WO2012160355A1 - System and method for generating no2 - Google Patents
System and method for generating no2 Download PDFInfo
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- WO2012160355A1 WO2012160355A1 PCT/GB2012/051121 GB2012051121W WO2012160355A1 WO 2012160355 A1 WO2012160355 A1 WO 2012160355A1 GB 2012051121 W GB2012051121 W GB 2012051121W WO 2012160355 A1 WO2012160355 A1 WO 2012160355A1
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- catalyst
- hydrogen
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- silver catalyst
- soot
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/944—Simultaneously removing carbon monoxide, hydrocarbons or carbon making use of oxidation catalysts
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/38—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
- B01J23/48—Silver or gold
- B01J23/50—Silver
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9404—Removing only nitrogen compounds
- B01D53/9409—Nitrogen oxides
- B01D53/9413—Processes characterised by a specific catalyst
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B21/00—Nitrogen; Compounds thereof
- C01B21/20—Nitrogen oxides; Oxyacids of nitrogen; Salts thereof
- C01B21/36—Nitrogen dioxide (NO2, N2O4)
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B32/00—Carbon; Compounds thereof
- C01B32/90—Carbides
- C01B32/914—Carbides of single elements
- C01B32/956—Silicon carbide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/20—Reductants
- B01D2251/202—Hydrogen
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/10—Noble metals or compounds thereof
- B01D2255/104—Silver
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/02—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust
- F01N3/021—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters
- F01N3/023—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters using means for regenerating the filters, e.g. by burning trapped particles
- F01N3/0231—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters using means for regenerating the filters, e.g. by burning trapped particles using special exhaust apparatus upstream of the filter for producing nitrogen dioxide, e.g. for continuous filter regeneration systems [CRT]
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/10—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
- F01N3/18—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control
- F01N3/20—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control specially adapted for catalytic conversion
- F01N3/206—Adding periodically or continuously substances to exhaust gases for promoting purification, e.g. catalytic material in liquid form, NOx reducing agents
- F01N3/2066—Selective catalytic reduction [SCR]
Definitions
- the present invention concerns improvements in catalytic processes, and more particularly concerns improvements in the oxidation of nitric oxide (also known as nitrogen monoxide or "NO").
- nitric oxide also known as nitrogen monoxide or "NO"
- CRT ® system comprises a platinum-based oxidation catalyst coated on a flow-through monolith substrate and downstream thereof a soot filter, preferably a wall-flow filter.
- the filter can be catalysed with a catalyst for reducing the combustion temperature of trapped soot, in which case the catalysed filter is often referred to as a Catalysed Soot Filter (CSF).
- CSF Catalysed Soot Filter
- the CRT ® reaction i.e. N0 2 + C (i.e. soot) ⁇ NO + CO
- the CRT ® reaction has been adapted and utilised extensively in recent years to provide a variety of approaches and systems for exhaust gas aftertreatment.
- CSF Catalysed Soot Filter
- a catalytic Pt coating is applied to a wall-flow filter which is disposed in the exhaust gas line.
- the filter surface generally has further catalysts to promote the soot oxidation reaction.
- the CSF tends to operate by accumulating soot when the vehicle is operated at low speeds, such as in an urban environment.
- the exhaust gas temperatures under low loads/low speeds are too low effectively to generate N0 2 or to cause the oxidation of soot by the CRT reaction.
- the CSF may be regenerated to remove the accumulation of soot by running the engine at higher speeds and/or under higher load or by engine management to create higher temperatures within the CSF. Whilst the CSF is effective, essentially it requires coatings containing expensive Pt for the purpose of generating N0 2 .
- SCR Selective Catalytic Reduction
- HC- SCR HydroCarbon Selective Catalytic Reduction
- hydrocarbon which is already present on-board in the form of fuel, has been found to have the ability to chemically reduce NOx.
- the necessary hydrocarbon may be supplied to the gas stream entering the SCR catalyst in a number of ways, including by post-combustion injection into the cylinders, and by injection of fuel into the exhaust gas stream.
