Method of denitrating exhaust gases

Abstract: A method of denitrating an exhaust gas by means of removing nitrogen oxides catalytically using ammonia as a reducing agent while introducing an exhaust gas containing the nitrogen oxides into a reaction vessel packed with a catalyst, comprising: providing a denitration catalyst layer in the upstream of the gas flow, an ammonia decomposition catalyst layer capable of decomposing oxidatively ammonia into nitrogen and nitrogen oxides in the downstream and a second denitration catalyst layer or a denitration catalyst layer capable of decomposing ammonia in the further downstream; and, adding ammonia in an amount not less than the reaction equivalence for the nitrogen oxides in the exhaust gas to the inlet of the first denitration catalyst layer.

Description: Specification Field and background of the invention The present invention relates to a method of denitrating an exhaust gas by which nitrogen oxides (NOx) in the exhaust gas can be eliminated at a high efficiency. Description of related art As a method of eliminating NOx contained in a burning exhaust gas, a selective catalytic hydrogenation using NH 3 as a reducing agent is of wide use majorly in thermal-power stations. As a catalyst, a titanium oxide-based catalyst having vanadium, tungsten or molybdenum as an active component is mainly employed. Control of NOx emission becomes strict more and more in these days, and a higher efficiency of denitration is required in suburban thermal-power stations along with the enlargement of generating facilities in response to the increase in demand of electricity power. A conventional denitration method employs NH 3 as a reducing agent, and decomposes NOx into N 2 on the catalyst according to the formula shown below. 4NO + 4NH 3 + O 2 → 4N 2 + 6H 2 O Based on this formula, it is possible theoretically that 100% elimination of NOx is conducted by adding NH 3 in the molar amount equal to that of NOx. However, it is not practical to effect completely uniform mixing of NH 3 and NO x in the exhaust gas, and NH 3 should be added in excess of NOx for the purpose of highly efficient denitration. Accordingly, disadvantage has been experienced that unreacted NH 3 is emitted in a significant amount. EP-A-0 268 118, EP-A-0 261 610 and EP-A-0 567 964 disclose processes for removing nitrogen oxide from an exhaust gas which comprises mixing the exhaust gas with excess ammonia, and then flowing the resulting mixture through a first denitration catalyst layer and subsequently through an ammonia decomposition catalyst layer. Summary of the invention According to the present invention, highly efficient denitration can be conducted while reducing the emission of unreacted NH 3 into atmosphere to a level as low as possible. Thus, the present invention provides a method for removing nitrogen oxides from an exhaust gas comprising: (a) flowing the exhaust gas containing the nitrogen oxides through a reaction vessel packed with a first denitration catalyst layer, an ammonia decomposition catalyst layer downstream of the first denitration catalyst layer and which contains a catalyst capable of oxidatively decomposing ammonia into nitrogen and nitrogen oxides, and a second denitration catalyst layer downstream of the ammonia decomposition catalyst layer; and (b) adding ammonia as a reducing agent to the exhaust gas prior to the first denitration catalyst layer in an amount not less than the reaction equivalence for the nitrogen oxides contained in the exhaust gas; wherein the ammonia decomposition catalyst has: (i) a crystalline silicate carrier which in its dehydrated form has the formula: (1.0±0.8)R 2 O· [aM 2 O 3 ·bAl 2 O 3 ]·cMeO·ySiO 2 wherein R is an alkaline metal ion and/or hydrogen ion; M is at least one of a group VIII element, a rare earth element, titanium, vanadium, chromium, niobium, antimony and gallium; Me is an alkaline earth metal, a≥0, b≥0, c≥0, a+b=1, y>12, and y/c>12; the silicate having an X-ray diffraction pattern as shown in Table 1 in the specification, and (ii) at least one