver is present in an amount of at least about three weight percent based on a total weight of the material that is the templated substrate.
23. The method as defined in claim 21, wherein the condensing step includes calcinating.
24. The method as defined in claim 21, wherein the hydrolyzing step comprises hydrolyzing the reaction product over a period that is greater than about 1 hour.
US12/362,533 2009-01-30 2009-01-30 Templated catalyst composition and associated method Abandoned US20100196237A1 (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
US12/362,533 US20100196237A1 (en) 2009-01-30 2009-01-30 Templated catalyst composition and associated method
US14/160,379 US9463439B2 (en) 2009-01-30 2014-01-21 Templated catalyst composition and associated method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
US12/362,533 US20100196237A1 (en) 2009-01-30 2009-01-30 Templated catalyst composition and associated method

Related Child Applications (1)

Application Number Title Priority Date Filing Date
US14/160,379 Division US9463439B2 (en) 2009-01-30 2014-01-21 Templated catalyst composition and associated method

Publications (1)

Publication Number Publication Date
US20100196237A1 true US20100196237A1 (en) 2010-08-05

Family

ID=42397889

Family Applications (2)

Application Number Title Priority Date Filing Date
US12/362,533 Abandoned US20100196237A1 (en) 2009-01-30 2009-01-30 Templated catalyst composition and associated method
US14/160,379 Expired - Fee Related US9463439B2 (en) 2009-01-30 2014-01-21 Templated catalyst composition and associated method

Family Applications After (1)

Application Number Title Priority Date Filing Date
US14/160,379 Expired - Fee Related US9463439B2 (en) 2009-01-30 2014-01-21 Templated catalyst composition and associated method

Country Status (1)

Country Link
US (2) US20100196237A1 (en)

Cited By (17)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20090074641A1 (en) * 2007-09-19 2009-03-19 General Electric Company Catalyst and method of manufacture
US20090263297A1 (en) * 2007-09-19 2009-10-22 General Electric Company Catalyst and method of manufacture
US20100233053A1 (en) * 2008-05-19 2010-09-16 General Electric Company Catalyst and method of manufacture
US20110047995A1 (en) * 2009-08-31 2011-03-03 General Electric Company Catalyst and method of manufacture
US20110209459A1 (en) * 2010-02-26 2011-09-01 Dan Hancu System and Method for Controlling Nitrous Oxide Emissions of an Internal Combustion Engine and Regeneration of an Exhaust Treatment Device
EP2422875A1 (en) * 2010-08-31 2012-02-29 General Electric Company Method of manufacturing a catalyst and method for preparing fuel from renewable sources using the catalyst
US8505285B2 (en) 2010-10-06 2013-08-13 General Electric Company Catalyst and method of manufacture
US8586501B2 (en) 2010-10-04 2013-11-19 General Electric Company Catalyst and method of manufacture
WO2014052480A1 (en) * 2012-09-25 2014-04-03 University Of Connecticut Mesoporous metal oxides processes for preparation thereof
WO2014052482A1 (en) * 2012-09-25 2014-04-03 University Of Connecticut Office Of Economic Development Mesoporous metal oxides and processes for preparation thereof
US8889587B2 (en) 2009-08-31 2014-11-18 General Electric Company Catalyst and method of manufacture
US20140378296A1 (en) * 2007-09-19 2014-12-25 General Electric Company Manufacture of Catalyst Compositions and Systems
US9375710B2 (en) 2007-09-19 2016-06-28 General Electric Company Catalyst and method of manufacture
US9463439B2 (en) 2009-01-30 2016-10-11 General Electric Company Templated catalyst composition and associated method
US9463438B2 (en) 2009-01-30 2016-10-11 General Electric Company Templated catalyst composition and associated method
US9545618B2 (en) 2011-06-21 2017-01-17 General Electric Company Method for preparing a catalyst composition suitable for removing sulfur from a catalytic reduction system
CN110911697A (en) * 2019-11-22 2020-03-24 深圳大学 Transition metal/nitrogen-doped porous carbon nanosphere electrocatalyst and preparation method thereof

