GB2056424A - Decomposition of ozone - Google Patents

Decomposition of ozone Download PDF

Info

Publication number
GB2056424A
GB2056424A GB8024800A GB8024800A GB2056424A GB 2056424 A GB2056424 A GB 2056424A GB 8024800 A GB8024800 A GB 8024800A GB 8024800 A GB8024800 A GB 8024800A GB 2056424 A GB2056424 A GB 2056424A
Authority
GB
United Kingdom
Prior art keywords
process according
ozone
support
catalyst
layer
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.)
Granted
Application number
GB8024800A
Other versions
GB2056424B (en
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.)
Johnson Matthey PLC
Original Assignee
Johnson Matthey PLC
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 Johnson Matthey PLC filed Critical Johnson Matthey PLC
Publication of GB2056424A publication Critical patent/GB2056424A/en
Application granted granted Critical
Publication of GB2056424B publication Critical patent/GB2056424B/en
Expired legal-status Critical Current

Links

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
    • B01J23/16Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/32Manganese, technetium or rhenium
    • B01J23/34Manganese
    • 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
    • B01D53/8671Removing components of defined structure not provided for in B01D53/8603 - B01D53/8668
    • B01D53/8675Ozone
    • 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
    • B01J23/14Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of germanium, tin or lead
    • 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
    • B01J23/40Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals of the platinum group metals
    • 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
    • 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
    • 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
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/74Iron group metals
    • 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
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • 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
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/89Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals
    • 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
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/89Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals
    • B01J23/8933Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals also combined with metals, or metal oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • 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
    • B01J37/024Multiple impregnation or coating
    • B01J37/0244Coatings comprising several layers

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

A process for the removal of ozone from a mixture of gases, containing ozone, comprises passing the mixture of gases over a catalyst such that at least a portion of the ozone undergoes catalytic decomposition into oxygen, the said catalyst comprising catalytic material including one or more of Pt, Ru, Rh, Pd, Ir, Os, Fe, Co, Ni, Ag, Mn and Sn alloys, mixtures and compounds containing one or more of these metals.