- N0 2 :NO mixture in gas entering a SCR catalyst beneficially improves the rate of NO x reduction, compared to the same process practised on an exhaust gas wherein NO x is present entirely as NO or particularly wherein NO x is present entirely as N0 2 .
- EP 1054722 discloses the oxidation of NO to N0 2 thereby to provide a mixture of NO and N0 2 at the SCR catalyst inlet.
- the present invention provides a process for the generation of N0 2 by oxidation of NO in the presence of a catalyst, comprising the step of passing NO in the presence of a gaseous oxidising agent over a silver catalyst, in the presence of a quantity of hydrogen, wherein:
- the silver catalyst is deposited on a soot filter or as a component of a Catalytic Soot Filter;
- the silver catalyst is disposed upstream of a soot filter
- the silver catalyst is disposed upstream of a selective catalytic reduction catalyst.
- the invention also provides an exhaust system for an internal combustion engine, which system comprising a catalyst chamber, a silver catalyst positioned within the catalyst chamber and means to supply a quantity of hydrogen to the catalyst chamber, wherein the silver catalyst is disposed in one of the following arrangements:
- the silver catalyst is deposited on a soot filter or as a component of a Catalytic Soot Filter;
- the silver catalyst is disposed upstream of a soot filter
- the silver catalyst is disposed upstream of a selective catalytic reduction catalyst
- N0 2 is generated by contacting the silver catalyst with hydrogen.
- the system of feature (iii) comprises means for injecting a nitrogenous reductant between the silver catalyst and the SCR catalyst and a source of nitrogenous reductant.
- the silver catalyst is silver on an alumina support.
- the silver is desirably present as dispersed silver particles or Ag 2 0 clusters, but in the preferred catalysts, the particles are too small to be seen by Transmission Electron Microscopy. Larger silver particles are not particularly active.
- the alumina is in the form of boehmite or gamma alumina.
- the silver is present in an amount below 10% by weight of the alumina, more preferably below 5wt%, and most preferably an amount of approximately 2wt%.
- Suitable silver catalysts may be prepared in known manner.
- Suitable alumina supports are commercially available, such as “Disperal ® (Sasol) and "SCF140” (Condea).
- the mixture of NO and gaseous oxidising agent is conveniently an exhaust stream from an internal combustion engine. If the quantity of oxidising agent is too low for the desired quantity of reaction, for example the exhaust stream is from a stoichiometric engine, supplementary air may be added. Conveniently, the gas mixture is from a lean burn engine such as a diesel engine.
- the quantity of hydrogen suitable for the present invention is in the region of 200-5000ppm of the total gas present in the catalyst chamber, such as 500-3000ppm or 750-2000ppm, but is conveniently around lOOOppm.
- the hydrogen may conveniently be supplied to the gas stream before it enters the catalyst chamber, although other ways of injecting or admixing the hydrogen may be considered. It will be noted that such quantities of hydrogen are relatively small and even where present the exhaust gas remains lean overall.
- N0 2 in the present invention is, as with every catalytic reaction, temperature sensitive, although the method may be used over a usefully broad temperature range of approximately 150°C to 450°C. Desirably, the method operates at 200°C to 400°C, especially in the range 220°C to 300°C.
- the present invention offers a useful control over the generation of N0 2 , because N0 2 is produced in the present invention mainly or exclusively when hydrogen is supplied to the catalyst chamber.
- Existing Pt catalysts can generate relatively high tailpipe N0 2 levels, which may present the engine/vehicle designer with difficulties in meeting required levels of regulated emissions. So, for example, the California Air Resources Board (CARB) has proposed that a maximum of 20% of tailpipe NO x of the relevant drive cycle is emitted as N0 2 .
- N0 2 is toxic and can cause headaches, dizziness and nausea in low doses. It also has an objectionable
- the means for supplying the hydrogen in the present invention may therefore provide for continuous hydrogen supply, but in at least some applications, the means may desirably provide for intermittent supply, e.g. by a pre-programmed control means, desirably in response to engine operating conditions which are known to be associated with increased soot formation, or in response to sensed accumulation of soot on a filter by feedback control, e.g. again controlled by pre-programmed means. This may be achieved using known technology.
- the silver catalyst may be incorporated in a CSF, to replace all or a proportion of the Pt catalyst normally present.
