CA1100292A - Catalysis - Google Patents

Catalysis

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Publication number
CA1100292A
CA1100292A CA274,184A CA274184A CA1100292A CA 1100292 A CA1100292 A CA 1100292A CA 274184 A CA274184 A CA 274184A CA 1100292 A CA1100292 A CA 1100292A
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Prior art keywords
catalyst
process according
oxide
silica
run
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Expired
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CA274,184A
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French (fr)
Inventor
Stephen J. Knight
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Johnson Matthey PLC
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Johnson Matthey PLC
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    • 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
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/92Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9404Removing only nitrogen compounds
    • B01D53/9409Nitrogen oxides
    • B01D53/9413Processes characterised by a specific catalyst
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/10Noble metals or compounds thereof
    • B01D2255/102Platinum group metals
    • B01D2255/1025Rhodium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/10Noble metals or compounds thereof
    • B01D2255/102Platinum group metals
    • B01D2255/1028Iridium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/206Rare earth metals
    • B01D2255/2063Lanthanum
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/206Rare earth metals
    • B01D2255/2065Cerium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/20707Titanium

Abstract

ABSTRACT OF THE DISCLOSURE

This invention relates to catalytic processes for the purification of air and other gaseous media, for example, exhaust gases from industrial plant and automobiles.
In particular, the invention is concerned with contacting the gas at an elevated temperature with a catalyst compris-ing one or more of the metals platinum, rhodium, iridium, osmium, palladium, ruthenium, gold and silver supported on or associated with a refractory oxide support made from silica, alumina or mixtures or compositions containing silica and/or alumina.

Description

110~292 : `' ; This invention relates to a catalytic process for use in the purification of air and other ga~eous media. More particularly, it relates to the catalytic removal of one or more oxides of nitrogen, especially in the presence of excess oxygen, and also to the catalytic removal of carbon monoxide and organic compounds such as the lower hydro-carbons.
The exhaust gases from an internal combustion engine include - oxygen, carbon monoxide, unburnt hydrocarbons and nitrogen oxides. If the engine is fuelled by petrol, the oxygen is generally present in a stoichio-metrically lean concentration, that is, the atmosphere is a "net reducing atmosphere". Under such conditions, the nltrogen oxides may be catalytically reduced in one catalyst bed and the carbon monoxide and hydrocarbons may be mixed with additional oxygen and catalytically oxidised in a second catalyst bed. If, on the other hand, the engine is fuelled by diesel, there is a stoichiometric excess of oxygen in the exhaust gases and the nitrogen oxides may only be catalytically reduced after adding an excess of a reducing fuel. The exhaust of a petrol~fuelled internal combustion engine will also be oxygen-rich under certain operating conditions.
In the manufacture of nitric acid, tail gases contain appreciable quantities of N0 and other oxides of nitrogen which it is desirable to remove before venting .

to atmospllcre.
Accordillg to one feature of the invention, a process for the cat;alytic removal of oxides of nitrogen present in a gas comprises contacting the gas at elevated temperature with a catalyst comprising one or more metals from the platinum group, gold and silver, supported on or associa-ted with a refractory oxide.
By "the platinum group" we mean platinum, rhodium, iridium, osmium, palladium and ruthenium, and of these we particularly prefer to use platinum, rhodium or iridium.
The metals may be alloyed together, or may be present as a mixture or alloy with one or more base metals or one or more precious metals, other than those of the platinum group.
The refractory oxide may be an oxide or a mixture of oxides of elements of Groups IIA, IIB or IVB of the Periodic Table, or of the transition metals. Such elements are, for example, beryllium, magnesium, calcium, scandium, yttrium, titanium, zirconium, aluminium, silicon or germanium. Additionally, such compounds as the aluminos-ilicates may be used. We prefer to use either silica or alumina, or mixtures or compositions c,ontaining silica and alumina, or an aluminosilicate.
A process according to the present invention will remove oxides of nitrogen from a gas under either reducing or oxidising conditions Under oxidising conditions, removal may occur either by decomposition or by selective reduction.
Such a process represents a - -considerable advance in the technology of purification of petrol and diesel exhaust gases and nitric acid tail gases.
- According to a further feature of the invention, a process for the catalytic removal of oxides of nitrogen and the catalytic oxidation of carbon monoxide and hydrocarbons present in a gas comprises contacting the gas at elevated temperature with a catalyst comprising one or more metals of the platinum group supported on or associated with a refractory oxide, where "platinum group" and "refractory oxide"- have meanings as defined above. In its most important embodiment, the present invention provides a process for the catalytic reduction under oxidizing conditions for one or more oxides of nitrogen present in the exhaust from an internal combustion engine or from an industrial plant gas which comprises contacting the gas under oxidizing condi*ions at an elevated tem-perature with a metal catalyst comprising at least one metal selected from the group consisting of platinum, rhodium, and palladium metals supported on a particulate silica support, said particulate oxide support being itself deposited on a catalyst substrate.
Optionally, the catalyst may be associated with one or more other catalytic metals or metal oxides to assist in pro-moting the oxidation reaction.
Under certain circumstances, the catalytic decomposition of nitrogen oxides may lead to the formation of nitrous oxide. A
further option, therefore, is that the catalyst be associated with one or more catalytic metals or oxides to promote the reduction or decomposition of nitrous oxide. We have found that oxides of one or more of lanthanum, cerium and titanium are particularly useful ~.' for this purpose.
By "elevated temperature" we mean a temperature sufficient for catalytic decomposition of a significant quantity of the oxide of nitrogen etc. present or catalytic oxidation of a significant quantity of the organic compound - 4a -.