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US11311859B2 (en) * 2016-09-12 2022-04-26 Cataler Corporation Exhaust gas purification catalyst and method for manufacturing exhaust gas purification catalyst
CN111974964A (en) * 2020-09-09 2020-11-24 苏州慧驰轻合金精密成型科技有限公司 Ultrahigh-strength high-heat-conductivity semisolid extrusion casting aluminum alloy casting and preparation process thereof

Citations (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4480050A (en) * 1982-08-02 1984-10-30 Uop Inc. Exhaust gas oxidation catalyst
US5609839A (en) * 1993-12-17 1997-03-11 N.E. Chemcat Corporation Nox removal catalyst and method of purifying exhaust gas by using the same
US6146602A (en) * 1999-02-08 2000-11-14 Ford Global Technologies, Inc. Mesoporous oxide molecular sieves for absorbing nitrogen oxides in oxidizing engine exhaust gas
US6365118B1 (en) * 1992-12-14 2002-04-02 Delphi Technologies, Inc. Reduction of NOx in the exhaust from leanOx internal combustion engines
US20030118960A1 (en) * 2001-12-21 2003-06-26 Balmer-Millar Mari Lou Lean NOx aftertreatment system
US20030134745A1 (en) * 2001-12-18 2003-07-17 Park Paul W. Metal/metal oxide doped oxide catalysts having high deNOx selectivity for lean NOx exhaust aftertreatment systems
US20060133976A1 (en) * 2004-12-22 2006-06-22 Male Jonathan L Catalyst system and method for the reduction of NOx
US7081231B1 (en) * 2000-11-08 2006-07-25 Caterpillar Inc. Method and system for the combination of non-thermal plasma and metal/metal oxide doped γ-alumina catalysts for diesel engine exhaust aftertreatment system
US7146802B2 (en) * 2004-10-07 2006-12-12 General Motors Corporation Reducing NOx emissions with a staged catalyst
US20070031310A1 (en) * 2005-08-05 2007-02-08 Lee Jong-Hwan Reduction of NOx emissions using a staged silver/alumina catalyst system
US20070101704A1 (en) * 2005-11-07 2007-05-10 Goulette David A Vehicle exhaust aftertreatment system
US20080069743A1 (en) * 2006-09-20 2008-03-20 Castellano Christopher R Catalysts, systems and methods to reduce nox in an exhaust gas stream
US7428810B2 (en) * 2006-04-25 2008-09-30 Caterpillar Inc. System for increasing efficiency of an SCR catalyst
US7431905B2 (en) * 2005-10-04 2008-10-07 General Electric Company Catalyst system and method for the reduction of NOx
US7448207B2 (en) * 2004-10-11 2008-11-11 Volvo Lastvagnar Ab System and method for reduction of nitrogen oxides from exhaust gases generated by a lean-burn combustion engine

