Title of Invention

"PROCESS FOR THE PREPARATION OF A CATALYST COMPOSITION COMPRISING TIO2, WO3, AND A RARE EARTH METAL VANADATE"

Abstract

"Process for the preparation of a catalyst composition comprising TiO2, WO3, and a rare earth metal vanadate" wherein RE is at least one of the group of rare earth metals Y, Ce, Pr, Nd, Sm, Er, and Yb in an amount of up to 6.0 wt.-%; V is vanadium in an amount of 0.2-2.5 wt.-% O is oxygen in an amount of up to 3,5 wt.-%; and S is a support containing TiO2 in an amount of at least 70 wt.-%, with the rest being WO3 and optionally SiO2. This catalyst composition shows high removal efficiencies for NOx even after aging at 750° C.

Full Text

EXHAUST GAS CATALYST The invention relates to an exhaust gas catalyst composition, in the following "catalyst composition", and a process for its preparation. The reduction of nitrogen oxide emissions represents one of the greatest challenges in environmental protection. Several approaches have been followed to reduce NOX emissions for both mobile and stationary applications including combustion modification methods and denitrification of flue gases. The former, although NOX removal efficiency varies with the technology applied, cannot achieve more than 50-60% of removal efficiency. After-treatment of flue gases can achieve substantially larger efficiencies especially when a catalytic method is employed. Several type of catalysts have been tested which are active under different environments and conditions. The use of a large number of catalysts to eliminate NO is associated with different reaction pathways that can be divided as follows (1): 1. The selective catalytic reduction of NO with ammonia (herein after referred to as SCR), for stationary applications like power stations and chemical industrial plants. 2. The catalytic reduction of NO in the presence of CO, typical of automotive pollution control. 3. The catalytic reduction of NO in the presence of hydrocarbons, a method not in use commercially but potentially interesting for automotive and industrial pollution control. 4. The direct elimination of NO through decomposition for which a durable and stable catalysts has not yet been developed. 5. The sorbing of NO or NOx-trap catalysts. Among these methods the most widely employed technology for stationary applications is SCR (2-4). It was introduced in the late 1970s for the control of NOX emissions in stack gases for thermal power plants and other industrial facilities. SCR plants are currently operating in USA, Japan, Europe and Far East for a total capacity of the order of 180000 MW. The SCR is based on the reduction of NOX with NH3 into water and nitrogen according to the reaction: 4NO + 4NH3 + O2 = 4N2 + 6H2O The technology is operated commercially over metal-oxide SCR catalysts made of a homogeneous mixture of TiO2 (80-90 wt.-%), WO3 (6-10 wt.-%) and V2O5 (up to 3 wt.-%) which may contain some SiO2 (0-10 wt-%) in the formulation. Titania is used as an active support of high surface area to support the active component V2O5 which is responsible for the activity of catalysts for NOX reduction at low and medium operation temperatures. It is also responsible for the oxidation of SO2 to S03 when SO2 containing gases are delivered to the catalyst. Therefore, for high-sulfur content off-gases, its amount is kept low (below 1 wt-%). WO3 (sometime also MoO3 is employed as a chemical/structural promoter to enlarge the temperature window of application. Silica is often used to improve the catalyst strength and stability. Commercial catalysts are employed as honeycomb monoliths due to several advantages over a packed bed arrangement: lower pressure drop, higher attrition resistance, less plugging by fly ash. GB 1 495 396 describes a catalyst composition containing as active ingredients oxides from titanium, at least one of molybdenum, tungsten, iron, vanadium, nickel, cobalt, copper, chromium and uranium, and as optional component(s) tin and/or at least one of silver, beryllium, magnesium, zinc, boron, aluminium, yttrium, rare earth metal, silicon, niobium, antimony, bismuth, manganese, thorium and zirconium, which oxides are present as an intimate mixture. EP 1 145 762 Al describes a process for the preparation of a vanadia SCR-catalyst supported on titania. The process is characterized in that the catalyst is prepared by dispersing titania in an ammonium metavanadate solution, adjusting the pH of the solution to a value of 7.0-7.1, stirring the resulting suspension for a time for complete adsorption of the vanadium compound on titania, filtering the suspension and drying and calcining the resulting catalyst compound. In spite of the fact that SCR technology is used