active metal selected from platinum, palladium, ruthenium, iridium, and rhodium. Preferably, the ammonia is added in step (b) to the exhaust gas at the inlet of the first denitration catalyst layer. Preferably, the first and second denitration catalyst layers contain TiO 2 -based catalysts containing V, W or Mo as an active component. Preferably, the second denitration catalyst layer is capable of decomposing ammonia and contains a TiO 2 -based catalyst supporting either 4.5% by wt. or more of V 2 O 5 or 0.0001% by wt. or more of Pt, Pd, Ru, Rh or Ir. Preferably the ammonia decomposition catalyst may be a catalyst having a performance of 70% or higher as % nitrogen selection defined as follows: % nitrogen selection =[1-{(NOx (ppm) at outlet of ammonia decomposition catalyst - NOx (ppm) at inlet of ammonia decomposition catalyst)/(NH 3 (ppm) at inlet of ammonia decomposition catalyst - NH 3 (ppm) at outlet of ammonia decomposition catalyst)}]. Lattice spacing (interstitial distance) (d value) Relative strength 11.2 ± 0.3 VS 10.0 ± 0.3 VS 6.7 ± 0.2 W 6.4 ± 0.2 M 6.0 ± 0.2 M 5.7 ± 0.2 W 5.6 ± 0.2 M 4.6 ± 0.1 W 4.25 ± 0.1 M 3.85 ± 0.1 VS 3.75 ± 0.1 S 3.65 ± 0.1 S 3.3 ± 0.1 M 3.05 ± 0.1 W 3.0 ± 0.1 M VS: Very strong S: Strong M: Medium W: Weak (X-ray source: Cu) Brief description of the drawings The invention will now be described with reference to the drawings in which: Figure 1 shows a schematic view illustrating a first method (system) of denitrating an exhaust gas according to the present invention; and, Figure 2 shows a schematic view illustrating a second method (system) of denitrating an exhaust gas according to the present invention. Description of the preferred embodiments An embodiment of the first denitration method according to the present invention is described with referring to Figure 1. First denitration catalyst layer 1001 is provided in the furthermost upstream of the gas flow, and NH 3 decomposition catalyst layer 1002 is provided in the downstream, and then second denitration catalyst layer 1003 is provided in the further downstream, and NH 3 in an amount not less than the reaction equivalence for the NOx in the exhaust gas is added to the inlet of the first denitration catalyst layer 1001, whereby accomplish 90% or more of the denitration reaction in the first denitration catalyst layer 1001. Unreacted NH 3 coming from first denitration catalyst layer 1001 is decomposed by NH 3 decomposition catalyst layer 1002 to adjust the concentrations of NOx and NH 3 at the inlet of second denitration catalyst layer 1003 located in the downstream, whereby reducing the concentrations of NOx and NH 3 at the outlet of second denitration catalyst layer 1003 to the levels not exceeding 0.1 ppm and 3 ppm, respectively. First and second denitration catalyst layers 1001 and 1003 provided in the upstream and downstream, respectively, may employ conventional TiO 2 -based catalysts containing V, W or Mo as an active component. In the embodiment of the present invention described above, it is preferable that the catalyst employed in NH 3 decomposition catalyst layer 1002 has a % nitrogen selection as defined below not less than 70%. % nitrogen selection =[1-{(NOx (ppm) at outlet of ammonia decomposition catalyst - NOx (ppm) at inlet of ammonia decomposition catalyst)/(NH 3 (ppm) at inlet of ammonia decomposition catalyst - NH 3 (ppm) at outlet of ammonia decomposition catalyst)}]. Thus, since a small % nitrogen selection of the ammonia decomposition catalyst as defined above leads to a small range of the operation of the facility for achieving 0 < NH 3 (ppm) - NOx (ppm) < 3 (ppm) at the outlet of ammonia decomposition catalyst layer, it is required to control the facility with a wide range of gas treatment and temperature. Accordingly, % nitrogen selection is preferably 70% or higher. As a NH 3 decomposition catalyst having the % nitrogen selection specified above, a catalyst having a crystalline silicate which is represented by the formula as dehydrated: (1.0±0.8)R 2 O•[aM 2 O 3 •bAl 2 O 3 ]•cMeO•ySiO 2 wherein R denotes