- the CSF is generally of single "brick" design, that is to say, a single filter substrate which is coated with all necessary catalytic coatings, including zoned or homogeneous arrangements.
- Alternative designs such as the conventional CRT ® system, or a SCRT ® system, in which a filter (which may itself be catalysed to reduce the soot oxidation temperature) is separate from the N0 2 generating catalyst, may also benefit from the present invention, i.e. in order from upstream to downstream, the exhaust system comprises an oxidation catalyst, a filter e.g. a wall-flow filter, an injector for ammonia or a precursor thereof, such as urea and a SCR catalyst (see EP 1054722, the entire contents of which is incorporated herein by reference).
- the invention is expected to be applied initially to so-called LDD (light duty diesel) engines, which are used widely in personal automobiles and light commercial applications. It is expected to be subsequently applied to heavy duty diesel (HDD) applications, such as trucks, buses and stationary sources.
- LDD light duty diesel
- HDD heavy duty diesel
- the invention should not be considered as limited to diesel applications, however, and gasoline engine or other applications may be developed in the future.
- the required hydrogen may be supplied from a variety of sources. It may be convenient, for example, to produce hydrogen by fuel reforming or by exhaust gas reforming.
- the on-board reforming of fuel or exhaust gas is currently under active development by commercial and academic teams.
- the reformate gas may, in certain cases, be used directly without purification or separation, in the present invention.
- an emission control catalyst it is conventional to deposit an emission control catalyst on a flow-through substrate or on a filter.
- Conventional catalyst substrates and filters may be used to support the silver catalyst in the present invention, and conventional deposition techniques may be used.
- the catalyst may include other components which assist or do not significantly degrade the performance of the silver catalyst.
- a model, (i.e. synthetic) LDD exhaust gas containing 12% 0 2 , lOOOppm CO, 300ppm NO, 300ppm C 3 H 6 , 4.5% H 2 0, 4.5% C0 2 , balance nitrogen is passed over the catalyst bed at various catalyst temperatures, and the quantity of N0 2 in the outlet gas is measured.
- the results are shown in Figure 1 , for the same catalyst of 2wt% Ag deposited on Disperal alumina, both with the standard gas and for the standard gas with lOOOppm H 2 added. It can be seen from Figure 1 that without H 2 , negligible N0 2 is produced until at about 450°C, approximately 20ppm is produced. However, the addition of H 2 has an immediate and dramatic effect, peaking at approximately 160ppm at a temperature of approximately 250°C.
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- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Biomedical Technology (AREA)
- Materials Engineering (AREA)
- Combustion & Propulsion (AREA)
- Health & Medical Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Exhaust Gas After Treatment (AREA)
- Inorganic Chemistry (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
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Abstract
An exhaust system for an internal combustion engine comprises a catalyst chamber, a silver catalyst positioned within the catalyst chamber and means to supply a quantity of hydrogen to the catalyst chamber, wherein the silver catalyst is disposed in one of the following arrangements: (i) the silver catalyst is deposited on a soot filter or as a component of a Catalytic Soot Filter; (ii) the silver catalyst is disposed upstream of a soot filter; and/or (iii) the silver catalyst is disposed upstream of a selective catalytic reduction catalyst, and wherein N02 is generated by contacting the silver catalyst with hydrogen.
Description
SYSTEM AND METHOD FOR GENERATING NO?
The present invention concerns improvements in catalytic processes, and more particularly concerns improvements in the oxidation of nitric oxide (also known as nitrogen monoxide or "NO").
It is known that NO present in a gas stream such as an exhaust gas from an internal combustion engine can be oxidised to N02 by passing the exhaust gas stream over a platinum catalyst. This Pt-catalysed reaction has been used in a number of systems used commercially for exhaust gas aftertreatment. In particular, the first successful apparatus for removing combustion soot from diesel exhausts, the CRT® system developed and licensed by Johnson Matthey, uses N02 for the low temperature oxidation of soot. (The principle of the CRT® system is disclosed in EP 341832, the entire contents of which are incorporated herein by reference). The N02 required is formed by passing the lean exhaust gas from the diesel engine, which contains excess oxygen and NO, over a Pt catalyst. That is commercial CRT® system comprises a platinum-based oxidation catalyst coated on a flow-through monolith substrate and downstream thereof a soot filter, preferably a wall-flow filter. The filter can be catalysed with a catalyst for reducing the combustion temperature of trapped soot, in which case the catalysed filter is often referred to as a Catalysed Soot Filter (CSF).