Description

SPECIFICATION Ozone removal This invention relates to the decomposition of ozone and in particular to the catalytic decomposition of ozone.
Ozone is thermodynamically unstable and will decompose slowly at 2500C in the absence of a catalyst. The odour of ozone is perceptible at a concentration of less than 1 ppm in air. At concentrations greater than 2 ppm ozone causes irritation in the respiratory tract and damage to tissues occurs at higher concentrations. The presence of ozone, even in small concentrations, in the environment is undesirable.
Ozone may be removed from a gas stream by a number of methods such as gas scrubbing, thermal decomposition and gas adsorption. Apparatus for either gas scrubbing or gas adsorption requires maintenance and it is not always suitable for use when space or weight is at a premium.
Ozone is often produced as an unwanted by-product in photocopiers and similar apparatus which can result in oxidation of metal components. It may also be present in such a concentration that people working in the vicinity may be affected. Ozone is sometimes used in the treatment of sewage and a quantity of it may remain at the end of the treatment. The gas, ozone may also be found in the vicinity of arc lamps, welding and any high voltage sources.
Ozone is present in the air at heights above 25,000 feet. At heights from 25,000 to 30,000, for example, its concentration will be between 0 and 20 ppm and at 30,000 to 55,000 feet between 20 and 20,000 ppm. Air for the cabin of an aircraft normally enters via a primary compressor of one or more of the aircraft engines, passes through the cabin and is released to the atmosphere by a valve. This controls the pressure of the air in the cabin which is normally kept at approximately 63 cm Hg, equivalent to the air pressure at a height of 5,000 feet. Since a number of aircraft cruise at between 25,000 and 30,000 feet and there is a high through-put of air through the cabin, the passengers and crew are exposed to above average concentrations of ozone.
An object of the present invention is to remove at least a portion of any ozone present in a gas stream.
According to the present invention a process for the removal of ozone from a mixture of gases, containing ozone, comprises passing the mixture of gases over a catalyst such that at least a portion of the ozone undergoes catalytic decomposition into oxygen, the said catalyst comprising catalytic material including one or more members of the group consisting of Pt, Ru, Rh, Pd, Ir, Os, Fe, Co, Ni, Ag, Mn and Sn alloys, mixtures and compounds containing one or more of these metals.
The catalytic material may be deposited on a ceramic or metal support and a layer of refractory metal oxide may be interposed between the catalytic material and the support.
The layer of refractory metal oxide, the so-called 'washcoat' may comprise one or more oxides of B, Al, Ba, Sr, Ca, Mg, Be, Si, Ti, Zr, Sc, Y and the rare earths. Preferably the washcoat loading should be between 0.2 g/cu.in. and 2 g/cu.in. of the support and we particularly prefer the loading to be between 0.4 g/cu.in. and 1 g/cu.in. The catalyst loading of the platinum group metals is preferably within the range 20 to 200 grams per cubic foot whereas the loading of the remaining catalyst metals listed above is preferably within the range 50 to 1 ,000 grams per cubic foot considered reiative-to the weight of the washcoated support.
The support which may comprise channels extending from one face to an opposite face may be made from a ceramic material such as cordierite or a base metal or a platinum group metal or an alloy containing a platinum group metal. Preferably, the support is made from an oxidation resistant metal or alloy and we particularly prefer Kanthal D or an iron alloy containing chromium and aluminium such as Fecralloy (Registered Trade Mark). The composition of Kanthal D is (% w/w) chromium 23%, cobalt 0.5-2%, aluminium 0.7% and balance iron.
The cell density of the support, that is, the number of cells or channels across the face of the support, is preferably 200 cells/sq. in. and above we prefer 350 cells/sq. in. and above.
The preferred catalytic material is chosen from the group consisting of Pt, Pd, Fe, Ag and Mn and, of these, we particularly prefer Pt, Ag and Mn.
The catalytic material may be or may be derived from an integral part of the support. When the support contains one or more platinum group metals, for example, these may constitute the catalytic material. Similarly when the support is of an alloy containing iron, iron compounds formed on the surface by the corrosion of the metal may act as catalytic material.
To study the parameters involved in the catalytic decomposition of ozone a number of catalysts were tested in a tubular reaction. The catalyst samples comprised a catalytic material deposited on a metal support of Fecralloy having the composition of (% w/w) chromium 15.0%, aluminium 4.5 to 4.8%, yttrium 0.4 to 0.5% and balance iron), 1 inch long and 2 inches in diameter, the said support carrying an alumina washcoat. The loading of the washcoat was 0.7 g/cu.in. In the tubular reactor, a stream of gases containing ozone was passed through the catalyst. In order to do this, a gas stream containing a mixture of nitrogen and oxygen was first passed over an electric heater, to enable the temperature of the gases to be adjusted, before ozone, produced by high voltage discharge, was added to the gas stream.
The concentration of the ozone present in the gas stream was substantially 1.5 ppm. This concentration was measured by a Dasibi, model 1003, ozone analyser, before and after the catalyst. The space volocitywas 325,000 hr#1 and the gas pressure 15 p.s.i.g. (29.7 p.s.i.a.).
A series of test were conducted with samples of catalyst employing different catalytic materials.
The cell density of the supports used was 400 cells/sq. in. and the temperature of the gas was at 150-0 C.
The results are given in graphical form in the attached figures 1 to 22 and certain details of the tests and the figures in which the results are displayed, are set forth in the following tables 1, 2 and 3.
TABLE 1
Loading of Catalytic Catalytic Material Deposited Material - g/cu.ft.
on the Washcoated Support of Washcoated Support Fig.
Platinum 120 1 Platinum 120 2 5.5% Rh, 94.5% Pt. 120 3 35% Rh, 65% Pt 120 4 Platinum and Silver Pt 120 + Ag 500 5 Palladium 120 6 33, > 0 Pd 662/,0/0 Pt 120 7 Silver 500 8 Manganese dioxide (MnO2) 500 9 Manganese sesquioxide (Mn2Oa) 250 10 Triiron tetroxide (Fe3O4) 375 11 Table 2 below, relates to a series of tests conducted with platinum as the catalytic material at a loading of 120 g/cu.ft. on a number of supports with various cell densities. The temperature was kept at 1 500C.
TABLE 2
Cell Density in Cells/Sq. in Fig.
180 12 400 1 550 - 13 1200 14 These results are summarised in Figure 1 5, which is a graph of ozone conversion vs. cell density.
Another series of tests was conducted with platinum as the catalytic material at a loading of 120 g/cu.ft. on supports with a cell density of 400 cells/sq.in. The temperature of the stream of gases was varied, as shown in Table 3.
TABLE 3
Temperature of Gas Stream, C Fig.
20 16 50 17 80 18 125 19 150 1 200 20 250 21 Finally these results are summarised in Figure 22, which is a graph of ozone conversion vs.
temperature.
In all the foregoing tests, the maximum back pressure of the support was 8 mm Hg. This low back pressure is one of the advantages to be gained by using metal supports. A further advantage of these supports is that they may more easily be constructed with cell densities in excess of 500 cells per square inch, for example, than ceramic supports.

