IE49846B1 - Exhaust gas purification - Google Patents

Exhaust gas purification

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Publication number
IE49846B1
IE49846B1 IE1344/80A IE134480A IE49846B1 IE 49846 B1 IE49846 B1 IE 49846B1 IE 1344/80 A IE1344/80 A IE 1344/80A IE 134480 A IE134480 A IE 134480A IE 49846 B1 IE49846 B1 IE 49846B1
Authority
IE
Ireland
Prior art keywords
exhaust gas
chamber
engine
catalyst
catalyst system
Prior art date
Application number
IE1344/80A
Other versions
IE801344L (en
Original Assignee
Johnson Matthey Co Ltd
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Filing date
Publication date
Application filed by Johnson Matthey Co Ltd filed Critical Johnson Matthey Co Ltd
Publication of IE801344L publication Critical patent/IE801344L/en
Publication of IE49846B1 publication Critical patent/IE49846B1/en

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Classifications

    • 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
    • B01D53/9445Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC]
    • B01D53/9454Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC] characterised by a specific device
    • 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
    • B01D53/944Simultaneously removing carbon monoxide, hydrocarbons or carbon making use of oxidation catalysts
    • B01J35/58
    • 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
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
    • F01N3/00Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
    • F01N3/08Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
    • F01N3/10Exhaust 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
    • F01N3/24Exhaust 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 constructional aspects of converting apparatus
    • F01N3/28Construction of catalytic reactors
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
    • F01N2330/00Structure of catalyst support or particle filter
    • F01N2330/12Metallic wire mesh fabric or knitting
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
    • F01N2470/00Structure or shape of gas passages, pipes or tubes
    • F01N2470/16Plurality of inlet tubes, e.g. discharging into different chambers
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
    • F01N2470/00Structure or shape of gas passages, pipes or tubes
    • F01N2470/18Structure or shape of gas passages, pipes or tubes the axis of inlet or outlet tubes being other than the longitudinal axis of apparatus
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F02COMBUSTION ENGINES; HOT-GAS OR COMBUSTION-PRODUCT ENGINE PLANTS
    • F02BINTERNAL-COMBUSTION PISTON ENGINES; COMBUSTION ENGINES IN GENERAL
    • F02B3/00Engines characterised by air compression and subsequent fuel addition
    • F02B3/06Engines characterised by air compression and subsequent fuel addition with compression ignition
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02TCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO TRANSPORTATION
    • Y02T10/00Road transport of goods or passengers
    • Y02T10/10Internal combustion engine [ICE] based vehicles
    • Y02T10/12Improving ICE efficiencies

Abstract

An internal combustion engine includes apparatus for reducing pollutants contained in exhaust gases omitted from the engine, the apparatus comprising a casing (1) defining a chamber containing a catalyst (3), the catalyst including a substrate made from filamentary metallic material in knitted, woven or crushed form, a first layer of a refractory metal oxide applied to the substrate and a second layer of a catalytic material applied to the first layer, the chamber having an inlet in communication with the exhaust ports (7, 8, 9, 10) of the engine via which exhaust gas emitted from the engine is lead into the chamber and passed through the catalyst prior to passage through an exhaust system (11) to atmosphere.

Description

This invention relates to exhaust gas purification and in particular to a process for oxidising particles in exhaust gas emitted from a diesel engine when the exhaust gas is at a temperature of 200 to 400°C and to a diesel engine in combination with apparatus suitable for oxidising carbon particles in exhaust gas emitted from the engine.
Exhaust gas emitted from a diesel engine contains solid/liguid particles (i.e. solid particles having a liquid outer covering layer). Also present are solid chain aggregates (in which spherical particles of o between 100 to 800 A diameter link up together), liquid sulphates, liquid hydrocarbons and gaseous hydrocarbons such as aldehydes. The solid/liquid particles generally comprise carbon particles with adsorbed liquid hydrocarbons and the solid chain aggregates are generally composed of high molecular weight organic compounds and/or inorganic sulphates.
About 90% of these smoke forming particles have maximum dimensions of less than one micron which is within the respirable particle size and the maximum dimension of the remaining 10% of these smoke forming particles are less than four microns. Usually, the catalytic oxidation of carbon particles takes place at about 400°C whereas their normal (ie uncatalysed) For temperature of combustion is 700 - 800°C. hydrocarbon particles catalytic oxidation will take place at temperatures about 200°C.
An object of the present invention is to reduce 5 the quantity both of noxious gases and particulates especially carbon particles present in exhaust gas emitted from diesel engine when the exhaust gas is at a temperature of from 200 to 400°C.
Accordingly this invention provides a process 10 for enabling the oxidation of particles in exhaust gas emitted from a diesel engine to be initiated at temperature of from 200 to 400°C which comprises passing the exhaust gas through a chamber containing an interstitial catalyst system comprising a catalyst, a 15 layer of refractory metal oxide and a support comprising filamentary metallic material in a knitted or woven form, the catalyst being disposed on or throughout the layer of refractory metal oxide which in turn is disposed on the surface of the filamentary metallic material wherein 20 the exhaust gas is passed into the chamber in a first direction and caused to pass in a direction transverse to the first direction during a portion of its passage through the chamber thereby increasing turbulence within the interstitial catalyst system. For example 25 the exhaust gas may be passed through the catalyst system in a direction transverse of the first direction.