Family Cites Families (88)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
IN170003B (en) 1985-06-28 1992-01-25 Shell Int Research
US5244852A (en) 1988-11-18 1993-09-14 Corning Incorporated Molecular sieve-palladium-platinum catalyst on a substrate
US5302319A (en) * 1991-01-07 1994-04-12 United Technologies Corporation Preparation of sol gel composition for electrophoresis
JPH04354536A (en) 1991-05-29 1992-12-08 Asahi Glass Co Ltd Catalyst for decomposition of nitrogen oxide and method for decomposing nitrogen oxide
DE4128629A1 (en) 1991-08-29 1993-03-04 Basf Ag SILVER-CONTAINING CARRIER CATALYST AND METHOD FOR THE CATALYTIC DECOMPOSITION OF NITROGEN MONOXIDE
EP0577438B1 (en) 1992-07-03 2001-05-16 Kabushiki Kaisha Riken Exhaust gas cleaner and method of cleaning exhaust gas
JPH06126134A (en) 1992-10-13 1994-05-10 Osaka Gas Co Ltd Method for purification of nitrogen oxide in exhaust gas
JPH06343829A (en) 1993-06-08 1994-12-20 Kao Corp Exhaust gas purifying method and catalyst used therefor
JPH0763048A (en) 1993-08-20 1995-03-07 Ngk Insulators Ltd Exhaust emission control system and method thereof
JP3440290B2 (en) 1993-08-26 2003-08-25 独立行政法人産業技術総合研究所 Exhaust gas purification method
US5510306A (en) 1993-12-29 1996-04-23 Shell Oil Company Process for isomerizing linear olefins to isoolefins
KR0136893B1 (en) 1994-11-03 1998-04-25 강박광 Selective catalytic reduction of nitrogen oxide
US5714130A (en) 1994-11-28 1998-02-03 Kabushiki Kaisha Riken Exhaust gas cleaner and method for cleaning exhaust gas
IT1271312B (en) 1994-12-21 1997-05-27 Enirisorse Spa SOL-GEL PROCESS FOR OBTAINING SPHERES, MICROSPHERES OR COATINGS OF CELL-SHAPED MONOLITES, CONSTITUTED FROM PURE OR ZIRCONIUM OXIDE WITH OTHER OXIDES, USEFUL AS CATALYSTS OR SUPPORTS FOR CATALYSTS
US5772972A (en) 1995-01-09 1998-06-30 Ford Global Technologies, Inc. Catalyst/hydrocarbon trap hybrid system
US5622684A (en) 1995-06-06 1997-04-22 Board Of Trustees Operating Michigan State University Porous inorganic oxide materials prepared by non-ionic surfactant templating route
US5770778A (en) 1995-07-28 1998-06-23 Eastman Kodak Company Purification of ethylene glycol recovered from polyester resins
JP3494331B2 (en) 1996-02-02 2004-02-09 トヨタ自動車株式会社 Exhaust gas purification catalyst and method for producing the same
US6169119B1 (en) * 1997-02-14 2001-01-02 Reliance Electric Technologies, Llc Metal oxide sols and process for making the same
US5922294A (en) * 1997-03-10 1999-07-13 Ford Global Technologies, Inc. High surface area, thermally stabilized titania automotive catalyst support
DE19725092A1 (en) 1997-06-13 1998-12-17 Itt Mfg Enterprises Inc Hydraulic unit
DE19730126A1 (en) 1997-07-14 1999-01-21 Basf Ag Solid surface containing alumina
JPH1147602A (en) 1997-08-07 1999-02-23 Mazda Motor Corp Catalyst for purification of exhaust gas and its production
JP3417309B2 (en) 1997-10-28 2003-06-16 トヨタ自動車株式会社 Hydrocarbon adsorbent
WO1999029400A1 (en) 1997-12-10 1999-06-17 Ab Volvo Porous material, method and arrangement for catalytic conversion of exhaust gases
US6528034B1 (en) 1999-11-09 2003-03-04 Board Of Trustees Of Michigan State University Ultra-stable lamellar mesoporous silica compositions and process for the prepration thereof
GB0020287D0 (en) 2000-08-17 2000-10-04 Aea Technology Plc The catalytic treatment of gases
US6800586B2 (en) 2001-11-23 2004-10-05 Engelhard Corporation NOx reduction composition for use in FCC processes
US6703343B2 (en) 2001-12-18 2004-03-09 Caterpillar Inc Method of preparing doped oxide catalysts for lean NOx exhaust
EP1340541A1 (en) 2002-02-28 2003-09-03 Corning Incorporated Structured catalysts incorporating thick washcoats and method of preparation thereof
US7214643B2 (en) 2002-03-22 2007-05-08 Kabushiki Kaisha Toyota Chuo Kenkyusho Metal oxide and method for producing the same, and catalyst
US20030186805A1 (en) 2002-03-28 2003-10-02 Vanderspurt Thomas Henry Ceria-based mixed-metal oxide structure, including method of making and use
FR2842419A1 (en) 2002-07-19 2004-01-23 Oreal A method of broadening the UV absorption spectrum of an organic UVA filter used in cosmetic composition to protect against solar radiation by immobilizing it in a matrix produced by sol-gel from a silicon alkoxide and a surfactant
US6660683B1 (en) 2002-10-21 2003-12-09 W.R. Grace & Co.-Conn. NOx reduction compositions for use in FCC processes
EP1594594B1 (en) 2003-02-12 2012-05-23 Delphi Technologies, Inc. SYSTEM FOR NOx ABATEMENT
ITMI20031360A1 (en) * 2003-07-03 2005-01-04 Enitecnologie Spa POROUS SOLID CATALYTICALLY ACTIVE AMORPHOUS AND PROCESS FOR ITS PREPARATION.
GB0318776D0 (en) 2003-08-09 2003-09-10 Johnson Matthey Plc Lean NOx catalyst
US7108835B2 (en) 2003-10-08 2006-09-19 Rentech, Inc. Fischer-tropsch slurry reactor cooling tube arrangement
US7541010B2 (en) 2003-12-19 2009-06-02 Caterpillar Inc. Silver doped catalysts for treatment of exhaust
FR2866871B1 (en) 2004-02-26 2007-01-19 Rhodia Chimie Sa COMPOSITION BASED ON ZIRCONIUM, PRASEODYM, LANTHAN OR NEODYME OXIDES, PREPARATION METHOD AND USE IN A CATALYTIC SYSTEM
US20050198092A1 (en) 2004-03-02 2005-09-08 Jia-Pei Shen Fast fourier transform circuit having partitioned memory for minimal latency during in-place computation
JP2006021100A (en) 2004-07-07 2006-01-26 Nippon Gas Gosei Kk Catalyst for manufacture of liquefied petroleum gas and method of manufacturing liquefied petroleum gas using it
JP2006079738A (en) 2004-09-10 2006-03-23 Matsushita Electric Ind Co Ltd Disk device