Claims (10)

1. A process for the removal of ozone from a mixture of gases, containing ozone, comprises passing the mixture of gases over a catalyst such that at least a portion of the ozone undergoes catalytic decomposition into oxygen, the said catalyst comprising catalytic material including one or more members of the group consisting of Pt, Ru, Rh, Pd, Ir, Os, Fe, Co, Ni, Ag, Mn and Sn and alloys, mixtures and compounds containing one or more of these metals.
2. A process according to claim 1 wherein the catalytic material is deposited on a ceramic or metallic support.
3. A process according to claim 2 wherein the support carries a first layer of a refractory metal oxide upon which a second layer of the catalytic material is deposited.
4. A process according to claim 3 wherein the refractory metal oxide layer comprises one or more of the oxides of B, Al, Ba, Sr, Ca, Mg, Be, Si, Ti, Zr, Sc, Y and the rare earths.
5. A process according to claim 3 wherein the loading of the first layer of refractory metal oxide falls within the range 0.2 g/cm inch and 2 g/cu. inch of the support.
6. A process according to claim 5 wherein the loading of the first layer of refractory metal oxide falls within the range 0.4 g/cm inch and 1 g/cm inch.
7. A process according to any one of claims 2 to 6 wherein the catalyst loading relative to the total weight of the support and the first layer falls within the range 20 to 200 g/cm foot for Pt, Ru, Rh, Pd, Ir and Os and within the range 50 to 1000 g/cu foot for Fe, Co, Ni, Ag, Mn and Sn.
8. A process according to any preceding claim wherein the substrate is made from an oxidation resistant alloy comprising, apart from impurities, chromium 23%, cobalt 0.5-20%, aluminium 0.7%, balance iron.
9. A process according to any one of claims 1 to 8 wherein the substrate is made from an oxidation resistant alloy comprising, apart from impurities, chromium 1 5%, aluminium 4.5 to 4.8%, yttrium 0.4 to 0.5% and balance iron.
10. A process according to claim 8 or claim 9 wherein the catalyst support has a cell density of at least 200 cells per square inch.
GB8024800A 1979-08-08 1980-07-29 Decomposition of ozone Expired GB2056424B (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
GB7927702 1979-08-08
GB7930980 1979-09-06

Publications (2)

Publication Number Publication Date
GB2056424A true GB2056424A (en) 1981-03-18
GB2056424B GB2056424B (en) 1983-07-06

Family

ID=26272480

Family Applications (1)

Application Number Title Priority Date Filing Date
GB8024800A Expired GB2056424B (en) 1979-08-08 1980-07-29 Decomposition of ozone

Country Status (5)

Country Link
CA (1) CA1152969A (en)
DE (1) DE3029948A1 (en)
FR (1) FR2462928A1 (en)
GB (1) GB2056424B (en)
SE (1) SE8005540L (en)

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2142324A (en) * 1983-06-29 1985-01-16 Teledyne Ind A method of removing ozone from air
US4619821A (en) * 1985-12-02 1986-10-28 Amoco Corporation Ozone decomposition
GB2210607A (en) * 1987-04-29 1989-06-14 Ricoh Kk Ozone decomposing material
US5145657A (en) * 1987-01-21 1992-09-08 Nippon Shokubai Kagaku Kogyo Co., Ltd. Method for purification of gas
US5232886A (en) * 1988-11-28 1993-08-03 Sakai Chemical Industry Co., Ltd. Catalysts and methods for ozone decomposition
US5256377A (en) * 1987-04-29 1993-10-26 Ricoh Company, Ltd. Ozone decomposing material and ozone decomposing apparatus using the ozone decomposing material
US5286700A (en) * 1990-09-29 1994-02-15 Nippon Shokubai Co., Ltd. Catalyst and method of preparing the catalyst
WO2000069009A2 (en) * 1999-04-27 2000-11-16 Symyx Technologies, Inc. Platinum-ruthenium-palladium-osmium alloy for use as a fuel cell catalyst
US6200542B1 (en) * 1995-01-20 2001-03-13 Engelhard Corporation Method and apparatus for treating the atmosphere
US6586359B1 (en) 1998-03-23 2003-07-01 Engelhard Corporation Catalytic material for treating pollutant-containing gases
EP1336997A2 (en) * 2002-02-19 2003-08-20 Samsung Electronics Co., Ltd. Metal catalyst based on Pt-Ru, a fuel cell electrode, and DMFC
US6818254B1 (en) 1995-01-20 2004-11-16 Engelhard Corporation Stable slurries of catalytically active materials
US7473402B2 (en) * 2004-03-26 2009-01-06 Honeywell International, Inc. Ozone removal system and method for low and high temperature operation
CN107456978A (en) * 2017-09-01 2017-12-12 深圳市高斯宝电气技术有限公司 A kind of ozone decomposition catalyst and preparation method thereof