Generally the chamber is defined by a casing having an entry port in communication with an exhaust port in the engine and having an exit port from which exhaust gas can be taken to atmosphere whereby exhaust gas from the engine can be passed through the chamber. The support is mounted within the chamber preferably spaced from the casing so as to define an outer passageway. The support may be shaped so as to define a central passageway within the support. When the support is associated with outer and central passageways, one of the passageways communicates with the entry port or ports and the other communicates with the exit port and the support is positioned so that the exhaust gas discharged from the engine is caused to pass through one passageway then into the interstitial catalyst system and through the other passageway, the outer and central passageways and the support being aligned relative to the entry port or ports such that exhaust gas passing through the chamber is caused to flow in a direction transverse of the entry port or ports during a portion of its passage through the chamber thereby increasing turbulence within the interstitial catalyst system.
Accordingly this invention also provides a diesel engine in combination with apparatus suitable for oxidising carbon particles in exhaust gas emitted from the engine wherein (a) the apparatus comprises a casing defining a chamber having one or more entry ports in communication with one or more exhaust ports in the engine and having an exit port from which exhaust gas can be taken to atmosphere wherein gas from the engine can be passed through the chamber. (b) The chamber contains an interstitial catalyst system comprising a catalyst, a layer of refractory metal oxide and a support comprising filamentary metallic material in a knitted or woven form, the catalyst being disposed on or throughout the layer of refractory metal oxide which in turn is disposed on the surface of the filamentary metallic material, (c) The catalyst system is mounted within the chamber spaced from the casing so as to define an outer passageway, and is shaped so as to define a central passageway within the catalyst system, (d) One of the passageways communicates with the entry port or ports and the other communicates with the exit port and the catalyst system is positioned so that the exhaust gas discharged from the engine is caused to pass through one passageway then into the interstitial catalyst system and through the other passageway, - 5 (e) the outer and central passageways and the catalyst system are aligned relative to the entry port or ports such that exhaust gas passing through the chamber is caused to flow in a direction transverse of the entry port or ports during a portion of its passage through the chamber thereby increasing turbulence within the interstitial catalyst system.
Preferably the chamber casing has a plurality of entry ports in communication with the exhaust valves of the engine. Preferably the exit port in the chamber casing is adjacent to an exhaust pipe.
Preferably the catalyst system contained in the chamber comprises a catalyst selected from the group of catalytic metals consisting of Ru, Rh, Pd, Ir, Pt, Fe, Co, Ni, V, Cr, Mo, W, Y, Ce, alloys thereof and intermetallic compounds containing at least 20% by weight of one or more of the metals disposed upon the surface of or throughout the layer of refractory metal oxide.
The layer of refractory metal oxide is preferably a washcoat layer containing (in the form of their oxides) one or more members of the group consisting of Mg, Ca, Sr, Ba, Sc, Y, the lanthanides, Ti, Zr, Hf, Th, Ta, V, Cr, Mn, Co, Ni, B, Al, Si and Sn. Preferred washcoat materials are A12O3 and alumina hydrates but stablising oxides such as BaO and oxides promoting catalytic activity such as TiO2, ZrOj, HfOj, ThOj, Cr2O3 and NiO may also be present.
The filamentary metallic material of the support is preferably made from base metal alloys which are corrosion resistant and preferably oxidation resistant.
Examples of such base metal alloys are nickel and chromium alloys having an aggregate Ni plus Cr content greater than 20% by weight and alloys of iron including at least one of the elements chromium (3 - 40) wt %, aluminium (1 - 10) wt %, cobalt (trace - 5) wt %, nickel (trace - 72) wt % and carbon (trace - 0.5) wt %. Such supports are described in German DOS 2450664.
Other examples of base metals capable of withstanding the rigorous conditions required are iron-aluminium-chromium alloys which may also contain yttrium. The latter alloys may contain 0.5 - 12 wt % Al, 0.1 - 3.0 wt % Y, 0 - 20 wt % Cr and balance Fe.
These are described in United States Patent Specification No.3298826. Another range of Fe-Cr-Al-Y alloys contain 0.5 - 4 wt % Al, 0.5 - 3.0 wt % Y, 20.0 - 95 wt % Cr and balance Fe. These are described in United States Patent Specification No. 3027252.
Alternatively the base metal alloys may have less corrosion resistance, eg mild steel, but with a protective coating composition covering the surface of the substrate as described in British Patent Specification I No. 2O13517A. 1 Where wire is used as the filamentary metallic material, its thickness is preferably between 0.025 to 0.5 mm (ie 0.001 and 0.02 inches) thick and preferably between 0.025 to 0.3 mm (ie 0.001 and 0.012 inches) thick. Preferably prior to its fabrication into woven or knitted form the wire is rolled down to a ribbon having two flat opposite surfaces.
The invention is further illustrated by the following specific embodiments described with reference to Figures 1 to 4 of the drawings and by the following Examples, results from which are shown as graphs by the Figures 5 to 14 of the drawings. In the drawings, Figure 1 shows a section through a chamber suitable for use in combination with a diesel engine according to the invention.
Figure 2 shows a section through an alternative apparatus for use in combination with a diesel engine according to the invention.
Figure 2a shows on a larger scale a section through a further alternative apparatus, Figure 3 shows in perspective an assembly of supporting bars suitable for acting as a central support In the apparatus.
Figure 4 shows in perspective an alternative central support for the apparatus. 9846 Figures 5 to 9 show graphs of the composition of pollutants in exhaust discharging from a diesel engine operated on an LA4 cold start cycle versus miles notionally travelled.
Figures 10 to 14 show similar graphs to those of Figures 5 to 9 but obtained from a diesel engine operated on an IA4 hot start cycle.
Figure 1 shows apparatus 1 comprising a chamber lb for use In combination with a diesel engine (not shown).