worldwide there are still opportunities to improve catalytic performance especially in relation to the following issues: (i) to improve catalyst design in order to obtain at the same time a higher activity in NOX removal and a lower activity in SO2 oxidation; (ii) to limit ammonia slip and to improve the behaviour of the system under dynamic conditions; (iii) to extend the present applicable temperature range of SCR catalysts towards higher temperature up to 600°C and to avoid deactivation which occurs at present catalysts when operated at high temperatures. It is in fact known that the activity of a "V2O5/TiO2/SiO2 catalyst increases markedly with a rise in calcinations temperature up to 600-650°C and then rapidly decreases. This is mainly due to phase transformation of TiO2 (anatase) into TiO2 (rutile) and consequent loss of BET surface area with changes in the chemical state of surface vanadium species. Solving these issues will pave the road for use of SCR also in mobile applications; the process using urea as reducing agent is in fact investigated intensively for use in diesel or gasoline lean-burn engines (5-6). The challenges for automotive applications are high SCR activity and improved thermal stability of vanadia-tungsta-titania catalysts in the temperature range 423-1000K. Such extreme operating temperatures (compared to "classic" SCR applications where temperature range of the order of 573-773K are often encountered) are certainly of short duration and may occur at very high power output (low rpm and high load). The present invention is aimed to solve the problem related to improvement of thermal stability at higher temperatures where state of the art V/Ti/W/Si and V/Ti/W catalysts still suffer strong deactivation. The catalyst composition according to the invention is represented by the general formula REVO/S wherein RE is at least one of the group of rare earth metals Y, Ce, Pr, Nd, Sm, Gd, Tb, Dy, Er and Yb in an amount of up to 6.0 wt-%; V is vanadium in an amount of 0.2-2.5 wt-%; O is oxygen in an amount of up to 3.5 wt.-%; and S is a support containing TiO2 in an amount of at least 70 wt.-%, with the rest being WO3 and optionally SiO2. The invention is based on the observation that promotion of V/Ti/W/Si and V/Ti/W catalysts with rare earth (RE) strongly improves activity even after aging at temperatures of 750°C for several hours, when the activity of state of the art catalysts drops to negligible values. This allows potential application of these catalysts in the removal of NOX from diesel or gasoline lean-burn automotive engines in addition to stationary applications at high temperatures. In a preferred embodiment RE is at least one of the group of Pr, Sm, Gd, Tb, Dy and Er, and particularly one of the group of Sm, Gd, Tb, Dy and Er, and more preferred at least one of Er and Tb. Also preferred is that the support S of the catalyst composition contains SiO2 in an amount of 4-12 wt-%, particularly in an amount of 5-10 wt-%. The invention is also directed to a first process (process I) for the preparation of a catalyst composition, characterized in that a solid support containing TiO2 in an amount of at least 70 wt-%, WO3 in an amount of 5-20 wt-%, and optionally SiO2 in an amount of up to 15 wt-%, is contacted with an aqueous solution containing an vanadium salt and a salt of at least one rare earth metal selected from the group of Y, Ce, Pr, Nd, Sm, Gd, Tb, Dy, Er and Yb to give a slurry which is broxtght to dryness and calcined. By bringing the solid support in contact with the solution of the rare earth salt, adsorption on the support takes place. A second process (process II) for the preparation of a catalyst composition is characterized in that a solid support containing TiO2 in an amount of at least 70 wt.-%, WO2 in an amount of 5-20 wt.-%, and optionally SiO2 in an amount of up to 15 wt-%, is contacted with a vanadium salt and a hydroxide of at least one rare earth metal selected from the group of Y, Ce, Pr, Nd, Sm, Gd, Tb, Dy, Er and Yb to give a slurry which is brought to dryness and calcined. By bringing the solid support in contact with the hydroxide of the rare earth, adsorption on the support takes place. A third process (process III) for the preparation of a catalyst composition is characterized in that a solid support containing TiO2 in an amount of at least 70 wt.-%, WO3 in an amount of 5-20 wt.