Although there were suggestions prior to the CRT® system to catalyse a filter in an effort to reduce the soot combustion temperature, it seems what may be termed "the CRT® reaction", i.e. N02 + C (i.e. soot)→ NO + CO, was not discovered or appreciated because of the high sulphur content in fuel at the time. Subsequently, the CRT® reaction has been adapted and utilised extensively in recent years to provide a variety of approaches and systems for exhaust gas aftertreatment. One example of this approach is in the CSF (Catalysed Soot Filter), which has been found effective to remove particulate from the exhaust gases from light duty diesel engines. That is, a catalytic Pt coating is applied to a wall-flow filter which is disposed in the exhaust gas line. The filter surface generally has further catalysts to promote the soot oxidation reaction. The CSF tends to operate by accumulating soot when the vehicle is operated at low speeds, such as in an urban environment. The exhaust gas temperatures under low loads/low speeds are too low effectively to generate N02 or to cause the oxidation
of soot by the CRT reaction. The CSF may be regenerated to remove the accumulation of soot by running the engine at higher speeds and/or under higher load or by engine management to create higher temperatures within the CSF. Whilst the CSF is effective, essentially it requires coatings containing expensive Pt for the purpose of generating N02.
Another exhaust gas aftertreatment is SCR (Selective Catalytic Reduction). Several commercial applications use ammonia, generated from a urea solution, to reduce NOx (nitrogen oxides) to nitrogen (N2). An alternative SCR system that has the attraction that no separate on-board storage of urea reductant is required, is HC- SCR (HydroCarbon Selective Catalytic Reduction) in which hydrocarbon, which is already present on-board in the form of fuel, has been found to have the ability to chemically reduce NOx. The necessary hydrocarbon may be supplied to the gas stream entering the SCR catalyst in a number of ways, including by post-combustion injection into the cylinders, and by injection of fuel into the exhaust gas stream. Several SCR catalysts have been studied for HC-SCR, including catalysts based on silver, such as Ag on alumina. One exhaust system which combines the commercial CRT® system and a SCR catalyst is disclosed in EP 1054722, the entire contents of which is incorporated herein by reference, wherein the CRT® device is disposed upstream of a means for injecting reductant into the exhaust gas and the SCR catalyst (in that order). The system described in EP 1054722 is known by the registered trademark "SCRT®". From EP 1054722 and other publications it is known that an approximately 1:1
N02:NO mixture in gas entering a SCR catalyst beneficially improves the rate of NOx reduction, compared to the same process practised on an exhaust gas wherein NOx is present entirely as NO or particularly wherein NOx is present entirely as N02. In order to take advantage of this phenomenon, EP 1054722 discloses the oxidation of NO to N02 thereby to provide a mixture of NO and N02 at the SCR catalyst inlet.
There is a need for alternative catalysts and methods for generating N02 for improving downstream processes, desirably including the reduction or elimination of Pt in the catalyst.
Accordingly, the present invention provides a process for the generation of N02 by oxidation of NO in the presence of a catalyst, comprising the step of passing NO in the presence of a gaseous oxidising agent over a silver catalyst, in the presence of a quantity of hydrogen, wherein:
(i) the silver catalyst is deposited on a soot filter or as a component of a Catalytic Soot Filter;
(ii) the silver catalyst is disposed upstream of a soot filter; and/or
(iii) the silver catalyst is disposed upstream of a selective catalytic reduction catalyst.
The invention also provides an exhaust system for an internal combustion engine, which system comprising a catalyst chamber, a silver catalyst positioned within the catalyst chamber and means to supply a quantity of hydrogen to the catalyst chamber, wherein the silver catalyst is disposed in one of the following arrangements:
(i) the silver catalyst is deposited on a soot filter or as a component of a Catalytic Soot Filter;
(ii) the silver catalyst is disposed upstream of a soot filter; and/or
(iii) the silver catalyst is disposed upstream of a selective catalytic reduction catalyst,
and wherein N02 is generated by contacting the silver catalyst with hydrogen.