Chamber lb defined by casing la contains a centrally positioned catalyst system 3 located within a reaction tube 2. Casing la has entry ports 7, 8, 9 and 10 which are adjacent to and continuous with exhaust ports in the engine (not shown). Casing la also has one exit port 12 adjacent to an exhaust pipe 11. A support comprising filamentary metallic material and tube 2 is in turn supported in chamber lb by struts 5 and 6.
Tube 2 is positioned transversely of entry ports 7 to 10 and is spaced from casing la so as to define a passageway 2a. The exhaust gas on entering chamber lb has to pass through tube 2 and so come into close and continuous contact with catalyst system 3 before leaving chamber lb and entering the exhaust pipe 11. The exhaust gas flow through the chamber lb is generally indicated by the labelled arrows Fj, F?, F^, F^, and Fg.
Combusted gas flows In from the engine exhaust ports through the openings 7, 8, 9 and 10 and flows along transverse tube 2 and out into exhaust pipe 11. A retaining bar 4 is placed across the exit of tube 2 to ensure that catalyst system 3 remains in position.
The interstitial support in the catalyst is preferably of knitted wire mesh. This may be fabricated into a single monolith or it may be made up in annular sections.
A layer of refractory metal oxide washcoat and the catalyst may be applied to each section of the support separately or after the sections have been linked together. Alternatively the filamentary metallic material (in sections or linked together) may have the washcoat and catalyst applied after it has been placed in the tube.
Figure 2 shows an alternative apparatus 21 in which chamber 21b defined by a casing 21a having entry ports 27, 28 29 and 30, adjacent and in communication with engine exhaust ports (not shown) and one exit port 32 adjacent to the exhaust pipe 31. Interstitial catalyst system 23 (comprising a filamentary metallic support, a refractory metal oxide washcoat layer and a catalyst) is disposed centrally within chamber 21b and transversely of entry ports 27 to 30 so as to define a 4 9 0 4 0 transverse passageway 23a. The exhaust gas on entering chamber 21b is compelled to pass through the interstices of the catalyst system before leaving chamber 21b and entering exhaust pipe 31. The exhaust gas flows through chamber 21b as indicated by the labelled arrows, F41, F42, F43, F44, and F45· The gas flows in from the engine exhaust ports (not shown) as indicated by F41, F42, F43, and F44 and then through catalyst system 23 and out into a central passageway 22a defined by perforated tube 22 as indicated by F^.
In this embodiment the support in the catalyst system is preferably of knitted wire which may be made up either in sections or in one unit. If the support is in sections, eg of doughnut configuration, these are normally linked together before the support is placed in the chamber. One end of tube 22 is closed off by welded disc 26. An annular disc 25 at the other end holds catalyst system 23 in position on tube 22.
The catalyst system 23 is located in chamber 21b by attaching the ends covered by the discs 25 and 26 to casing 21a. Tube 22 also ensures that catalysts system 23 does not collapse inwards. Tube 22 allows exhaust gas to pass through it into central passageway 22a so that the gas can be taken to atmosphere along exhaust pipe 11.
Accordingly tube 22 should be permeable and may be constructed of wire mesh or perforated metal having holes or slots.
Figure 3 shows an alternative central structure in which in place of tube 22 there is provided a series of rigid bars, 100 to 500, running the length of chamber 21b. Bars 100 to 500 are maintained in fixed spatial relationship to one another by spacing plates 600. Accordingly bars 100 to 500 hold catalyst system 23 rigidly in place with chamber 21b. Spacing plates 600 in pairs connect three of the five bars and are usually at right angles to each other thus being disposed along a diameter of a central cylindrical exit passageway. Two or more pairs of spacing plates 600 may be used and they are usually positioned at regular intervals in the length of the chamber. Alternatively the spacing plates 600 . may be adapted to extend the whole length of chamber 21b as shown in Figure 4 whereupon they may be used instead of bars 100 to 500.
Rods and spacing plates need to be constructed of a material resistant to oxidation up to at least 800°C.
Figure 2a shows a further alternative apparatus 100 in which a chamber 100b defined by a casing 100a having entry ports 101 and 102 comprising sleeves 106 and 107 adjacent to and in communication with engine exhaust ports (not shown) and having an exit port 103 adjacent to an exhaust pipe (not shown). An interstitial catalyst system 104 (comprising a support, a refractory metal oxide washcoat and a catalyst) is disposed centrally within chamber 100b and transversely of entry ports 101 and 102 so as to define a passageway 104a.
Exhaust gas emitted from the engine has to pass through catalyst system 104 before leaving chamber 100b.
Catalyst system 104 is located in chamber 100b using spacing plates, 105, as shown in Figure 4. One end 109 of spacing plates 105 is fixed to casing 100a and a disc 108 is attached to the other end of spacing plates 105 to ensure that no exhaust gas can leave chamber 100b without passing through catalyst 104. The exhaust gas flows into chamber 100b through the entry ports 101 and 102 down through sleeves 106 and 107 into the inner space 110 provided by the spacing plates 105, and through the catalyst 104 onwards. The exhaust gas then flows out of chamber lOOb through exit port 103. The flow of the exhaust gas is indicated by the labelled arrows Fgo to Flo9. For simplicity. Figure 2a shows only two entry ports 101 and 102.
The support for the catalyst system is preferably of knitted wire which may be made up into four sections or three units. If the support is in sections, eg of doughnut confuguration, these are normally linked together before the support is placed in the chamber.