US7371358B2 (en) 2004-10-25 2008-05-13 The United States Of America As Represented By The Administrator Of The National Aeronautics And Space Administration Catalyst for treatment and control of post-combustion emissions
JP4494417B2 (en) 2004-11-01 2010-06-30 三菱電機株式会社 Voice coil motor control device, driving method thereof, and imaging device
CN100546710C (en) * 2005-01-24 2009-10-07 金文申有限公司 Metallic composite
KR100577837B1 (en) 2005-01-27 2006-05-12 (주)이엔디솔루션 The catalyst and apparatus for reducing exhaust gas of diesel engine
WO2006093802A2 (en) 2005-02-28 2006-09-08 Catalytic Solutions, Inc. Catalyst and method for reducing nitrogen oxides in exhaust streams with hydrocarbons or alcohols
US7743602B2 (en) 2005-06-21 2010-06-29 Exxonmobil Research And Engineering Co. Reformer assisted lean NOx catalyst aftertreatment system and method
US7803338B2 (en) 2005-06-21 2010-09-28 Exonmobil Research And Engineering Company Method and apparatus for combination catalyst for reduction of NOx in combustion products
US7867598B2 (en) 2005-08-31 2011-01-11 Ngk Insulators, Ltd. Honeycomb structure and honeycomb catalytic body
US7655203B2 (en) 2005-10-04 2010-02-02 General Electric Company Multi-component catalyst system and method for the reduction of NOx
KR100871898B1 (en) 2005-10-28 2008-12-05 에스케이에너지 주식회사 Exhaust gas purifying device for diesel engine
US20070149385A1 (en) 2005-12-23 2007-06-28 Ke Liu Catalyst system for reducing nitrogen oxide emissions
EP1832345A1 (en) 2006-03-10 2007-09-12 Asahi Kasei Kabushiki Kaisha Catalyst for exhaust gas purification
US20080085231A1 (en) 2006-10-05 2008-04-10 Frederic Vitse System and method for reducing nitrogen oxides emissions
BRPI0718969A2 (en) 2006-11-16 2014-01-07 Albemarle Netherlands Bv A process for converting the molybdenum sulphide feedstock into a purified molybdenum trioxide product; AND PURIFIED SOLID MOLIBDENE THYROXIDE
US7709414B2 (en) 2006-11-27 2010-05-04 Nanostellar, Inc. Engine exhaust catalysts containing palladium-gold
TWI449572B (en) 2006-11-29 2014-08-21 Umicore Shokubai Japan Co Ltd Oxidation catalyst and the oxidation catalyst using an exhaust gas purification system
US20080131345A1 (en) 2006-11-30 2008-06-05 Frederic Vitse Multi-bed selective catalytic reduction system and method for reducing nitrogen oxides emissions
US7891171B2 (en) 2006-12-05 2011-02-22 GM Global Technology Operations LLC Hybrid catalyst for NOx reduction using fuel hydrocarbons as reductant
US7494634B2 (en) 2007-01-10 2009-02-24 General Electric Company Reduction of nitrogen oxides using multiple split streams
US20100150801A1 (en) 2007-09-19 2010-06-17 General Electric Company FORMED CATALYST FOR NOx REDUCTION
US8871669B2 (en) 2008-05-19 2014-10-28 General Electric Company Catalyst and method of manufacture
US8530369B2 (en) 2007-09-19 2013-09-10 General Electric Company Catalyst and method of manufacture
US20090075813A1 (en) 2007-09-19 2009-03-19 General Electric Company Catalyst and method of manufacture
US20090263297A1 (en) 2007-09-19 2009-10-22 General Electric Company Catalyst and method of manufacture
US20100143227A1 (en) 2008-12-05 2010-06-10 General Electric Company MIXED CATALYST FOR NOx REDUCTION AND METHODS OF MANUFACTURE THEREOF
US20110047995A1 (en) 2009-08-31 2011-03-03 General Electric Company Catalyst and method of manufacture
US20090318283A1 (en) 2008-06-20 2009-12-24 General Electric Company Catalyst composition and method
US20100095591A1 (en) 2008-10-20 2010-04-22 General Electric Company Emissions control system and method
EP2189217A1 (en) * 2008-11-17 2010-05-26 Technical University of Denmark Nanoparticular metal oxide/anatase catalysts.
US20100190639A1 (en) * 2009-01-28 2010-07-29 Worsley Marcus A High surface area, electrically conductive nanocarbon-supported metal oxide
US20100196236A1 (en) 2009-01-30 2010-08-05 General Electric Company Templated catalyst composition and associated method
US20100196237A1 (en) 2009-01-30 2010-08-05 General Electric Company Templated catalyst composition and associated method
US8353155B2 (en) 2009-08-31 2013-01-15 General Electric Company Catalyst and method of manufacture
US8889587B2 (en) 2009-08-31 2014-11-18 General Electric Company Catalyst and method of manufacture
US20110120100A1 (en) 2009-11-24 2011-05-26 General Electric Company Catalyst and method of manufacture
US20110152068A1 (en) 2009-12-17 2011-06-23 General Electric Company Processing of high surface area oxides
US20110152064A1 (en) 2009-12-17 2011-06-23 General Electric Company Processing of high surface area oxides
US8476187B2 (en) 2010-01-06 2013-07-02 General Electric Company Process for preparing catalyst powder
US20110209466A1 (en) 2010-02-26 2011-09-01 General Electric Company Catalyst composition and catalytic reduction system comprising yttrium
US20120047877A1 (en) 2010-08-31 2012-03-01 General Electric Company Exhaust treatment system and method of operation
US8101145B1 (en) 2010-08-31 2012-01-24 General Electric Company Exhaust treatment system and method of operation
US8586501B2 (en) 2010-10-04 2013-11-19 General Electric Company Catalyst and method of manufacture
US8505285B2 (en) 2010-10-06 2013-08-13 General Electric Company Catalyst and method of manufacture
US20120093703A1 (en) 2010-10-13 2012-04-19 General Electric Company Catalyst and method of manufacture
US20120329644A1 (en) 2011-06-21 2012-12-27 General Electric Company Catalyst composition and catalytic reduction system