In one embodiment, therefore, the system of feature (iii) comprises means for injecting a nitrogenous reductant between the silver catalyst and the SCR catalyst and a source of nitrogenous reductant.
It will be appreciated that the combination of all of features (i), (ii) and (iii) results in a system having the system "architecture" of the EP 1504722, whereas the combination of features (i) and (ii), for example, provides the commercial CRT® embodiment, wherein the filter, e.g. a wall-flow filter, is also catalysed.
It will be recognised that to supply a particularly active reducing agent in the form of hydrogen to assist in an oxidation reaction is counter- intuitive, and that the results are surprising.
Desirably, the silver catalyst is silver on an alumina support. Our initial studies indicate that the silver is desirably present as dispersed silver particles or Ag20 clusters, but in the preferred catalysts, the particles are too small to be seen by Transmission Electron Microscopy. Larger silver particles are not particularly active. Most desirably, the alumina is in the form of boehmite or gamma alumina.
Preferably, the silver is present in an amount below 10% by weight of the alumina, more preferably below 5wt%, and most preferably an amount of approximately 2wt%. Suitable silver catalysts may be prepared in known manner. Suitable alumina supports are commercially available, such as "Disperal® (Sasol) and "SCF140" (Condea).
The mixture of NO and gaseous oxidising agent is conveniently an exhaust stream from an internal combustion engine. If the quantity of oxidising agent is too low for the desired quantity of reaction, for example the exhaust stream is from a stoichiometric engine, supplementary air may be added. Conveniently, the gas mixture is from a lean burn engine such as a diesel engine.
Early studies indicate that the quantity of hydrogen suitable for the present invention is in the region of 200-5000ppm of the total gas present in the catalyst chamber, such as 500-3000ppm or 750-2000ppm, but is conveniently around lOOOppm. The hydrogen may conveniently be supplied to the gas stream before it enters the catalyst chamber, although other ways of injecting or admixing the hydrogen may be considered. It will be noted that such quantities of hydrogen are relatively small and even where present the exhaust gas remains lean overall.
The formation of N02 in the present invention is, as with every catalytic reaction, temperature sensitive, although the method may be used over a usefully broad temperature range of approximately 150°C to 450°C. Desirably, the method operates at 200°C to 400°C, especially in the range 220°C to 300°C.
The present invention offers a useful control over the generation of N02, because N02 is produced in the present invention mainly or exclusively when hydrogen is supplied to the catalyst chamber. Existing Pt catalysts can generate
relatively high tailpipe N02 levels, which may present the engine/vehicle designer with difficulties in meeting required levels of regulated emissions. So, for example, the California Air Resources Board (CARB) has proposed that a maximum of 20% of tailpipe NOx of the relevant drive cycle is emitted as N02. N02 is toxic and can cause headaches, dizziness and nausea in low doses. It also has an objectionable
"swimming ροοΓ'-type chlorine smell.
The means for supplying the hydrogen in the present invention may therefore provide for continuous hydrogen supply, but in at least some applications, the means may desirably provide for intermittent supply, e.g. by a pre-programmed control means, desirably in response to engine operating conditions which are known to be associated with increased soot formation, or in response to sensed accumulation of soot on a filter by feedback control, e.g. again controlled by pre-programmed means. This may be achieved using known technology.
Initial applications of the invention are expected to be related to the CRT® reaction. Thus, the silver catalyst may be incorporated in a CSF, to replace all or a proportion of the Pt catalyst normally present. The CSF is generally of single "brick" design, that is to say, a single filter substrate which is coated with all necessary catalytic coatings, including zoned or homogeneous arrangements. Alternative designs, such as the conventional CRT® system, or a SCRT® system, in which a filter (which may itself be catalysed to reduce the soot oxidation temperature) is separate from the N02 generating catalyst, may also benefit from the present invention, i.e. in order from upstream to downstream, the exhaust system comprises an oxidation catalyst, a filter e.g. a wall-flow filter, an injector for ammonia or a precursor thereof, such as urea and a SCR catalyst (see EP 1054722, the entire contents of which is incorporated herein by reference).