EXAMPLE 1 The effect of a catalyst system on the temperature at which catalytic oxidation of particles entrained in the exhaust gas stream of a diesel engine took place were studied. A number of sample catalyst systems were prepared. The catalyst systems comprised a support fabricated from 310 stainless steel wire of diameter 0.010 inch (0.25 mm) rolled down to ribbon 0.0004 inch (0.01 mm) thick, a layer of alumina and a layer of one or more platinum group metal catalysts at a loading of 2.46 mg/g of alumina. A portion of coated wire was cut from a catalyst system. The portion was heated together with particulate matter, collected from the exhaust gas stream of a diesel engine. Heating was performed in the sample pan of a differential scanning colorimeter (a DSC) in an atmosphere of 1% oxygen in argon. As the temperature was gradually raised, samples of the atmosphere above the sample pan were taken via a heated capillary tube to a mass spectrometer. Four mass numbers were traced: carbon dioxide (44), doubly charged argon (20), oxygen (32) and water (18) or nitrogen and carbon monoxide (28). The temperature at which the differential plot of the DSC peaked was taken to be the temperature at which combustion of the particles took place. This temperature can be referred to as the light-off temperature. The results were given below: Alumina Loading g/g of wire Catalytic metal(s) Light-off temperature (°C) 0.33 5.7 Rh 94.3% Pt 235 0.28 67 % Pt 33%Pd 207 0.30 Pd 265 0.28 Pt 220 The light-off temperatures observed for particulates from the exhaust gas stream of a diesel engine, 207 - 265°C, is considerably lower than the temperature required for combustion to take place when no catalyst is present.
Since the presence of a catalyst enables oxidation of the particles in the exhaust gas to take place at a lower temperature than the normal temperature at which combustion takes place it is possible to oxidise the particles in the exhaust gas emitted from a diesel engine with little or no extra heating. This is due to the fact that the operating temperature of a diesel engine at medium to full power is about 400°C so that no preheating of the emitted exhaust gas is required before passing the exhaust gas into the catalyst system.
EXAMPLE 2 The (200 cc capacity) multicylinder engine.of a - 15 commercially available diesel engine-powered automobile was modified to demonstrate the results obtained in operation of the present invention.
Apparatus for oxidising carbon particles outlined 5 in the first embodiment of the invention as described with reference to Figure 1 was fitted to the engine. The support in the catalyst system comprised knitted mesh made from wire having the following composition: % wt Cr 15 Al 4 Y 0.3 Fe Balance Deposited on this support was a washcoat consisting of gamma alumina stabilised with 5% by weight BaO and a catalytic metal layer composed of platinum and palladium. The Pt/Pd loading was 2.5 g total (pt:pd ratio 1:1) on a total catalyst volume of 84 cubic inches (1377 cm3). The results were obtained by driving the automobile through the LA4 diesel cycle (as hereinafter defined). The hydrocarbons, carbon monoxide (CO), nitrogen oxides (NOx) and particles present in the exhaust gas emissions were measured in g/mile (g/1.6km). Base line measurements were first taken without a catalyst system in the chamber but with back pressure adjusted to the same value as with the catalyst system present, are given in Table 1: Results TABLE 1 Hydrocarbons Co NOx Particles q/mile g/mile g/mile g/mile (g/1.6km (g/1.6km) (g/1.6km) (g/1.6km) Baseline figures 1.54 1.93 1.53 0.85 Modified engine 0.214 1.892 0.979 0.44 The back pressure was found to be high.
EXAMPLE 3 Further experiments were carried out using the same catalyst as ln Example 2 above. Baseline particle emissions using the same vehicle were determined in four tests as g/mile (g/1.6km) figures. These were expanded to include thermogravimetric determinations of the percentage carbon and volatiles contained with the particles and the g/mile (g/1.6km) sulphate contained within the particles. The results are shown as follows.
Baseline Figures Hast No. Particles g/faile % Carbon % Volatiles Sulphates g/taile (g/1.6km) (g/1.6km) 1 0.582 62.5 37.5 0.015 2 0.512 58.0 42.0 0.011 3 0.509 59.6 . 40.4 0.012 4 0.482 61.8 38.2 0.012 NOTE: All above measurements completed on a hot LA4 driving cycle.
The full baseline emissions determined for HC, CO and NOx were also determined, the results being as follows: Test No. Hydrocarbons 00 g/nile rt Ard 1δ NOx g/mile i (g/1.6km) (g/1.6km) (g/1.6km) 1 0.350 1.564 1.775 2 0.339 1.529 1.803 3 0.354 1.561 1.786 The apparatus was designed within the constraints available in ι the vehicle without any modification being made to the engine compartment layout :. This resulted in a catalyst volume of 0.9 litres which i was anticipated to be inadequate but upon which full tests were completed The results of these are as follows: Test No, . Particles % Carbons % Volatiles Sulphate gAnile g/inile (g/1.6km) (g/1.6km) 1 0.494 79.4 20.6 0.036 2 0.441 76.4 23.6 0.037 3 0.444 75.3 24.7 0.035 4 0.515 67.3 32.7 0.055 5 0.466 63.4 36.6 0.064 6 0.499 76.1 23.9 0.051 ά ο σ «ι vr NOTE; The vehicle had completed 500 road miles prior to the first test and the entire period of testing was completed under simulated city driving conditions using the LA4 cycle.