an alkaline metal ion and/or hydrogen ion, M denotes at least one element selected from the group consisting of VIII group elements, rare earth elements, titanium, vanadium, chromium, niobium, antimony and gallium, Me denotes an alkaline earth metal, a+b=1 , a≥0, b≥0, c≥0, y/c>12 and y>12, and which has a X-ray diffraction pattern shown in Table 1 shown above as a carrier and at least one metal selected from the group consisting of platinum, palladium, ruthenium, iridium, and rhodium as an active metal is preferable. The exhaust gas which has been denitrated by supplying an excessive amount of NH 3 in first denitration catalyst layer 1001 now has the composition of NOx:0 to 10 ppm and NH 3 :10 to 30 ppm, and then is introduced into the above-mentioned NH 3 decomposition catalyst layer whereby reducing the amount of NH 3 to achieve the condition "0 < NH 3 (ppm) - NOx (ppm) < 3 (ppm)" at the outlet of NH 3 decomposition catalyst layer 1002, and the exhaust gas having this composition is then denitrated in second denitration catalyst layer 1003 to achieve the concentrations of NOx and NH 3 not exceeding 0.1 ppm and 3 ppm, respectively. Contrary to this, a conventional method wherein NOx in an exhaust gas is denitrated by using only a denitration catalyst layer while adding an excessive amount of NH 3 to achieve a concentration of NOx in the exhaust gas not exceeding 0.1 ppm can not avoid a content of NH 3 in the exhaust gas which is at least 10 ppm. Example 1 described below was conducted in relation with the first denitration method referring to Figure 1. Example 1: (Preparation of denitration catalyst) A powder catalyst consisting of 4% by weight of vanadium pentaoxide (V 2 O 5 ) and 8% by weight of tungsten trioxide (WO 3 ) on titanic (T i O 2 ) was molded into a lattice honeycomb having the pitch of 3.3 mm and the wall thickness of 0.5 mm, which was used as a denitration catalyst. (Preparation of NH 3 decomposition catalyst) 5616 g of water glass #1 (SiO 2 : 30%) was dissolved in 5429 g of water to yield solution A. Separately, 718.9 g of aluminum sulfate, 110 g of ferric chloride, 47.2 g of calcium acetate, 262 g of sodium chloride and 2020 g of concentrated hydrochloric acid were dissolved together in 4175 g of water to yield solution B. Solution A and solution B were fed in a constant ratio to form a precipitate, and the mixture was stirred thoroughly to yield a slurry at pH 8.0. The slurry thus obtained was charged in a 20 L autoclave, to which 500 g of tetrapropyl ammonium bromide was added and the mixture was subjected to hydrothermal synthesis at 160°C for 72 hours. After synthesis, washing with water, drying and sintering for 3 hours at 500°C, crystalline silicate 1 was obtained. Crystalline silicate 1 thus obtained is represented in a molar ratio (excluding crystal water) by the formula shown below and has the crystal structure by X-day diffraction pattern in Table 1 shown above. 0.5Na 2 O•0.5H 2 O•[0.8Al 2 O 3 •0.2Fe 2 O 3 •0.25CaO]•25SiO 2 Crystalline silicate 1 obtained above was subjected to NH 4 ion exchange by stirring with 4N aqueous solution of NH 4 Cl at 40°C for 3 hours. After the ion exchange, the silicate was washed and dried at 100°C for 24 hours and sintered at 400°C for 3 hours to obtain crystalline silicate 1 of type H. Crystalline silicate of type H is of the type which has protons on its surface. Crystalline silicate 1 of type H thus obtained was impregnated with each of the aqueous solutions of chloroplatinic acid, palladium nitrate, ruthenium chloride and iridium chloride, evaporated to dryness and sintered at 500°C for 3 hours to obtain a powder catalyst. To 100 g of the powder obtained, 3 g of alumina sol and 55 g of silica sol (SiO 2 : 20% by weight) as binders and 200 g of water were added to obtain a slurry, which was wash-coated to a monolith support for coagulate (30-cells/square inch in a form of lattice) at the coating rate of 200 g/m 2 . The catalysts thus obtained were designated as NH 3 decomposition catalysts 1 to 5. The characteristics of the catalysts are shown