Patent Citations (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4480050A (en) * 1982-08-02 1984-10-30 Uop Inc. Exhaust gas oxidation catalyst
US6365118B1 (en) * 1992-12-14 2002-04-02 Delphi Technologies, Inc. Reduction of NOx in the exhaust from leanOx internal combustion engines
US5609839A (en) * 1993-12-17 1997-03-11 N.E. Chemcat Corporation Nox removal catalyst and method of purifying exhaust gas by using the same
US6146602A (en) * 1999-02-08 2000-11-14 Ford Global Technologies, Inc. Mesoporous oxide molecular sieves for absorbing nitrogen oxides in oxidizing engine exhaust gas
US7081231B1 (en) * 2000-11-08 2006-07-25 Caterpillar Inc. Method and system for the combination of non-thermal plasma and metal/metal oxide doped γ-alumina catalysts for diesel engine exhaust aftertreatment system
US20030134745A1 (en) * 2001-12-18 2003-07-17 Park Paul W. Metal/metal oxide doped oxide catalysts having high deNOx selectivity for lean NOx exhaust aftertreatment systems
US20030118960A1 (en) * 2001-12-21 2003-06-26 Balmer-Millar Mari Lou Lean NOx aftertreatment system
US7146802B2 (en) * 2004-10-07 2006-12-12 General Motors Corporation Reducing NOx emissions with a staged catalyst
US7448207B2 (en) * 2004-10-11 2008-11-11 Volvo Lastvagnar Ab System and method for reduction of nitrogen oxides from exhaust gases generated by a lean-burn combustion engine
US20060133976A1 (en) * 2004-12-22 2006-06-22 Male Jonathan L Catalyst system and method for the reduction of NOx
US20070031310A1 (en) * 2005-08-05 2007-02-08 Lee Jong-Hwan Reduction of NOx emissions using a staged silver/alumina catalyst system
US7396517B2 (en) * 2005-08-05 2008-07-08 Gm Global Technology Operations, Inc. Reduction of NOx emissions using a staged silver/alumina catalyst system
US7431905B2 (en) * 2005-10-04 2008-10-07 General Electric Company Catalyst system and method for the reduction of NOx
US20070101704A1 (en) * 2005-11-07 2007-05-10 Goulette David A Vehicle exhaust aftertreatment system
US7428810B2 (en) * 2006-04-25 2008-09-30 Caterpillar Inc. System for increasing efficiency of an SCR catalyst
US20080069743A1 (en) * 2006-09-20 2008-03-20 Castellano Christopher R Catalysts, systems and methods to reduce nox in an exhaust gas stream