Test results obtained for the HC, CO and NOx emissions were as follows: Test No. Hydrocarbcns CO NOx g/nile g/taile (g/1.6km) g^nile (g/1.6km) (g/1.6km) 1 0.244 0.979 1.892 2 0.238 1.073 1.874 3 0.215 0.981 2.014 EXAMPLE 4 Apparatus as described ' with reference to Figure 2 was fitted onto the diesel engine of Example 2. The support comprised a mesh made of the same wire as used in Example 1 and was again provided with a washcoat of gamma alumina. The catalyst comprised rhodium 1¼ wt % and platinum 92¼ wt %. The total volume of the catalyst system was 110 cubic inches (1803 cm3). The weight of support and alumina washcoat were approximately 1.6kg and 5g respectively. 2.9g of the catalytic metals Rh and Pt in the above ratio were applied to the support. Baseline measurements were taken with no catalyst system present. The results are given below in Table 2 with the car being driven through the LA 4 cycle with a hot start.
TABLE 2 Hydrocarbons 00 NOx Particles g/nile (g/1.6km) g/nile (g/1.6km) g/ftiile (g/1.6km) g/inile (g/1.6km) Baseline figures 0.35 1.55 1.8 0.57 Modified engine 0.2 0.5 2.1 0.31 The back pressure without a catalyst system present was 2.4 Inches of mercury (0.08 bar) but was 3.5 inches of mercury (0.12 bar) when the catalyst system was present in the chamber. The C/H atomic ratio of the particles present in the exhaust gas before and after passage through the chamber was measured and is given below in Table 3 with a hot Btart for the engine.
TABLE 3 C/H ratio of particles present in the exhaust gas Before catalyst After catalyst C 63 80 H 37 20 This is a measure of the reduction in the organic compound content of the exhaust gases. The concentration of sulphate present in the exhaust gases before and after the catalyst was measured and found to be unchanged.
Further results obtained are given below in Table 4, 48OHO this time following a cold start for the engine.
TABLE 4 Hydrocarbons g/taile (g/1.6km) 00 g/inile (g/1.6km) NOx g/taile (g/1.6km) Particles g/toiile g/1.6km) Baseline figures 0.41 1.3 1.9 0.62 Modified engine 0.242 0.274 1.86 0.42 Modified engine 0.218 0.252 1.86 0.4 The composition of the particles present in the exhaust gas is given below in Table 5 again following a cold start for the engine. Adsorbed Hydrocarbons g/tnile (g/1.6km) Sulphates g/tnile (g/Ί· 6km) Carbon g/tnile g/1·6km) 15 Baseline figures 0.11 0.34 0.165 Modified engine 0.11 0.28 0.025 The results in Tables 2, 3, 4 and 5 were obtained using a commercially available diesel engine-powered automobile. The automobile had first completed 500 miles (800 km) round a test circuit and had then been driven through the taxi cycle (hereinafter defined with a maximum speed of 25mph (40kmph) Example 5 Further tests were conducted using a commercially available diesel engine-powered automobile. Apparatus as described with reference to Figure 2 was fitted onto the engine. A support was made of 310 stainless steel wire of diameter 0.01 inch (0.25 mm) which was flattened to 0.004 inch (0.01 mm) across before being knitted. The knitted support was coated with a washcoat of gamma alumina. The catalyst comprised rhodium .7% and platinum 94.3% with a loading of 25 g/ft3 (883 g/m3). The volume of wire used was 217 cubic inches. (3557 cm3).
The weight of particles present in the exhaust gas was measured by passing a known volume of exhaust through a dilution tunnel where it was diluted with a set volume of air to prevent the solids settling before passing the gases through a filter pad. The weight of particles enables a value for the particles in g/hr to be calculated. The particles present in the exhaust gas ware analysed further to give thermogravimetric weight, and the weight of volatile components, hydrocarbons, carbon and sulphate. Using the above method a number of filter pads were obtained for analysis. The weight of sulphate in the particles was measured by wet chemical analysis of the particles. Another sample was placed in a thermogravimetric balance where the sample was heated in an inert atmosphere to a temperature of 78O°C until the weight was constant. The weight loss between the initial weight and the new gives the weight of volatile components present. Air was introduced and heating continued until the weight was again constant. The difference in this weight and the value for the previous constant weight gives the weight of carbon components present. The remainder was ash and non-combustile material such as iron.
Baseline measurements were taken with a manifold connected to the engine in place of the apparatus. Measurements were taken up with the automobile driven through the LA4 cold start diesel cycle are given in Table 6 below, LA4 hot start diesel cycle results are given in Table 7 below, and the Highway driving test results are given in Table 8 below. The Highway test used was the standard test cycle used in the US for fuel consumption trials.
The results given in Tables 6 and 7 are shown in graphical form in Figures 5-9, LA4 cycle cold start, and in Figures 10 - 14 for LA4 cycle hot start. (Baseline figures dotted line and mofified engine continuous line).
The reduction in particle concentration (measured in g/mile) (g/1.6km) in a diesel engine according to the present invention is shown in column 3. Reductions in absorbed hydrocarbons and carbon present in the particles are shown in columns 7 and 9 respectively. Sulphate figures show an increase in some cases but the absolute level of the emission remains low.
Back pressure measurements were made. This is the difference in the pressure of the gases on leaving the engine exhaust ports and on leaving the chamber. The results are given in Table 9 for the automobile being driven through the LA4 cycle and in Table 10 for the Highway driving test.