in Table 2 below. NH 3 decomposition catalyst No. Active metal (amount supported: wt%) 1 Pt (0.02) 2 Pd (1) 3 Ru (0.3) 4 Ir (0.5) Crystalline silicates 2 to 8 of type H were prepared similarly in the method of preparation of NH 3 decomposition catalysts described above except for using 112 g of cobalt chloride, 105 g of titanium chloride, 10 g of vanadium chloride, 107 g of chromium chloride, 135 g of niobium chloride, 155 g of antimony chloride and 119 g of gallium chloride instead of ferric chloride. Using these crystalline silicates of type H and the aqueous solution of chloroplatinic acid, platinum was supported on each crystalline silicate of type H and wash-coated to a monolith support for coagulate similarly as described above at the coating rate of 200 g/m 2 of support surface. The catalysts thus obtained were designated as NH 3 decomposition catalysts 6 to 11. The characteristics of the catalysts are shown in Table 3 below. NH 3 decomposition catalyst No. Active metal (amount supported: wt%) 5 Pt (0.02) 6 Pt (0.02) 7 Pt (0.02) 8 Pt (0.02) 9 Pt (0.02) 10 Pt (0.02) 11 Pt (0.02) (Denitration reaction test: Test No.1) Three denitration catalysts having the size of 40 mm x 50 mm x 400 mmL, 1 NH 3 decomposition catalyst having the size of 42 mm x 50 mm x 500 mmL and 2 denitration catalysts, all described above, were attached serially and tested in the condition described below. Concentration of NOx in exhaust gas 50 ppm Concentration of NH 3 supplied 60 ppm, 70 ppm Concentration of O 2 in exhaust gas 14.7% Gas flow rate 22 Nm 3 /hour Gas temperature 360°C The results are shown in Table 5. At the outlet of the upstream first denitration catalyst layer which corresponds to a conventional denitration method, NOx was reduced to 0.02 to 0.03 ppm which indicated a high denitration efficiency, but NH 3 was emitted at a level as high as 10 to 20 ppm. In contrast, the method according to the present invention provided the levels of NOx and NH 3 at the outlet of the downstream second denitration catalyst layer as low as 0.02 to 0.1 ppm and less than 3 ppm, respectively, ensuring the low level of emission of both of NOx and NH 3 . NH 3 decomposition catalyst No. Inlet NH 3 (ppm) First denitration catalyst layer outlet Second denitration catalyst layer outlet NOx (ppm) NH 3 (ppm) NOx (ppm) NH 3 (ppm) 1 60 0.02 10.1 0.02 0.4 70 0.02 19.8 0.02 1.0 2 60 0.02 10.2 0.03 1.5 70 0.02 20.0 0.05 2.3 3 60 0.02 10.1 0.1 1.0 70 0.02 19.7 0.07 2.2 4 60 0.02 9.9 0.03 1.0 70 0.02 20.1 0.02 1.8 5 60 0.02 10.0 0.05 2.0 70 0.02 20.1 0.07 2.6 6 60 0.02 10.1 0.02 1.5 70 0.02 19.9 0.03 2.4 7 60 0.02 9.9 0.02 2.2 70 0.02 20.2 0.02 2.9 8 60 0.02 10.2 0.03 1.3 70 0.02 19.8 0.03 2.0 9 60 0.02 10.0 0.05 1.2 70 0.02 20.0 0.04 2.1 10 60 0.02 10.2 0.03 1.6 70 0.02 20.1 0.04 2.3 11 60 0.02 10.2 0.1 2.0 70 0.02 19.9 0.06 2.8 An embodiment of the second denitration method according to the present invention is described with referring to Figure 2. As shown in Figure 2, first denitration catalyst layer 2001 is provided in the furthermost upstream of the gas flow, and NH 3 decomposition catalyst layer 2002 is provided in the downstream, and then denitration catalyst layer 2003 having NH 3 decomposition ability is provided in the further downstream. NH 3 in an amount not less than the reaction equivalence for the NOx is added to the upstream to accomplish 90% or more of the denitration reaction in the upstream denitration catalyst layer. Then NH 3 is decomposed by NH 3 decomposition catalyst layer 2002 to adjust the concentrations of NOx and NH 3 at the inlet of the downstream denitration catalyst layer 2003 having NH 3 decomposition ability, whereby reducing the concentrations of NOx and NH 3 at the final outlet to the levels not exceeding 0.1 ppm and 3 ppm, respectively. The upstream denitration catalyst employed TiO 2 catalysts having V, W or Mo as an active component and supported 4.5% by weight of V 2 O 5 , while the downstream denitration catalyst having NH 3 decomposition ability supported V 2 O 5 in an amount greater than that supported by the