Cited By (23)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US9375710B2 (en) 2007-09-19 2016-06-28 General Electric Company Catalyst and method of manufacture
US20090263297A1 (en) * 2007-09-19 2009-10-22 General Electric Company Catalyst and method of manufacture
US20140378296A1 (en) * 2007-09-19 2014-12-25 General Electric Company Manufacture of Catalyst Compositions and Systems
US20090074641A1 (en) * 2007-09-19 2009-03-19 General Electric Company Catalyst and method of manufacture
US9272271B2 (en) * 2007-09-19 2016-03-01 General Electric Company Manufacture of catalyst compositions and systems
US8530369B2 (en) * 2007-09-19 2013-09-10 General Electric Company Catalyst and method of manufacture
US20100233053A1 (en) * 2008-05-19 2010-09-16 General Electric Company Catalyst and method of manufacture
US8871669B2 (en) 2008-05-19 2014-10-28 General Electric Company Catalyst and method of manufacture
US9463438B2 (en) 2009-01-30 2016-10-11 General Electric Company Templated catalyst composition and associated method
US9463439B2 (en) 2009-01-30 2016-10-11 General Electric Company Templated catalyst composition and associated method
US20110047995A1 (en) * 2009-08-31 2011-03-03 General Electric Company Catalyst and method of manufacture
US8889587B2 (en) 2009-08-31 2014-11-18 General Electric Company Catalyst and method of manufacture
US8459010B2 (en) * 2010-02-26 2013-06-11 General Electric Company System and method for controlling nitrous oxide emissions of an internal combustion engine and regeneration of an exhaust treatment device
US20110209459A1 (en) * 2010-02-26 2011-09-01 Dan Hancu System and Method for Controlling Nitrous Oxide Emissions of an Internal Combustion Engine and Regeneration of an Exhaust Treatment Device
EP2422875A1 (en) * 2010-08-31 2012-02-29 General Electric Company Method of manufacturing a catalyst and method for preparing fuel from renewable sources using the catalyst
US8586501B2 (en) 2010-10-04 2013-11-19 General Electric Company Catalyst and method of manufacture
US8505285B2 (en) 2010-10-06 2013-08-13 General Electric Company Catalyst and method of manufacture
US9545618B2 (en) 2011-06-21 2017-01-17 General Electric Company Method for preparing a catalyst composition suitable for removing sulfur from a catalytic reduction system
WO2014052482A1 (en) * 2012-09-25 2014-04-03 University Of Connecticut Office Of Economic Development Mesoporous metal oxides and processes for preparation thereof
WO2014052480A1 (en) * 2012-09-25 2014-04-03 University Of Connecticut Mesoporous metal oxides processes for preparation thereof
US9452933B2 (en) 2012-09-25 2016-09-27 University Of Connecticut Mesoporous metal oxides and processes for preparation thereof
US9908103B2 (en) 2012-09-25 2018-03-06 University Of Connecticut Mesoporous metal oxides and processes for preparation thereof
CN110911697A (en) * 2019-11-22 2020-03-24 深圳大学 Transition metal/nitrogen-doped porous carbon nanosphere electrocatalyst and preparation method thereof