PERCENTAGE DIFFERENCE id in σ> <*> .Η rd tt m tt o oo ή >-i TT OlfOHUIMtMH + + + +HIOH + + + + -46.3 +44.8 -41.3 -16.9 SULPHATE g/mile (g/1.6km) 0.009 kD H O) <*l σ» r* ca σ» id σ\ Ο ι—1 O CM KD rH rH o o o o o o o o 6 6 6 6 ο ό ό 6 0.0259 0.0139 0.0375 0.0152 0.0231 0.0192 PERCENTAGE DIFFERENCE O m in m m co η in in id in O tt cn io in in tt ie in n tt in 1 I 1 1 1 1 1 1 -61.9 -54.3 -55.8 -52.4 TOTAL PARTICLES g/mile (g/1.6km) 0.636 id η o ι-nr β v m 00 00 TT CJ rd r-l IO t- cn cn m cn 0.692 0.264 0.316 0.306 0.649 0.309 MILES O Ό V •Η V Ή C Ή «Η Ό 0» *"0888888 On® 0no Ο \o η η ω rn 5100 Baseline ..1 550 Modified Engine 6100 8500 12500 Baseline 12500 Modified Engine PERCENTAGE DIFFERENCE -39.7 Μ* Μ P* CX CO ι-l i-l l/WDrlcnH* ^•ΠίΛ^1^ 1 1 1 1 1 1 1 -56.4 -54.4 -46.6 -43.2 "e a e> OHIO r in m α η co CO 00 CQ -Ή · 00 M· Hinttinttioio CM ·—1 O i TT rd Sen 00 CO Ηΐ/ΙΓΊΝΗ OH XO o »-l CM < w co CM CM CM »H CM CM CO CM -M· CM CM CM XT CM υ σ» O' • • «·«···· • • • · • o o o o o o o o o o o o o o o W w 0 u < a a§ u » rH xo ox xo co σι cm co r—1 oo in xo U Pm • • • · Oi fa CM γ* σι xo cm ό· oo XO xo oo in W H 00 p* xo co t*· co r* r* XO P* p- fa Q 1 1 1 1 1 1 1 1 1 1 1 1 Ul a 2 e Q 8 fl) W < f-t vc CQ U · (M γ-ν φ hh On 00 r* p* ox rH KO Eh o co CO CM H m CM 00 CM co 00 ρ» co r-l OX O fa w 5P in r* co xo co co uo o xr xo O ω o O' O' CM o OOOOHOO CM o o o CM o Q >4 *-* • • ······ · • • • · • 2« o o o o o o o o o o o o o o o Ό 0) C V Ό a TJ Ή •Η φ Φ H Φ rM Ή C •Η φ r-4 •H a> 0) •H *H cn V c CQ Ό O' M co -H (3 o J3 u Ό O' (0 O' 0) S H H 0 C n o c 2 a w s w o o ο O Q Q O O o Q O o o ooooooo o o O O uo uo ΟΝβΟΌΝσι r4 o cM in CM CM o o XO r-4 <-| CO CO M· ·Μ» in in xo oo rd rd TABLE 6 (COLD START LA4) continued PERCENTAGE DIFFERENCE r~~ ninO r* id σι r* id ri in cn 1-4 | | «-4 cn F-l oo oo I + cn rl + + + + -1.0 +91.7 -5.7 21.2 SULPHATE g/mile (g/1.6km) 0.00802 σι id in CM O ID id r*ro)inHN^ Ο QQQd^NH O OOOOOOO • ······· O OOOOOOO 0.0193 0.0191 0.037 0.0182 0.0165 0.013 PERCENTAGE DIFFERENCE co 'J· 'i· cm io O' in o ro τ m «3 O't in io in io v >* in in 1 1 1 1 1 1 1 1 -58.6 -51.5 -49.3 i-4 • in «3» 1 TOTAL PARTICLES g/mile (g/1.6km) 0.572 1 inoo in h n m KD rl m ο rd o 00 ID CM CN CN CN cn cn CM CM ό όόόόόόό 0.548 0.227 0.226 0.278 0.521 0.286 MILES 0 Baseline Ό Φ *r| α> β Η Ή Ό σ* ο888888 Ο fN 00 ο ID σι Ο ID 1-4 r| cn cn 5100 Baseline 550 Modified Engine 6100 8500 12500 Baseline 12500 Modified Engine TABLE 7 (HOT START LA4) PERCENTAGE DIFFERENCE στ ^σιΟωηΝί m co i-i r-ι in -46.7 -39.0 -30.9 KO r-l CARBON g/mile (g/1.6km) 0.334 TT Nffl N t' TT Η Ί Ν η Ν πω •-ι ( στ to i-ι 0.3332 0.1775 0.203 0.23 0.296 0.238 PERCENTAGE DIFFERENCE «η ππ^ωπηοο ι-ι υ tt η π οι ωω oo co oo co r~~ io co oo 1 1 1 1 1 1 1 1 -84.5 -86.7 -84.7 -83.3 ADSORBED HYDROCARBONS g/mile (g/1.6km) 0.230 ci in co co in rn tt n to io ci Ο Ο ρ- O •η· Π ΠΠ IO c π π O OOOOOOO 6 OOOOOOO 0.1955 0.0304 0.026 0.0299 0.209 ro O 6 MILES 3 Baseline Ό V Η φ Ή C -Η -H UJ C} C O 8 S § 8 O O Ο ΓΊ CO O TO Cl OS Q_Ά rl η η n if -τ 5100 Baseline 550 Modified Engine 6100 8500 12500 Baseline 12500 Modified Engine TABLE 7 (HOT START LA4) continued PERCENTAGE DIFFERENCE +229.6 +633.0 +23.2 +35.5 CQ S En < rH VO σ» r*· VO rH X -H · vo in r- σν in m rH CN CM E ·-< rH m