~, ~

-' or carbon monoxide present to occur as a result of contact with a catalyst such as described above. In general; the elevated temperature would not exceed about 500-600 C. and, depending upon the exact nature of the catalyst, the optimum temperature could be in the region of 300~450 C.
The refractory oxide on which the catalytic metal or mixture of metals is deposited or with which it is associated, may be in the form of pellets, granules or powders but is preferably in the form of fine grains, the individual grains being typically slightly coarser than particles of powder.
An example of a suitable refractory oxide is Davison 70 (T.M.) silica.
The catalyst is optionally ultimately supported on a substrate known in the art. Examples of preferred substrates which may be used are porous refractory ceramic honeycombs or modules formed from corrugated metallic sheets rolled up to form a cellular structure. Other supports may be used, however, forlexample particulate solids sueh as granules, pellets, shapes and extrudates which can be constructed of ceramic or metallic refractory materials. Alternatively, the catalyst may be mixed with a catalytically inert refractory material, for example in the form of granules, as an extender or diluent.
The ultimate supporting structure may have a first coating, layer or deposit of a refractory oxide - 5 .
,.~

which may be the same as or different from the refractory oxide on which the catalytic metal is supported. This first refractory oxide is deposited on the ultimate support, preferably in the form of a film, and the film may have a thickness of 0.0004 to 0.001 inches.
Such oxides are calcined and preferably have a porous structure which has a relatively large internal pore volume and total surface area.
Such oxides are referred to as "active", that is, catalytically active, refractory oxides.
Refractory oxides suitable for this purpose may be selected from the group consisting of silica, silumina, silica/alumina, titania, zirconia, magnesia, quartz and proprietary molecular sieve zeolites.
Catalysts for use in the process of the invention may be deposited directly on the support without the intervention of an intermediate refractory oxide layer. Such an arrangement includes a catalyst comprising a platinum group metal supported on or associated with, for example, silica and deposited on a ceramic or metallic ultimate support, so that, although no separate intermediate refractory oxide layer is included, the refractory oxide of the catalyst acts in lieu of such an intermediate layer.
' , .

.

In addition to Davison 70 silica a range of colloidal suspensions sold under the trade mark SYTON by Monsanto may be used. For example, "Syton X30" which has a silica concentration of approximately 30%, has been used for applying silica to both ceramic and metallic monoliths prior to applying the precious metal.
The general procedure of preparation of such catalysts is to dip the monolith directly into the "Syton" solution, blow off the excess from the channels and surface of the monolith, dry and fire, and then to apply the precious metal by dipping into an aqueous solution of precious metal salt followed by drying and reducing in a stream of H2/N2. Metal supports (e.g. Fecralloy (T.M.) should be pre-oxidised by heating for 1 hour at 130C.
This has the effect of improving corrosion resistance to the gases with which the catalyst will come into contact and also improving the adhesion of the silica layer. Also, since metal supports, unlike ceramic supports, are not porous, two immersions in the silica sol, each followed by drying etc, are necessary to build up the desired coating of silica.
In detail, one method of applying a ca alyst according to the invention on a ceramic support will now be described.
A ceramic honeycomb monolith (Corning M20 (T.M.)~; 300 cells per square inch) made from cordierite and being in the shape of a cylinder 2 inches in diameter and 3 inches in length and therefore having a volume of 9.42 cu. ins. was immersed in 500 ml of Syton X30, the silica therein having a surface area in excess of 200 m2g-1, for 2 minutes. After withdrawal, the excess silica sol was first shaken off s~
.