Also Published As

Publication number Publication date
US20140199223A1 (en) 2014-07-17
US9463439B2 (en) 2016-10-11

Similar Documents

Publication Publication Date Title
US9463439B2 (en) Templated catalyst composition and associated method
US9463438B2 (en) Templated catalyst composition and associated method
US8530369B2 (en) Catalyst and method of manufacture
Costa et al. Mechanistic aspects of the H2-SCR of NO on a novel Pt/MgO− CeO2 catalyst
JP5584116B2 (en) Metal-doped zeolite and process for producing the same
CA2666550C (en) Vanadium-free catalyst for selective catalytic reduction and method of production thereof
RU2595336C2 (en) Method of producing zeolites and zeolite-like structures doped with metals, and methods for use thereof for catalytic reduction of nitrogen oxides
US20120093703A1 (en) Catalyst and method of manufacture
JP7222996B2 (en) SCR catalyst
CN107398298A (en) Copper is directly exchanged into Na+Method in type chabazite molecular sieve, and catalyst, system and method
US20140294710A1 (en) Method For Preparing A Catalyst Composition Suitable For Removing Sulfur From A Catalytic Reduction System
BRPI1104360B1 (en) CATALYTIC COMPOSITION
CN103551141A (en) Pt/MOx catalyst and application thereof in toluene catalytic combustion
CN103180041A (en) Copper containing zsm-34, off and/or eri zeolitic material for selective reduction of nox
CN106334577A (en) Preparation method of Mo modified Cu-SSZ-13 catalyst
Kwon et al. Influence of support composition on enhancing the performance of Ce-V on TiO2 comprised tungsten-silica for NH3-SCR
CN104324728B (en) Mesoporous composite oxide catalyst for purifying tail gases and preparation method thereof
CN104801335A (en) Zr-Ce-Mn/ZSM-5 complex oxide catalyst adopting NH3 to reduce NOx at low temperature as well as preparation method of Zr-Ce-Mn/ZSM-5 complex oxide catalyst
JP2010142688A (en) Catalyst for selective catalytic reduction of nitrogen oxide
CA3082500A1 (en) Scr catalyst
JP2005238196A (en) Catalyst for cleaning nitrogen oxide, cleaning method for nitrogen oxide using it and nitrogen oxide cleaning apparatus
US20100086457A1 (en) Catalyst and method of manufacture
EP2474358B1 (en) Catalyst and Method of Manufacture
Andijani NH3-SCR DRIFTS Study for Mn-Based Catalyst Activity and Reaction Pathway over Unprotected and Zeolite-protected Catalyst
CN104801336A (en) Zr-Mn-Fe/ZSM-5 complex oxide catalyst adopting NH3 to reduce NOx at low temperature as well as preparation method of Zr-Mn-Fe/ZSM-5 complex oxide catalyst

Legal Events

Date Code Title Description
AS Assignment

Owner name: GENERAL ELECTRIC COMPANY, NEW YORK

Free format text: ASSIGNMENT OF ASSIGNORS INTEREST;ASSIGNORS:YIN, MING;LEWIS, LARRY NEIL;HANCU, DAN;AND OTHERS;SIGNING DATES FROM 20090121 TO 20090123;REEL/FRAME:022179/0595

STCB Information on status: application discontinuation

Free format text: ABANDONED -- AFTER EXAMINER'S ANSWER OR BOARD OF APPEALS DECISION