-%, and optionally SiO2 in an amount of up to 15 wt-%, is contacted with a vanadate (REVO4) of at least one rare earth metal selected from the group of Y, Ce, Pr, Nd, Sm, Gd, Tb, Dy, Er and Yb to give a slurry which is brought to dryness and calcined. By bringing the solid support in contact with the rare earth vanadate, adsorption on the support takes place. In a more preferred embodiment the rare earth metal is at least one of the group of Pr, Sm, Gd, Tb, Dy and Er, and particularly one of the group of Sm, Gd, Tb, Dy and Er, and more preferred at least one of Er and Tb. The invention is also directed to a catalyst composition which is obtainable according to the inventive processes mentioned above. The invention is also directed to a catalyst composition which is obtainable according to the inventive processes mentioned above, containing said rare earth metal in an amount of up to 6.0 wt.-%; vanadium in an amount of up to 2.5 wt.-%; oxygen in an amount of up to 3.5 wt-%; TiO2 in an amount of at least 65 wt.-%, WO3 in an amount of up to 20 wt-%, and optionally SiO2 in an amount of up to 15 wt-%. In the following preferred embodiments of the invention are described in more detail. The catalysts according to the invention were obtained starting from two support materials of composition 81%TiO2-9%WO3-10%SiO2 (Ti/W/Si) and 90% TiO2-10%WO3 (Ti/W). To this support, a combination of V and RE elements were added to provide a NOX reduction catalysts represented by the formula REVO/Ti-W-Si with RE= Y, Ce, Pr, Nd, Sm, Gd, Tb, Dy, Er and Yb. The content of the active phase was in the range up to 5.1 wt.-% RE element, 0.4-2.1 wt.-% vanadium and up to 2.7 wt-% oxygen, corresponding to a REVO loading in the range of 2.5-8.5 wt-% 1. Preparation of a catalyst according to the invention containing 5.0 wt.-% Er and 1.5 wt.-% V on a Ti-W-Si support 1.1. Preparation of the Ti-W-Si support Preparation of the support was carried out according to (7): 92.68g of titanium tetrachloride (TiCl4) was added dropwise to 1 liter of water under ice cooling with stirring. Then 16.06g of Lithosol 1530 KD (a tradename for a product of Zschimmer & Schwarz Chemische Fabriken, containing 30% of SiO2 in the sol state) were added. While thoroughly stirring the mixture at about 30°C, ammonia water was gradually added. When the pH of the mixture reached 7, the addition was stopped. The mixture was aged by allowing it to stand for 2 hours. The resulting TiO2-SiO2 gel was filtered , washed with water, dried at 120°C for 10 hours and further washed with water, then calcined at 500°C for 3 hours. The resulting TiO2-SiO2 powder contained 86 mole% of titanium and 14 mole% of silicon as SiO2. The resulting powder was designated as (Ti/Si). A solution of 8.16 g of ammonium paratungstate [(NH4)10 W12 O41-5H2O] in 500 ml of distilled water was added to 73.4g of (Ti/Si). They were thorougly mixed with stirring, concentrated, dried and calcined at 500°C for 6 hours. The resulting support had a weight% ratio TiO2:WO3:SiO2of 81:9:10. 1.2. Preparation of the catalyst according to the invention An aliquot of 69.7 mg of ammonium metavanadate was dissolved in 10 ml of IN oxalic acid. The solution was heated in order to obtain the blue complex (NH4)2[VO(C2O4)2] and then 2478.2 mg of erbium acetate solution (4.6% of Er) were added under mixing. Moreover, some drops of HNO3 were added in order to avoid the precipitation of the erbium oxalate. Then, the support (1831.8 mg of mixed oxide containing 81%TiO2-9%WO3-10%SiO2) was added. This slurry was brought to dryness under continuous stirring at 80-100°C. Finally, the solid was dried at 120°C overnight and calcined at 650°C for 2 hours, pressed into pellet, crushed and sieved in the range 355-425 µm. This will be referred as fresh sample. Aging of samples was carried out in a tubular furnace at a temperature of 750°C for 10 hours under air. 1.3. Preparation of the catalyst according to process II of the invention 1.3.1. Preparation of the Erbiumhydroxide (Er(OH)3) Erbiumhydroxide was prepared by dissolving 3,82 g of Er2O3 in approx. 35 ml of HNO3/water (1:1) mixture under stirring. As soon as the solution of Er-Nitrate was formed, cone. Ammonia solution was added until precipitation of Er-Hydroxide was completed. The precipitate was separated by filtration, washed several times with distilled water and dried at moderate temperatures (approx. 60°C) to produce a wet cake of Er-Hydroxide having an Er content of 19,6 % . 1.3.2. Preparation of the catalyst 104. 5 mg of monoethanolamine and 3659 mg of distilled water were mixed. The solution was heated up to 90°C and 104,54 mg of NH4VO3 added under stirring. To the solution there were added 759,9 mg Er(OH)3 (Er content being 19,6 %) followed by adding of 2747,7 mg of the Ti/W/Si support (containing 81%TiO2-9%WO3-10%SiO2). This slurry was brought to dryness under continuous stirring at 80-100°C. Finally, the solid was dried at 120°C overnight and calcined at 650°C for 2 hours, pressed into pellet, crushed and sieved in the range 355-425 µm. This will be referred as fresh sample. Aging of samples was carried out in a tubular furnace at a temperature of 750°C for 10 hours under air. 1.4. Preparation of the catalyst according to process III of the invention 1.4.1. Preparation of the Erbiumvanadate (ErVO4) The crystalline ErVO4 is prepared by the liquid - phase reaction method. 