and then blown off at an air pressure of 15 p.s.i. The weight of the monolith had increased from 92 to 108 g. The ~oated monolith was then dried at about 100C in a convection current of hot air flowing at>300 ft.min. 1 and was then roasted in a static kiln furnace at 500 C for ~ hour. The resulting coated monolith weighed 97.2 g, hence the weight of silica was 5.2 g which represented a loading of 0.55 g.in 3.
The film thickness represented by this loading falls within the range previously mentioned namely 0.0004 - 0.001 inch.
To deposit the precious metal on the silica, the following method was used:
The water absorption of the silica-coated monolith was measured and the amount of precious metal xequired to give a loading of 30 g.ft 3 of monolith was calculated. ~n aqueous solution of precious metal salt, for example, RhC13.xH20, at a concentration of 14 g.l 1 of Rh metal was made up and the silica-coated monolith immersed for 2 minutes in the solution, removed, allowed to drain and the excess salt solution blown off. The process was repeated, if and as necessary, until the predetermined weight, that is, of silica-coated monolith carrying the required quantity of solution corresponding to a metal loadlng of 30 g.ft 3, was achieved.
The process was completed by hot air drying and reduction in a tube furnace for one hour under an atmosphere of H2/N2 containing 5% H2 at 450 C (for rhodium) and 220C (for iridium).
Methods of deposition of oxide are described in our British Patent Specification No. 1,390,182. Descriptions of typical ceramic supports and useful metal supports which may be used are given in British Patent Specification No. 882,484 ~Corning) and in our published DOS No. 2,450,664.
The following descriptions, examples, tables and figures are illustrative of the invention.
Preparation of the Catalysts - Catalysts comprising pla*inium, rhodium and iridium supported on Davison 70 silica were prepared by impregnation of the silica with a solution of the relevant chloride or acid chloride of the required strength and volume. The impregnated silica was then dried in vacuo (0.1 torr) at room temperature and reduced in a stream of hydrogen at 350C. (for platinum) and 450C. (for rhodium and iridium).
The following silica-supported catalyts were pre-pared using the above method.

` ' , , , . ~
Catalyst A Rh/SiO2 6.14 x 10 2At~ (approx. 0.1 w/w%) Catalyst BRh/SiO2 6.14 x 10 At% (approx. 0.1 w/w%) Catalyst CPt/Sio2 6.14 x 10 At% (0.2 w/w%) Catalyst D`Pt/Sio2 6.14 x 10 At% (0.02 w/w%) Catalyst EIr/SiO2 6.14 x 10 At~ (approx. 0.02 w/w%) . .

g _ llC3~Z92 I

.
In the above table, atomlc percentages are quoted as atoms of the metal calculated as a percentage of the number of moles of silica.
In a similar way, weight percentages are expressed as weight of metal to ! weight of silica.
Experimental Test Rig The experimental runs, results of which are given below, were ¦ carried out in a silica reactor comprising two concentric tubes mounted ¦ vertically. The outer tube had an o.d. of about l~" and the inner tube had an o.d. of about 3/8". The catalyst was carried on a bed of silica wool in the inner tube and the reaction gas stream was passed down the outer tube and up the inner. The gases were passed through a pre-heating zone upstream of the catalyst. Reactor gas inlet temperature was measured by means of a chrome-aluminel thermocouple located in a well below the catalyst. The reactor was surrounded by a heater equipped to give variable heating rates. The inlet and outlet concentration of gases was monitored using a BOC Luminox Analyser and Perkin-Elmer ~17 gas chromatograph.
Experimental Results~and Discussion Two principal types of experiment were conducted on the catalysts. These were:
(a) a profile of activity in removal of oxides of nitrogen versus inlet temperature at a fixed ratio of oxidising to reducing species in the inlet gas stream; and (b) an isothermal profile of activity against ratio at a temperature chosen from the result of experiment type (i).
The ratio (R) of oxidising to reducing species in the inlet gas stream is calculated according to the equation - lU ~