Families Citing this family (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4343776A (en) * 1980-12-22 1982-08-10 Engelhard Corporation Ozone abatement catalyst having improved durability and low temperature performance
US4871709A (en) * 1987-07-14 1989-10-03 Nikki-Universal Co., Ltd. Ozone cracking catalyst
DE4041088A1 (en) * 1990-12-21 1992-07-02 Afs Entwicklungs & Vertriebs G Ozone removal from gas mixt. by filtering through two catalysts - first platinum@ to convert reactive gas to inert gas, then catalyst converting ozone to oxygen@
US5422331A (en) * 1994-02-25 1995-06-06 Engelhard Corporation Layered catalyst composition
US6214303B1 (en) 1995-01-20 2001-04-10 Engelhard Corporation Method and apparatus for treating the atmosphere
ATE216280T1 (en) 1995-01-20 2002-05-15 Engelhard Corp DEVICE FOR REMOVING CONTAMINANTS FROM AMBIENT AIR IN THE ENGINE HOOD OF A VEHICLE
JP3286134B2 (en) * 1995-10-12 2002-05-27 ファイラックインターナショナル株式会社 Ceramic catalyst for reforming fluid fuel
CN1104956C (en) * 1997-03-25 2003-04-09 市村富久代 Fluid fuel reforming ceramic catalysts and their manufacturing methods
AU5326099A (en) * 1998-09-08 2000-03-27 Engelhard Corporation Catalyst composition for the decomposition of ozone

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3433580A (en) * 1965-04-06 1969-03-18 Beckman Instruments Inc Ozone scavenger
DE2537090C3 (en) * 1975-08-20 1980-07-24 Institut Fisitscheskoj Chimii Imeni L.V. Pisarschevskovo Akademii Nauk Ukrainskoj Ssr, Kiew (Sowjetunion) Process for removing ozone contaminants from air or exhaust air
SE426787B (en) * 1976-03-12 1983-02-14 Johnson Matthey Co Ltd CATALYST DEVICE
DE2630901A1 (en) * 1976-07-09 1978-01-12 Hoechst Ag DEVICE FOR REMOVING OZONE FROM GAS MIXTURES
US4143118A (en) * 1977-08-08 1979-03-06 Xerox Corporation Apparatus and method for ozone reduction in electrostatographic reproduction equipment
US4206083A (en) * 1978-09-20 1980-06-03 Minnesota Mining And Manufacturing Company Catalyst for ozone decomposition
US4173549A (en) * 1978-09-22 1979-11-06 Dart Industries Inc. Catalyst composition for decomposing ozone
DE2850154C2 (en) * 1978-11-18 1982-02-18 Joh. A. Benckiser Gmbh, 6700 Ludwigshafen Catalyst for ozone destruction in ozone-containing air and ozone-containing gases based on manganese and silver