1.032 g of NH4VO3 are dissolved in distilled water at 80°C in order to obtain a 0.1 mol/1 solution; at the same time an Erbium Nitrate Solution (0.2 mol/1) is prepared by diluting 6.695 g of Er(NO3)3 solution (containing 22.16% of Er) with distilled water at 80°C. After mixing the two solutions under continuous stirring the pH was adjusted to 7.0 with the help of ammonia (30% solution). This causes the precipitation of a white-pale pink compound (EbVO4) that was filtered, washed several times with distilled water and dried at 100°C overnight. 1.4.2. Preparation of the catalyst Two slurries were formed dissolving 252.3 mg of ErVO4 and 2747.7 mg of the Ti/W/Si support (WO3/TiO2-(10%)SiO2) in distilled water. The two slurries were mixed heating up to 90°C and stirring. The final slurry was brought to dryness under continuous stirring at 80-100°C. Finally, the solid was dried at 120°C overnight and calcined at 650°C for 2 hours, pressed into pellet, crushed and sieved in the range 355-425 urn. This will be referred as fresh sample. Aging of samples was carried out in a tubular furnace at a temperature of 750°C for 10 hours under air. 2. Preparation of a state of the art catalyst 1.7%V/Ti/W (8) 2.1. Preparation of the Ti-W support The preparation of the support was carried out according to (9) : 87g of titanium tetrachloride (TiCL») were poured into 300 ml of ice water and the solution was neutralized with 3N ammonia water. The resulting precipitate was separated by filtration, and thoroughly washed with distilled water. A solution of 4.58g of ammonium paratungstate [(NH4)10W12O41-5H2O] in 325 ml of distilled water was thoroughly mixed with the resulting cake. The resulting slurry was dried, and calcined at 500°C for 6 hours in a muffle furnace. The resulting support had a weight% ratio TiO2:WO3 of 90:10. 2.2. Preparation of the catalyst 1.7%V/Ti/W An aliquot of 11.2 mg of ammonium metavanadate was dissolved in 10 ml of IN oxalic acid. The solution was heated in order to obtain the blue complex (NH4)2[VO(C2O4)2]]. Then, the support (1940 mg of mixed oxide containing 90%TiO2-10%WO3) was added. This slurry was brought to dryness under continuous stirring at 80-100°C. Finally, the solid was dried at 120°C overnight and calcined at 650°C for 2 hours, pressed into pellet, crushed and sieved in the range 355-425 µm. The specific surface areas of oxide powders were measured by the BET method using N2 adsorption/desorption at 77K with a Sorptomatic 1990 instrument (Carlo Erba). 3. Catalyst Testing Catalyst testing was carried out in the apparatus described in Figure 1. The gas feed consisted of NH3/N2, NO/N2, O2, N2. Mass flow meters were used to measure and control the single gaseous stream while an injection pump was used to introduce water. The feed stream was preheated and premixed and ammonia was added to the gaseous mixture immediately before entering the reactor to avoid side reactions. A tubular quartz reactor was employed inserted in a furnace. Temperature was controlled by a thermocouple inserted in the catalyst bed. The gas exiting the reactor was scrubbed with an aqueous solution of phosphoric acid to trap unconverted ammonia and then cooled to condense water vapor. Activity of the catalysts were measured under stationary conditions in a temperature range of 250°C to 450°C. Unless otherwise reported the standard gas composition and reaction conditions given in Table 1 were used. Conditions were selected in order to have a conversion not exceeding ca. 90% with reference catalyst. Gas composition analysis was carried out with an FTIR spectrometer equipped with a gas cell. Table 2 shows NOx removal efficiency in the temperature range 250-450°C for catalysts prepared according to process I containing 0.4-2.1 wt.% V and 1.4-5.1 wt.% RE on Ti/W/Si support. For comparison the activity of the state of the art reference catalyst based on 1.7 wt.