`'';~' R 2 2 x %2 ~ ~ NOx .
. ' ~ CO
~ Generally, the particular oxide of nitrogen (NOx) in the ~, equation is nitric oxide, NO.
In the experiments described below, the weight of catalyst tested was generally lg. In some experiments, smaller weights were tested, typically 0.005 g., but in all experiments using less than 1 g. of catalyst, pure silica was added as an extender to the catalyst to give a total weight of 1 g. in order to prevent bed fluidisation.
Space velocity was calculated on the basis of catalyst weight exclusive of the weight of added pure silica, if present, and is quoted in units of hr 1 Experimental runs were conducted as in the following table (Table 2) in which the "Catalyst" designation refers to Table 1, the "Experimental type" refers either to (a) or (b) as above, and the "R or temperature" refers to the fixed ratio R (for experimental type ~a)) or to the isothermal temperature (for experimental type (b)).

1:

,................. ... _ .. . .. ~

PS E~ _ _u~ _~ u) ., . o o ~ ~

X ~

t~ ~ ~1 O oNO o o o oO o o o o o ,, 0~_1 C~ O O C~ `1' 0 0 ~ I V

O ~ N u ) ~ 0~ ~ V

~!~ ~ L~

u nl~0 0 G t~ O 0 ~ V

V ~ _ ¢ ¢ ¢
._ . . Cd Z~ ~
~ 1~ ~ O ~ ~`I ~ .-1 1~ . _ ~ 1~

~` 12;

11(3~Z9~

Run l shows the actiVity of a ~h/SiO2 catalyst at an R value of 1.9 (i.e. oxidising conditions). NOx decomposition showed a maximum of 95% at about 230C. and the "half peak activity range" (that is, the active temperature range at half the maximum activity) was 220C. Nitrous oxide formation (as a percentage of the total NOx input) reaches a maximum just above the NOx decomposition threshold temperature and decreases steadily to zero at about 450C.
Run 2 was carried out under similar conditions to Run 1 using the same catalyst, except that the actual catalyst weight was 0.005g.
instead of lg. ~he effect of this was to raise the temperature of maximum activity to 400 C. At this temperature, decomposition of NOx is still 75%
despite the small amount of catalyst and the correspondingly high space velocity compared with Run 1. Formation of N20 did not rise above 18% and, at the temperature of maximum decomposition of NOx, was already dropping rapidly.
Run 3 was carried out using the same catalyst as Run 2 but under isothermal conditions, a temperature near the maximum activity of NOx decomposition from Run 2 being selected (395 C.). Maximum NOx decomposition (and minimum N20 formation) occurred at about the stoichiomet~ic point (R=l) and the value of R at 50% of the maximum NOx decomposition was 2.8.
Run 4 used ig. of a Rh/SiO2 catalyst of lower metal loading compared to Runs 1, 2 and 3. Diluting the metal loading results in a lower maximum of NOx decomposition at a higher temperature, and also a lower half-peak activity of 160C.
Run 5 - the isothermal plot using the catalyst of Run 4 -showed that the catalyst was less resistant to oxygen poisoning between R
values of about 1 and 5 and that production of N20 was higher than with the I` 110~29Z

similar catalyst of higher metal loading. The value of R at 50% of maximum NOx decomposition was 2.5.
Run 6 used lg. of a Pt/SiO2 catalyst and is comparable to Run 1 using a similarly loaded Rh/SiO2 catalyst. The results of Run 6 indicated that the maximum activity in NOx decomposition for Pt/SiO2 was only 50% compared with 95% for Rh/S102. However, this poor result does not necessarily reflect accurately the true activity of thls catalyst since little is known as yet about the relatlve dispersions of the metals on silica. The half~peak activity or Pt/SiO2 was 200C. compared to 220C. for Rh/SiO2.