rH CN 00 cn u w o o o rH CN o o o O cn tn • • • • • • • ω 6 o o o o o o o w w o o < a H w a 2 u ω cn rH rH cn U Cm • • • • 05 Cm cn CN o o ω H cn CO rH CU Q + 1 1 w ~ « e q j < U r-l VO Η Η -H · CN in cn 00 vo in cn OH gn cn in σν σν rH in CN t*» H 05 W in cn •*f co VO in VO cn < O’ O’ • • • • • • • CM ~ o o o o o o o o Φ Ό Ό Φ Ό Φ Ό e Φ Φ Φ c Φ c Φ •rl •Η φ c •Η Φ •rl •Η Φ wH Η φ rH Ή C •H Ή C rH ή e rH Ή fi Φ •H -h ω rH •Η Ή Φ •Η ·Η Φ •Η «Η co Ό O’ CG 0) Ό O’ co Ό O' co Ό O’ (0 O C co 0 C5 0 C (0 o c BQ a BQ H (0 S W CQ a » n a w a BQ Q o O O O o o δ o O O O δ o m in 00 rH rH in in CN CN ..0..,, rH J£ VO oo 00 rH rH - 29 4»Β4Ο » Η ο α ft Ζ gg Η ω υ Cm « Cm w Η fit Ω W W ο α < ζ gg W Η Ο Cm fit Cm W Η CM Ο ω ζ αο ω m §δ < °y W Ο Ω Λ ft Ο X κ 0>r ω u Ω Η Ζ θ' 00 Ρ Ρ ιη • • • • ρ η ΙΟ 00 ρ Ρ CM Ρ + 1 I + Ό Φ β β Ρ V β Ρ σι ο σι Ρ ιο ιο 01 Γ0 <Ν ο Ο CM ο ^9· ΙΟ Ρ ιο Ρ ρ CM ΓΟ X Ρ Xf ΓΟ CM *—» , • • « • • • Ε» ο 6 ο ο ο ο ο ο TES Ο Ζ Η > Ρ Λ ο Ό ιη ιη Ω • • CM ΙΟ ιη χ X Τ 00 k ιη Ρ 1 < S η *"* 00 ω Ω CM ρ X ιη Ρ Ρ ιο 00 σι CM ro σ» ο 00 ο X νο CM CM σι Γ0 σι Ε-« ΓΜ ο ρ ο CM ο CM ο • • • • • • ο ό ο ο ο ο ο ο φ τ) *0 φ Ό φ Ό β φ φ φ C φ β Φ Ρ Ρ Q) c *1-1 φ Ρ Ρ φ ρ -Η φ Ρ Ή β Ρ C Ρ «Η C Ρ Ή β φ Ρ Ρ Φ Ρ Ρ φ Ρ Ρ (0 Ό Cn φ Ό 0» (0 ό σ» (0 Ό θ' φ Ο β α Ο β φ 0 (4 φ 0 C α ζ ω <β Ζ bl ffl Ζ Μ Λ Ζ Η CQ ο Ο Ο ο Ο Ο Ο ο ο Ο ο Ο Ο Ο ιη ιη 00 Ρ ιη ιη CM CM .0— Ρ £ Ωβ- 00 οο d Ρ - 30 TABLE 9 Back pressure in inchee of mercury Miles Baseline Covered (or bar) After catalyst chamber (km/1.6) Max.
Average Max.
Average Hot Start 3.12 (0.11) 0.63 (0.02) 1800 4200 4900 5500 6100 2.42 (0.08) 0.65 (0.02) 8500 12500 2.88 (0.10) 3.42 (0.12) 3.8 (0.13) 3.67 (0.12) .35 (0.18) 4.58 (0.16) 3.31 (0.11) 2.38 (0.08) 0.75 (0.03) 1.0 (0.03) 0.98 (0.03) 0.91 (0.03) 1.9 (0.06) 1.43 (0.23) 0.96 (0.03) 0.85 (0.03) Cold Start 0 2.64 (0.09) 0.48 (0.02) 3.54 (0.12) 0.86 (0.03) 1800 3.15 (0.11) 1.15 (0.04) 4200 4.6 (0.16) 0.96 (0.03) 5 4900 4.5 (0.15) 0.95 (0.03) 5500 4.86 (0.16) 1.65 (0.06) 6100 *4.84 (0.16) 0.61 (0.02) 4.62 (0.15) 1.38 (0.05) 8500 3.28 (0.11) 0.95 (0.03) 12500 2.5 (0.08) 0.83 (0.03) 10 * High figure probably due to build up of carbon deposits - 32 Back Miles Covered (km/1.6) 1800 6100 8500 TABLE10 pressure in inches of mercury (or bar) Baseline Max.
After catalyst chamber Average Max.
Hot Start Average 3.34 (0.11) 1.98 (0.07) 2.0 (0.07) 1.1 (0.04) 4.05 (0.14) 2.9 (0.10) 3.12 (0.11) 2.0 (0.07) TABLE 11 Miles Covered 5 (km/1.6) 8500 Back pressure Baseline Max. 2.88 (0.10) 4.48 (0.06) in inches of mercury (or bar) Average 0.56 (0.02) 0.61 (0.02) After Catalyst chamber Max. 3.20 (0.11) 4.62 (0.16) Average 0.80 (0.03) 1.38 (0.05) In have been the foregoing description the following abbreviations used and their meanings are indicated.
CVS constant volume sampling.
LA4 Los Angeles Cycle as laid down by the Environmental Protection Agency (EPA) of the United States and is a standard test cycle devised to simulate a drive to work in Los Angeles traffic conditions. It is furthermore a test to which all new vehicles are subjected. ·» ** ο υ Taxi cycle A test cycle of about 50 miles (80km) long approved by EPA and carried out at low speeds up to 25 mph (40kmph) and includes periods when the car is stationary and the engine is idling.