Cited By (19)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2142324A (en) * 1983-06-29 1985-01-16 Teledyne Ind A method of removing ozone from air
US4619821A (en) * 1985-12-02 1986-10-28 Amoco Corporation Ozone decomposition
US5145657A (en) * 1987-01-21 1992-09-08 Nippon Shokubai Kagaku Kogyo Co., Ltd. Method for purification of gas
US5256377A (en) * 1987-04-29 1993-10-26 Ricoh Company, Ltd. Ozone decomposing material and ozone decomposing apparatus using the ozone decomposing material
GB2210607B (en) * 1987-04-29 1992-01-22 Ricoh Kk Ozone decomposing material and ozone decomposing apparatus using the ozone decomposing material
GB2210607A (en) * 1987-04-29 1989-06-14 Ricoh Kk Ozone decomposing material
US5232886A (en) * 1988-11-28 1993-08-03 Sakai Chemical Industry Co., Ltd. Catalysts and methods for ozone decomposition
US5286700A (en) * 1990-09-29 1994-02-15 Nippon Shokubai Co., Ltd. Catalyst and method of preparing the catalyst
US6616903B2 (en) 1995-01-20 2003-09-09 Engelhard Corporation Method and apparatus for treating the atmosphere
US6200542B1 (en) * 1995-01-20 2001-03-13 Engelhard Corporation Method and apparatus for treating the atmosphere
US6818254B1 (en) 1995-01-20 2004-11-16 Engelhard Corporation Stable slurries of catalytically active materials
US6586359B1 (en) 1998-03-23 2003-07-01 Engelhard Corporation Catalytic material for treating pollutant-containing gases
US6685898B2 (en) 1998-03-23 2004-02-03 Engelhard Corporation Hydrophobic catalytic materials and method of forming the same
WO2000069009A2 (en) * 1999-04-27 2000-11-16 Symyx Technologies, Inc. Platinum-ruthenium-palladium-osmium alloy for use as a fuel cell catalyst
WO2000069009A3 (en) * 1999-04-27 2001-07-19 Symyx Technologies Inc Platinum-ruthenium-palladium-osmium alloy for use as a fuel cell catalyst
EP1336997A2 (en) * 2002-02-19 2003-08-20 Samsung Electronics Co., Ltd. Metal catalyst based on Pt-Ru, a fuel cell electrode, and DMFC
EP1336997A3 (en) * 2002-02-19 2005-04-13 Samsung SDI Co., Ltd. Metal catalyst based on Pt-Ru, a fuel cell electrode, and DMFC
US7473402B2 (en) * 2004-03-26 2009-01-06 Honeywell International, Inc. Ozone removal system and method for low and high temperature operation
CN107456978A (en) * 2017-09-01 2017-12-12 深圳市高斯宝电气技术有限公司 A kind of ozone decomposition catalyst and preparation method thereof

Also Published As

Publication number Publication date
FR2462928A1 (en) 1981-02-20
SE8005540L (en) 1981-02-09
GB2056424B (en) 1983-07-06
DE3029948A1 (en) 1981-02-26
CA1152969A (en) 1983-08-30

Similar Documents

Publication Publication Date Title
GB2056424A (en) Decomposition of ozone
EP0306945B1 (en) Oxidation of carbon monoxide and catalyst therefor
EP0789621B1 (en) Catalyst with zirconia/ceria support
Tejuca et al. Surface behaviour of reduced LaCoO3 as studied by TPD of CO, CO2 and H2 probes and by XPS
Root et al. Adsorption and reaction of nitric oxide and oxygen on Rh (111)
US8992870B2 (en) Catalyst for decomposing nitrous oxide and method for performing processes comprising formation of nitrous oxide
KR100460249B1 (en) A Process for the Oxidation of Ammonia
JP3999557B2 (en) Catalyst for partial oxidation of hydrocarbon and method for producing hydrogen-containing gas using the catalyst
US6027703A (en) Method for operating a purification device for gases as well as a purification device for gases
EP0404046A1 (en) Catalyst composition for the oxidation of carbon monoxide
EP0311084B1 (en) Oxidation of carbon monoxide and catalyst composition therefor
EP2241368A1 (en) Catalyst and method for decomposing nitrous oxide and process for producing the catalyst
EP0912231B1 (en) Oxidation catalyst
US4818745A (en) Catalyst for oxidation of carbon monoxide and process for preparing the catalyst
US4753915A (en) Process for making a carrier-supported catalyst
EP0402899B1 (en) Process for preparing catalysts for oxidation of carbon monoxide
US20030181324A1 (en) Decomposition catalyst for nitrous oxide, prcocess for producing the same and process for decomposing nitrous oxide
EP0684869B1 (en) Catalyst for use in oxidation
US4940686A (en) Catalyst for oxidation of carbon monoxide
US7033558B2 (en) Method for eliminating traces of hydrocarbons from gas streams
JP4656353B2 (en) Room temperature catalyst
JPH11319559A (en) Catalyst and method for purifying exhaust gas containing methane
JP4656352B2 (en) Room temperature catalyst
WO2002068117A1 (en) Decomposition catalyst for nitrous oxide, process for producing the same and process for decomposing nitrous oxide
EP0993857B1 (en) Method for the catalytic oxidation of VOC/CO in the presence of organosilicate compounds

Legal Events

Date Code Title Description
PCNP Patent ceased through non-payment of renewal fee

Effective date: 19930729