Run 7 used 0.005g. of the same catalyst and is therefore comparable to Run 2. As in Run 2, lowering the quantity of catalyst increased the temperature of maximum activity in NOx decomposition but the maximum decomposition was only 17%.
Run 8 was carried out under isothermal conditions at a tempera-ture of 400C. Compared to Run 3 tusing Rh/SiO2 catalyst) the resistance to oxygen poisoning was poor. The value of R at 50% of maximum NOx decompo-I sition was 1.25.
Run 9 was carried out using lg. of a Pt/SiO2 catalyst havinga lower metal loading than that used in Runs 7 and 8. Run 9 therefore compares with Run 4 for Rh/SiO2 and the results show that Pt/SiO2 is inferior to Rh/SiO2 in respect of NOx decomposition and about the same for half peak activity.
Run 10 was carried out under isothermal conditions at a temperature of 360C. Again, comparing the results with Run 5, Pt/SiO2 shows less resistance to oxygen poisoning than does Rh/SiO2. The value of R at 50%
of maximum NOx decomposition was 1.7.
Run 11 used an Ir/SiO2 catalyst and compareswith Run 4 ~Rh/SiO2) and Run 9 (Pt/SiO2). Maximum Nox decompositlon was 65% at 345 C. and at this temperature production of N20 was vir-tually zero. Half peak activity was Run 12 was a re-run of Run 11, using the identical catalyst, and shows the remarkable effect of heating to 600C. in Run 11. Maximum Nox decomposition was 90% at a temperature of 350 C. and production of N20 was still extremely low, peaking at 2%. The half peak range was comparatively sharp at 100C.
Run 13, the isothermal experiment on Ir/SiO2 at 329C., shows that this catalyst is considerably more resistant to oxygen poisoning than either Rh/SiO2 (Run 5) or Pt/SiO2 (Run 10). The value of R at 50% of maximum NOx decomposition was 5. N20 production is consistently either very low or zero throughout the entire range of R.
In conclusion, it may readily be seen that these catalysts show remarkable results for the decompositlon of NOx under oxidising conditions.Furthermore, all of them showed high efficiency in the oxidation of carbon monoxide and it is anticipated that these catalyst, either alone or in asso-ciation with known oxidation catalyst, for example alloys of the precious metals such as Pt/Rh, will successfully oxidise the lower hydrocarbons typically- 20 present in the exhaust gas stream from an internal combustion engine.
Rh/SiO2 and Pt/SiO2 tended under certain conditions to cause the formation of nitrous oxide. We have found that certain additives may be incorporated or admixed with the catalysts to catalyse the reduction or de-composition of nitrous oxide. Examples of such additives are oxides of lanthanum, cerium and titanium.

Claims (10)

THE EMBODIMENTS OF THE INVENTION IN WHICH AN EXCLUSIVE
PROPERTY OR PRIVILEGE IS CLAIMED ARE DEFINED AS FOLLOWS:
1. A process for the catalytic reduction under oxidizing conditions of one or more oxides of nitrogen present in the exhaust from an internal combustion engine or from an industrial plant gas which comprises contacting the gas under oxidizing conditions at an elevated temperature with a metal catalyst comprising at least one metal selected from the group consisting of platinum, rhodium, and palladium metals supported on a particulate silica support, said particulate oxide support being itself deposited on a catalyst substrate.
2. A process according to claim 1 wherein the metals are present in the form of an alloy or as a mixture.
3. A process according to claim 1 or claim 2 wherein the catalyst includes one or more base metals or one or more precious metals not specified in claim 1.
4. A process according to claim 1 wherein the catalyst includes at least one additional metal or oxide for promoting the reduction of nitrogen oxide.
5. A process according to claim 4 wherein the oxide is an oxide of at least one of lanthanum, cerium and titanium.
6. A process according to claim 1 wherein the gas is automobile exhaust gas.
7. A process according to claim 1 wherein the substrate is made from a refractory oxide in the form of a honeycomb.
8. A process according to claim 1 wherein the substrate is made from a metallic sheet material in the form of a cellular structure.
9. A process according to claim 1 wherein the elevated temperature is within the range 500-600°C.
10. A process according to claim 9 wherein the elevated temperature is within the range 300-450°C.
CA274,184A 1976-03-18 1977-03-17 Catalysis Expired CA1100292A (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
GB10953/76A GB1581628A (en) 1976-03-18 1976-03-18 Catalytic purification of automobile exhaust gases
GB10953/76 1976-03-18