The invention is expected to be applied initially to so-called LDD (light duty diesel) engines, which are used widely in personal automobiles and light commercial applications. It is expected to be subsequently applied to heavy duty diesel (HDD) applications, such as trucks, buses and stationary sources. The invention should not be considered as limited to diesel applications, however, and gasoline engine or other applications may be developed in the future.
The required hydrogen may be supplied from a variety of sources. It may be convenient, for example, to produce hydrogen by fuel reforming or by exhaust gas reforming. The on-board reforming of fuel or exhaust gas is currently under active development by commercial and academic teams. The reformate gas may, in certain cases, be used directly without purification or separation, in the present invention.
It is conventional to deposit an emission control catalyst on a flow-through substrate or on a filter. Conventional catalyst substrates and filters may be used to support the silver catalyst in the present invention, and conventional deposition techniques may be used.
Whilst the present invention requires a silver catalyst as an essential requirement, the catalyst may include other components which assist or do not significantly degrade the performance of the silver catalyst.
The present invention will now be illustrated with reference to tests carried out using a synthetic diesel exhaust, and to the sole accompanying Figure, which is a graph wherein N02 formation is plotted as a function of temperature using a synthetic diesel exhaust gas with and without hydrogen and a Ag/Al203 catalyst.
In a laboratory rig, 0.4g of catalyst is held in a catalyst chamber with a test gas supply at a flow rate of 2 litre/min. The gas leaving the catalyst chamber is analysed using conventional equipment. Catalyst bed temperatures are measured at the bed inlet. The catalyst bed is heated by preheating the feed gas.
A model, (i.e. synthetic) LDD exhaust gas containing 12% 02, lOOOppm CO, 300ppm NO, 300ppm C3H6, 4.5% H20, 4.5% C02, balance nitrogen is passed over the catalyst bed at various catalyst temperatures, and the quantity of N02 in the outlet gas is measured. The results are shown in Figure 1 , for the same catalyst of 2wt% Ag deposited on Disperal alumina, both with the standard gas and for the standard gas with lOOOppm H2 added.
It can be seen from Figure 1 that without H2, negligible N02 is produced until at about 450°C, approximately 20ppm is produced. However, the addition of H2 has an immediate and dramatic effect, peaking at approximately 160ppm at a temperature of approximately 250°C.
Subsequent tests have been carried out by varying the loading of silver from 2 to 8wt , and by varying the catalyst support. The best results have been observed with over 200 ppm peak N02 output at approximately 225 °C, using 2wt silver on SCF140 gamma alumina.
Claims
1. An exhaust system for an internal combustion engine, which system comprising a catalyst chamber, a silver catalyst positioned within the catalyst chamber and means to supply a quantity of hydrogen to the catalyst chamber, wherein the silver catalyst is disposed in one of the following arrangements:
(i) the silver catalyst is deposited on a soot filter or as a component of a Catalytic Soot Filter;
(ii) the silver catalyst is disposed upstream of a soot filter; and/or
(iii) the silver catalyst is disposed upstream of a selective catalytic reduction catalyst,
and wherein N02 is generated by contacting the silver catalyst with hydrogen.
2. A system according to claim 1, feature (iii), comprising means for injecting a nitrogenous reductant between the silver catalyst and the SCR catalyst and a source of nitrogenous reductant.
3. A system according to claim 1 or 2, wherein the silver catalyst is silver deposited on alumina.
4. A system according to claim 3, wherein the alumina is gamma-alumina or boehmite.
5. A system according to claim 3 or 4, wherein the silver catalyst comprises silver in an amount of below 5% by weight.
6. A system according to any preceding claim, wherein the means to supply hydrogen comprises a reformer for fuel or for exhaust gas.
7. A system according to any preceding claim, wherein the means for supplying hydrogen is controlled, when in use, to supply hydrogen intermittently.
8. A system according to claim 7, wherein the intermittent supply of hydrogen is controlled, when in use, in response to engine operating conditions or in response to sensed accumulation of soot on a filter.