% V/Ti/W are also reported. The NOX reduction activity of all the catalysts examined in the present study increased with increasing reaction temperature up to about 320°C where a maximum NOX reduction activity was observed. At this point the activity began to decrease due to lower ammonia adsorption capacity. A strong effect is also shown with aging (calcination at 750°C for 10 h). Particularly for the state of the art catalyst calcined at a temperature of 750°C strong deactivation is observed with conversion dropping at values between 5-20%. A similar strong deactivation is observed also with La-containing catalyst. All the other catalysts can be broadly divided in two groups: group A catalysts (comprising Y,Ce,Pr and Nd) which suffer a slight deactivation after ageing and group B catalysts (comprising Sm, Gd, Tb, Dy, Er, ~Yb is in the middle of the two goups-) in which deactivation has no effect or even causes an improvement of overall efficiency. The best performances are observed with Er and Tb containing catalysts where a substantial increase of conversion is observed after ageing in all temperature range examined. The overall picture detailing activity drop/improvement after aging is shown in Figure 2, which also highlights a dependence of activity on position of the element in the periodic table. Table 2 shows also the NOX removal efficiency against RE and V loading. The loading amount was controlled by varying the amount of ammonium vanadate and rare earth acetate solutions in the impregnation. The preparation of a 0.4 wt.% V and 1.5 wt.% Er on Ti/W/Si is reported below. The support was prepared as already described. The supported catalysts were prepared according to the following procedure: 19 mg of ammonium metavanadate were dissolved in 10 ml of oxalic acid IN. The solution was heated in order to obtain the blue complex (NH4)2[V0(C204)2]and then 619.6 mg of erbium acetate solution (4.6% of Er) were added. Moreover, some drops of HNO3 were added in order to avoid the precipitation of the erbium oxalate. Then, the support (1831.8 mg of Ti/W/Si) was added. This slurry was brought to dryness under continuous stirring at 80-100°C. Finally, the solid was dried at 120°C overnight and calcined at 650°C for 2 hours, pressed into pellet, crushed and sieved in the range 355-425 µm]. Table 2a shows NOx removal efficiency in the temperature range 250-450°C for catalysts prepared according to process II containing 0,4-2.1 wt.% V and 1,4-5.1 wt.% RE on Ti/W/Si support. For comparison the activity of the state of the art reference catalyst based on 1,7 wt.% V/Ti/W are also reported. Table 2b shows NOx removal efficiency in the temperature range 250-450°C for catalysts prepared according to process III containing 0,4-2.1 wt.% V and 1,4-5.1 wt.% RE on Ti/W/Si support. For comparison the activity of the state of the art reference catalyst based on 1,7 wt.% V/Ti/W are also reported. As listed in table 2 (examples 8-10, 12-13) loading does not affect strongly activity after aging. For all the sample investigated an unusual promotion of activity is observed after aging at 750°C. Catalysts in the fresh state are less active at the lowest loading, (especially at the lowest temperatures) consistently with the presence of a lower amount of active phase containing vanadium. Maximum of activity is observed always at 320°C. Surface area analysis is reported in Table 4 and 5. With all the catalysts examined aging procedure causes a drop in surface area which is proportional to the amount of RE and V deposited. This would suggest that aging induce an interaction between the active phase containing rare earths and the support. X-ray diffraction analysis of the supports showed that TiO2 (anatase) is the only phase detected after aging at 750°C under air for l0h, indicating that transformation to rutile does not occur. The presence of silica has no effect on X-ray diffraction profile under these conditions. Aging under more severe conditions (850°C, l0h) induces a modification of diffraction profile of both supports. Segregation of crystalline WO3 is observed in both samples while for supports not containing silica, TiO2 in the form of rutile is clearly evidenced. The introduction of SiO2 strongly stabilizes anatase against its transformation to rutile. The introduction of vanadium modifies this picture by accelerating segregation of WO3-containing phases and transformation of anatase to rutile. Figure 3 and 4 show respectively X-ray diffraction profiles of fresh and aged V2O5/WT and V2O5/WTS. Peaks characteristic of V2O5 are not seen in both supports indicating that V2O5 is either amorphous when supported on TiCh or that the particle size is below the detection limits of X-ray technique. This is in agreement with the fact that crystalline V2O5 on TiO2 is observed only at higher loading (10). In the presence of V2Os the anatase to rutile phase transformation is initiated at lower temperature, as a consequence for WT support after calcinations at 750 for lOh approx 50% of TiO2 is in the form of rutile. The presence of V2O5 also accelerates segregation of crystalline WO3 phase, in accordance with previous observations (10-11). A more accurate analysis of X-ray diffraction profiles indicate that modification of WO3 by introduction of foreign cations into the oxide lattice could be responsible of small differences in the peak positions. Formation of mixed TixWyO3 or MxWyO3 (with M being an impurity present in the support) could be a possibility although no evidence can be found from existing XRD patterns. The presence of residual Ca from commercial additives was responsible of formation of CaWO4 in structured catalysts of similar composition treated at comparable temperatures (11). Reaction of supported vanadia with TiO2 to yield VxTii-xO2 in which vanadium is incorporated into the titania support in the form of rutile has been previously observed. In our case, lattice parameters of TiO2 (rutile) stabilized in the presence and in the absence of vanadia are coincident, indicating that formation of TiVO solid solution does not occur. SiO2-containing support shows a similar behavior although the transformation (anatase) to rutile is slower, in agreement with what observed in the absence Table 6 summarizes XRD data on RE containing catalysts prepared according to process I treated at two different aging temperatures. The diffraction profiles after aging at 650°C reveals the presence of weak signals due to formation of rare earth vanadates. These can be seen from the majority of RE elements investigated. Calcinations at 750°C clearly evidence formation of crystalline REVO4 for all elements with the exception of La. Interestingly, the presence of lanthanides seems to positively influence the degree of rutilization of the support and the process of segregation/formation of WO3. For silica containing support rutile is seen only at calcinations temperatures above 750°C and the appearance of crystalline WOs is also retarded (this is true except for Tb, Ce and Pr-containing catalysts where the formation of WO3 is not affected if compared with "V2O5-only samples). In the absence of silica, segregation of WO3 and transformation to rutile occur already at temperature of 750°C, although the presence of RE slow down their formation. Figure 5 shows the effect of aging treatment at temperatures in the range 650-850°C for Tb-V-OAVTS. (Table Removed) Table 2: Activity of fresh and aged catalysts containing RE and V on TiO2:WO3:SiO2 (81:9:10) matrix (Table Removed) Table 2a: Activity of fresh and aged catalysts prepared according to process II containing RE and V on TiO2:WO3:SiO2 (81:9:10) matrix (Table Removed) Table 2b: Activity of fresh and aged catalysts prepared according to process III containing RE and V on TiO2:WO3:SiO2 (81:9:10) matrix (Table Removed) Table 3: Activity of fresh and aged catalysts prepared according to process I containing RE and V on TiO2:WO3 (90:10) matrix (Table Removed) Table 4: Surface area of fresh and aged catalysts prepared according to process I containing RE and V on TiO2:WO3:SiO2 (81:9:10) matrix (Table Removed) Table 5: Surface area of fresh and aged V containing catalysts on TiO2:WO3:SiO2 (81:9:10) and TIO2/WO3 (90:10) matrix (Table Removed) Table 6: Identification of phases with XRD on samples prepared according to process I (4.6-5% RE loading) calcined at different temperatures (Table Removed) References: 1. V. I. Parvulescu, P. Grange, B. Delmon, Cat. Today 46 (1998) 233. 2. P. Forzatti, Appl. Catal. A: General 222 (2001) 221 3. S.E. Park, G.M. Kim, Y.J. Lee, J.S. Chang, S.H. Han, US Patent 5879645 (1999). 4. P.S.Ji, H.M.Eum, J.B.Lee, D.H.Kim, I.Y.Lee, I.S.Nam, S.W.Ham,S.T.Choo, US Patent 6380128(2002) 5. G. Madia, M. Elsener, M. Koebel, F. Raimondi, A. Woukan, Applied catalysis B: Environmental 39 (2002) 181. 6. M. Koebel, M. Elsener, M. Kleeman, Catal. Today 59 (2000) 335. 7. A. Inoue, T. Suzuki, K. Saito, Y.Aoki, T. Ono, T. Ohara, US patent 4221760 (1980). 8. A. Schafer-Sindlinger, A. Burkardt, H. Van der Tillaart, T. Kreuzer, E. Lox, W. Weisweller, Eu Patent Application EP 1 145762 Al 9. GB. Patent. 1495396 (1974); Mitsubishi Petrochemical Co. Ltd. 10. R. Y. Saleh, I. E. Wachs, S. S. Chan, C. C. Chersich, J. Catalysis 98 1(986) 102. 11.1. Nova, L. dall'Acqua, L. Lietti, E. Giamello, P. Forzatti, Applied Catalysis B: Environmental 35 (2001) 31. We Claim: 1. A process for the preparation of a catalyst composition, characterized in that a solid support containing TiO2 in an amount of at least 70 wt%, WO3 in an amount of 5-20 wt%, and optionally SiO2 in an amount of up to 15 wt% is contacted with a vanadate (REVO4) of at least one rare earth metal selected from the group of Y, Ce, Pr, Nd, Sm, Gd, Tb, Dy, Er and Yb to give a slurry which is brought to dryness and calcined. 2. Catalyst composition obtainable as claimed in claim 1.