Claims (15)

1. CLAIMS:1. A process for enabling the oxidation of particles in exhaust gas emitted from a diesel engine to be initiated at temperature of from 200 to 400°C which
2. A process according to claim 1 wherein the chamber casing has a plurality of entry ports in communication with a plurality of exhaust ports in the engine. 20
3. A process according to claim 1 or claim 2 wherein the filamentary metallic material is in the form of wire having a thickness of from 0.025 to 0.5 mm (ie 0.001 to 0.02 inches)
4. A process according to claim 3 wherein prior to its fabrication into woven or knitted form, the wire is 25 rolled down to a ribbon having two flat opposite surfaces. 5. 10. A combination according to claim 9 wherein prior to its fabrication into woven or knitted form, the wire is roiled down to a ribbon having two flat opposite surfaces. 5 suitable for oxidising carbon particles in exhaust gas emitted from the engine wherein (a) the apparatus comprises a casing defining a chamber having one or more entry ports in communication with one or more exhaust ports
5. A process according to any one of the preceding claims wherein the catalyst comprises a metal chosen from platinum, rhodium, or palladium or their alloys. 5 comprises passing the exhaust gas through a chamber containing an interstitial catalyst system comprising a catalyst, a layer of refractory metal oxide and a support comprising filamentary metallic material in a knitted or woven form, the catalyst being disposed on or throughout the
6. A diesel engine in combination with apparatus
7. A combination according to claim 6 wherein the outer and central passageways and the catalyst system extend in a direction transverse of the entry port or ports whereby exhaust gas passing through the passageways flows in a direction transverse of the entry port or ports.
8. A combination according to claim 6 or claim 7 wherein the apparatus comprises a chamber having a plurality of entry ports in communication with a plurality of exhaust ports in the engine. • 49846
9. A combination according to any one of Claims 6 to 8 wherein the filamentary metallic material is in the form of wire having a thickness of from 0.025 to 0.5 mm (ie 0.001 to 0.02 inches)
10. To 10 wherein the catalyst comprises a metal chosen from platinum, rhodium, or palladium or their alloys. 10 in the engine and having an exit port from which exhaust gas can be taken to atmosphere whereby exhaust gas from the engine can be passed through the chamber, (b) the chamber contains an interstitial 15 catalyst system comprising a catalyst, a layer of refractory metal oxide and a support comprising filamentary metallic material in a knitted or woven form, the catalyst being disposed on or throughout the layer of refractory 20 metal oxide which in turn is disposed on the surface of the filamentary metallic material, (c) the catalyst system is mounted within the chamber spaced from the casing so as to define an outer passageway, and is shaped so as to define 25 a central passageway within the catalyst system, 37 10 (d) one of the passageways communicates with the entry port or ports and the other communicates with the exit port and the catalyst system is positioned so that the exhaust gas discharged from the engine is caused to pass through one passageway then into the interstitial catalyst system and through the other passageway, (e) the outer and central passageways and the catalyst system are aligned relative to the entry port or ports such that exhaust gas passing through the chamber is caused to flow in a direction transverse of the entry port or ports during a portion of its passage through the chamber thereby increasing turbulence within the interstitial catalyst system. 10 layer of refractory metal oxide which in turn is disposed on the surface of the filamentary metallic material wherein the exhaust gas is passed into the chamber in a first direction and caused to pass in a direction transverse to the first direction during a portion of its passage through 15 the chamber thereby increasing turbulence within the interstitial catalyst system.
11. A combination according to any one of Claims 6
12. A process for oxidising particles in exhaust gas emitted from a diesel engine substantially as herein described and illustrated in Examples 2 to 5. 15
13. A process for oxidising particles in exhaust gas emitted from a diesel engine substantially as herein described and illustrated in the drawings.
14. A combination of a diesel engine and apparatus suitable for oxidising carbon particles in exhaust gas emitted 20 from the diesel engine substantially as herein described and illustrated in Examples 2 to 5.
15. A combination of a diesel engine and apparatus suitable for oxidising carbon particles in exhaust gas emitted from the diesel engine substantially as herein described and illustrated in Figures 2 to 14 of the drawings.
IE1344/80A 1979-06-29 1980-06-27 Exhaust gas purification IE49846B1 (en)

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ZA837689B (en) * 1982-10-18 1984-06-27 Universal Matthey Prod Oxidation catalysts
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FR2633664B3 (en) * 1988-07-08 1990-06-08 Piaggio & C Spa COMBUSTION PRODUCTS EXHAUST DEVICE FOR A TWO-STROKE ENGINE
DE68900928D1 (en) * 1988-10-12 1992-04-09 Johnson Matthey Plc METAL FABRIC.
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US5258340A (en) * 1991-02-15 1993-11-02 Philip Morris Incorporated Mixed transition metal oxide catalysts for conversion of carbon monoxide and method for producing the catalysts
DE4229471A1 (en) * 1992-09-03 1994-03-10 Man Nutzfahrzeuge Ag Process for the purification of exhaust gases from diesel engines
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NL8003699A (en) 1980-12-31
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IT1136188B (en) 1986-08-27
IT8012584A0 (en) 1980-06-27
SE8004632L (en) 1980-12-30
DE3024491A1 (en) 1981-01-29
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CA1165247A (en) 1984-04-10
DK155541B (en) 1989-04-17
DK155541C (en) 1989-10-16
FR2460388B1 (en) 1987-03-20
LU82550A1 (en) 1980-10-24

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