9. A process for the generation of N02 by oxidation of NO in the presence of a catalyst, comprising the step of passing NO in the presence of a gaseous oxidising agent over a silver catalyst, in the presence of a quantity of hydrogen, wherein
(i) the silver catalyst is deposited on a soot filter or as a component of a Catalytic Soot Filter;
(ii) the silver catalyst is disposed upstream of a soot filter; and/or
(iii) the silver catalyst is disposed upstream of a selective catalytic reduction catalyst.
10. A process according to claim 9, wherein the NO in the presence of a gaseous oxidising agent comprises the exhaust gas from an internal combustion engine.
11. A process according to claim 9 or 10, wherein the hydrogen is present in an amount in the region of 200-5000 ppm of the total gas present.
12. A process according to claim 9, 10 or 11, wherein the catalyst temperature is from 200 to 400° C.
13. A process according to claim 9, 10, 11 or 12, wherein the supply of hydrogen is intermittent.
14. A process according to claim 13, wherein the intermittent supply of hydrogen is in response to engine operating conditions or to sensed accumulation of soot on a filter.
Applications Claiming Priority (4)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US201161488480P | 2011-05-20 | 2011-05-20 | |
| US61/488,480 | 2011-05-20 | ||
| GB1111180.4 | 2011-06-30 | ||
| GB201111180A GB201111180D0 (en) | 2011-05-20 | 2011-06-30 | System and method for generating NO2 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2012160355A1 true WO2012160355A1 (en) | 2012-11-29 |
Family
ID=44511888
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/GB2012/051121 Ceased WO2012160355A1 (en) | 2011-05-20 | 2012-05-18 | System and method for generating no2 |
Country Status (3)
| Country | Link |
|---|---|
| DE (1) | DE102012208399B4 (en) |
| GB (2) | GB201111180D0 (en) |
| WO (1) | WO2012160355A1 (en) |
Citations (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP0341832A2 (en) | 1988-05-13 | 1989-11-15 | Johnson Matthey Inc. | Treatment of diesel exhaust gas |
| JPH11319563A (en) * | 1998-05-11 | 1999-11-24 | Mazda Motor Corp | Exhaust gas purification catalyst |
| EP1054722A1 (en) | 1998-02-06 | 2000-11-29 | Johnson Matthey Public Limited Company | System for nox reduction in exhaust gases |
| DE10261817A1 (en) * | 2002-12-19 | 2004-07-01 | INSTITUT FüR ANGEWANDTE CHEMIE BERLIN-ADLERSHOF E.V. | Selective catalytic reduction of nitrogen oxides with ammonia and oxygen, useful for purifying stationary or mobile engine exhaust gas and waste gas from nitric acid manufacture, uses added hydrogen and catalyst containing silver |
| EP1504722A2 (en) | 2003-08-08 | 2005-02-09 | Genefast S.r.l. | Device for drawing biological and/or chemical samples |
| US20070031310A1 (en) * | 2005-08-05 | 2007-02-08 | Lee Jong-Hwan | Reduction of NOx emissions using a staged silver/alumina catalyst system |
| US20080069741A1 (en) * | 2006-09-20 | 2008-03-20 | Gerald Stephen Koermer | Catalysts to Reduce NOx in an Exhaust Gas Stream and Methods of Preparation |
| US20100000202A1 (en) * | 2008-07-07 | 2010-01-07 | Fisher Galen B | Dual catalyst NOx reduction system for exhaust from lean burn internal combustion engines |
| EP2223735A1 (en) * | 2007-11-08 | 2010-09-01 | Honda Motor Co., Ltd. | Exhaust cleaner for internal combustion engine and method of exhaust purification |