Publications (1)

Publication Number Publication Date
CA1100292A true CA1100292A (en) 1981-05-05

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JP (1) JPS52116779A (en)
BE (1) BE852590A (en)
CA (1) CA1100292A (en)
DE (1) DE2712009A1 (en)
FR (1) FR2344323A1 (en)
GB (1) GB1581628A (en)
SE (1) SE7703019L (en)
ZA (1) ZA771544B (en)

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US5924280A (en) * 1997-04-04 1999-07-20 Clean Diesel Technologies, Inc. Reducing NOx emissions from an engine while maximizing fuel economy
US5976475A (en) * 1997-04-02 1999-11-02 Clean Diesel Technologies, Inc. Reducing NOx emissions from an engine by temperature-controlled urea injection for selective catalytic reduction
US6203770B1 (en) 1997-05-12 2001-03-20 Clean Diesel Technologies, Inc. Urea pyrolysis chamber and process for reducing lean-burn engine NOx emissions by selective catalytic reduction
US6361754B1 (en) 1997-03-27 2002-03-26 Clean Diesel Technologies, Inc. Reducing no emissions from an engine by on-demand generation of ammonia for selective catalytic reduction
US6592833B1 (en) * 1999-10-18 2003-07-15 Delphi Technologies, Inc. Method of NOx abatement in high temperature lean NOx catalyst systems
US7090810B2 (en) 2000-12-01 2006-08-15 Fuel Tech Inc. Selective catalytic reduction of nox enabled by sidestream urea decomposition
US7682586B2 (en) 2006-08-22 2010-03-23 Babcock Power Environmental, Inc. Thermal decomposition of urea in a side stream of combustion flue gas using a regenerative heat exchanger
US7829033B2 (en) 2003-07-03 2010-11-09 Fuel Tech, Inc. Selective catalytic reduction of NOx enabled by sidestream urea decomposition
US8017100B2 (en) 2007-04-27 2011-09-13 Babcock Power Environmental Inc. Conversion of urea to reactants for NOx reduction

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WO1993022046A1 (en) * 1992-05-01 1993-11-11 Nalco Fuel Tech Process for the efficient catalytic reduction of nitrogen oxides
US5298230A (en) * 1992-05-01 1994-03-29 Nalco Fuel Tech Process for the efficient catalytic reduction of nitrogen oxides
US6361754B1 (en) 1997-03-27 2002-03-26 Clean Diesel Technologies, Inc. Reducing no emissions from an engine by on-demand generation of ammonia for selective catalytic reduction
US5976475A (en) * 1997-04-02 1999-11-02 Clean Diesel Technologies, Inc. Reducing NOx emissions from an engine by temperature-controlled urea injection for selective catalytic reduction
US5924280A (en) * 1997-04-04 1999-07-20 Clean Diesel Technologies, Inc. Reducing NOx emissions from an engine while maximizing fuel economy
US6203770B1 (en) 1997-05-12 2001-03-20 Clean Diesel Technologies, Inc. Urea pyrolysis chamber and process for reducing lean-burn engine NOx emissions by selective catalytic reduction
US6592833B1 (en) * 1999-10-18 2003-07-15 Delphi Technologies, Inc. Method of NOx abatement in high temperature lean NOx catalyst systems
US7090810B2 (en) 2000-12-01 2006-08-15 Fuel Tech Inc. Selective catalytic reduction of nox enabled by sidestream urea decomposition
US7829033B2 (en) 2003-07-03 2010-11-09 Fuel Tech, Inc. Selective catalytic reduction of NOx enabled by sidestream urea decomposition
US7682586B2 (en) 2006-08-22 2010-03-23 Babcock Power Environmental, Inc. Thermal decomposition of urea in a side stream of combustion flue gas using a regenerative heat exchanger
US8017100B2 (en) 2007-04-27 2011-09-13 Babcock Power Environmental Inc. Conversion of urea to reactants for NOx reduction

Also Published As

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BE852590A (en) 1977-09-19
DE2712009A1 (en) 1977-09-22
GB1581628A (en) 1980-12-17
JPS52116779A (en) 1977-09-30
FR2344323A1 (en) 1977-10-14
SE7703019L (en) 1977-09-19
ZA771544B (en) 1978-01-25

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