Documents:

3316-DELNP-2006-Abstract-(08-11-2011).pdf

3316-delnp-2006-abstract.pdf

3316-DELNP-2006-Claims-(08-11-2011).pdf

3316-delnp-2006-claims.pdf

3316-DELNP-2006-Correspondence Others-(02-12-2011).pdf

3316-DELNP-2006-Correspondence Others-(08-11-2011).pdf

3316-delnp-2006-Correspondence Others-(13-06-2012).pdf

3316-delnp-2006-correspondence-others 1.pdf

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3316-delnp-2006-description (complete).pdf

3316-DELNP-2006-Drawings-(08-11-2011).pdf

3316-delnp-2006-drawings.pdf

3316-DELNP-2006-Form-1-(08-11-2011).pdf

3316-delnp-2006-form-1.pdf

3316-delnp-2006-form-18.pdf

3316-DELNP-2006-Form-2-(08-11-2011).pdf

3316-delnp-2006-form-2.pdf

3316-delnp-2006-form-26.pdf

3316-DELNP-2006-Form-3-(08-11-2011).pdf

3316-delnp-2006-form-3.pdf

3316-delnp-2006-form-5.pdf

3316-delnp-2006-GPA-(13-06-2012).pdf

3316-delnp-2006-pct-101.pdf

3316-delnp-2006-pct-105.pdf

3316-delnp-2006-pct-210.pdf

3316-delnp-2006-pct-220.pdf

3316-delnp-2006-pct-237.pdf

3316-delnp-2006-pct-308.pdf

3316-delnp-2006-pct-311.pdf

3316-delnp-2006-pct-401.pdf

3316-delnp-2006-pct-408.pdf

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3316-DELNP-2006-Petition-137-(08-11-2011).pdf

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