| US20100284875A1 (en) * | 2009-05-11 | 2010-11-11 | Basf Corporation | Treatment of power utilities exhaust |
| EP2301650A1 (en) * | 2009-09-24 | 2011-03-30 | Haldor Topsøe A/S | Process and catalyst system for SCR of NOx |
-
2011
- 2011-06-30 GB GB201111180A patent/GB201111180D0/en not_active Ceased
-
2012
- 2012-05-18 GB GB1208763.1A patent/GB2491244B/en not_active Expired - Fee Related
- 2012-05-18 WO PCT/GB2012/051121 patent/WO2012160355A1/en not_active Ceased
- 2012-05-21 DE DE102012208399.5A patent/DE102012208399B4/en not_active Expired - Fee Related
Patent Citations (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP0341832A2 (en) | 1988-05-13 | 1989-11-15 | Johnson Matthey Inc. | Treatment of diesel exhaust gas |
| EP1054722A1 (en) | 1998-02-06 | 2000-11-29 | Johnson Matthey Public Limited Company | System for nox reduction in exhaust gases |
| JPH11319563A (en) * | 1998-05-11 | 1999-11-24 | Mazda Motor Corp | Exhaust gas purification catalyst |
| DE10261817A1 (en) * | 2002-12-19 | 2004-07-01 | INSTITUT FüR ANGEWANDTE CHEMIE BERLIN-ADLERSHOF E.V. | Selective catalytic reduction of nitrogen oxides with ammonia and oxygen, useful for purifying stationary or mobile engine exhaust gas and waste gas from nitric acid manufacture, uses added hydrogen and catalyst containing silver |
| EP1504722A2 (en) | 2003-08-08 | 2005-02-09 | Genefast S.r.l. | Device for drawing biological and/or chemical samples |
| US20070031310A1 (en) * | 2005-08-05 | 2007-02-08 | Lee Jong-Hwan | Reduction of NOx emissions using a staged silver/alumina catalyst system |
| US20080069741A1 (en) * | 2006-09-20 | 2008-03-20 | Gerald Stephen Koermer | Catalysts to Reduce NOx in an Exhaust Gas Stream and Methods of Preparation |
| EP2223735A1 (en) * | 2007-11-08 | 2010-09-01 | Honda Motor Co., Ltd. | Exhaust cleaner for internal combustion engine and method of exhaust purification |
| US20100000202A1 (en) * | 2008-07-07 | 2010-01-07 | Fisher Galen B | Dual catalyst NOx reduction system for exhaust from lean burn internal combustion engines |
| US20100284875A1 (en) * | 2009-05-11 | 2010-11-11 | Basf Corporation | Treatment of power utilities exhaust |
| EP2301650A1 (en) * | 2009-09-24 | 2011-03-30 | Haldor Topsøe A/S | Process and catalyst system for SCR of NOx |
Non-Patent Citations (3)
| Title |
|---|
| N BOGDANCHIKOVA: "On the nature of the silver phases of Ag/Al2O3 catalysts for reactions involving nitric oxide", APPLIED CATALYSIS. B, ENVIRONMENTAL, vol. 36, no. 4, 28 March 2002 (2002-03-28), pages 287 - 297, XP055033355, ISSN: 0926-3373, DOI: 10.1016/S0926-3373(01)00286-7 * |
| SAZAMA P ET AL: "Enhancement of decane-SCR-NOx over Ag/alumina by hydrogen. Reaction kinetics and in situ FTIR and UV-vis study", JOURNAL OF CATALYSIS, ACADEMIC PRESS, DULUTH, MN, US, vol. 232, no. 2, 10 June 2005 (2005-06-10), pages 302 - 317, XP004905893, ISSN: 0021-9517, DOI: 10.1016/J.JCAT.2005.03.013 * |
| VILLANI ET AL: "Catalytic carbon oxidation over Ag/Al2O3", JOURNAL OF CATALYSIS, ACADEMIC PRESS, DULUTH, MN, US, vol. 236, no. 1, 15 November 2005 (2005-11-15), pages 172 - 175, XP005126884, ISSN: 0021-9517, DOI: 10.1016/J.JCAT.2005.09.018 * |
Also Published As
| Publication number | Publication date |
|---|---|
| DE102012208399B4 (en) | 2015-06-11 |
| GB201111180D0 (en) | 2011-08-17 |
| DE102012208399A1 (en) | 2012-11-22 |
| GB2491244B (en) | 2014-05-07 |
| GB2491244A (en) | 2012-11-28 |
| GB201208763D0 (en) | 2012-07-04 |
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