upstream catalyst, i.e., in an amount of 4.5% by weight or greater, or, contained 0.0001% by weight or more of a noble metal (Pt, Pd, Ru, Rh or Ir). As a NH 3 decomposition catalyst, a catalyst having a crystalline silicate which is represented by the formula as dehydrated: (1±0.8)R 2 O•[aM 2 O 3 •bAl 2 O 3 ]•cMeo•ySiO 2 wherein R denotes an alkaline metal ion and/or hydrogen ion, M denotes at least one element selected from the group consisting of VIII group elements, rare earth elements, titanium, vanadium, chromium, niobium, antimony and gallium, Me denotes an alkaline earth metal, a+b=1 , a≥0, b≥0, c≥0, y/c>12 and y>12, and which has a X-ray diffraction pattern shown in Table 1 shown above as a carrier and at least one metal selected from the group consisting of platinum, palladium, ruthenium and iridium as an active metal may be employed. It is preferable to control the operation to achieve the concentrations of NOx and NH 3 of 0 to 10 ppm and 10 to 30 ppm, respectively, at the outlet of the upstream denitration catalyst layer, and to reduce NH 3 in the subsequent NH 3 decomposition catalyst layer to achieve the difference between the concentrations of NH 3 and NOx at its outlet: 0 < NH 3 (ppm) - NOx (ppm) < 3 ppm. By such denitration method, the concentrations of NOx and NH 3 not exceeding 0.1 ppm and 3 ppm, respectively, at the outlet can be achieved. In the conventional denitration methods employing only denitration catalyst layers, 10 ppm or higher of NH 3 emission could not be avoided in order to achieve 0.1 ppm or lower of NOx at the outlet. Example 2 described below was conducted in relation with the second denitration method referring to Figure 2. Example 2: (Preparation of denitration catalyst 101) A powder catalyst consisting of 4% by weight of vanadium pentaoxide (V 2 O 5 ) and 8% by weight of tungsten trioxide (WO 3 ) on titanic (TiO 2 ) was molded into a lattice honeycomb having the pitch of 3.3 mm and the wall thickness of 0.5 mm, which was designated as denitration catalyst 101. (Preparation of NH 3 decomposition catalysts 101 to 119) The 5616 g of water glass #1 (SiO 2 : 30%) was dissolved in 5429 g of water to yield solution A. Separately, 718.9 g of aluminum sulfate, 110 g of ferric chloride, 47.2 g of calcium acetate, 262 g of sodium chloride and 2020 g of concentrated hydrochloric acid were dissolved together in 4175 g of water to yield solution B. Solution A and solution B were fed in a constant ratio to form a precipitate, and the mixture was stirred thoroughly to yield a slurry at pH 8.0. The slurry thus obtained was charged in a 20 L autoclave, to which 500 g of tetrapropyl ammonium bromide was added and the mixture was subjected to hydrothermal synthesis at 160°C for 72 hours. After synthesis, washing with water, drying and sintering for 3 hours at 500°C, crystalline silicate 101 was obtained. Crystalline silicate 101 thus obtained is represented in a molar ratio (excluding crystal water) by the formula shown below and has the crystal structure by X-lay diffraction pattern in Table 1 shown above. 0.5Na 2 O•0.5H 2 O•[0.8Al 2 O 3 •0.2Fe 2 O 3 •0.25CaO]•25SiO 2 Crystalline silicate 101 obtained above was subjected to NH 4 ion exchange by stirring with 4N aqueous solution of NH 4 Cl at 40°C for 3 hours. After the ion exchange, the silicate was washed and dried at 100°C for 24 hours and sintered at 400°C for 3 hours to obtain crystalline silicate 101 of type H (a catalyst which has protons on its surface). Crystalline silicate 101 of type H thus obtained was impregnated with each of the aqueous solutions of chloroplatinic acid, palladium nitrate, ruthenium chloride, chloroiridic acid and rhodium chloride, evaporated to dryness and sintered at 500°C for 3 hours to obtain a powder catalyst. To 100 g of the powder obtained, 3 g of alumina sol and 55 g of silica sol (SiO 2 : 20% by weight) as binders and 200 g of water were added to obtain a slurry, which was wash-coated to a monolith support for coagulate (30-cells/square inch in a form of lattice) at the coating rate of 200 g/m 2 . The catalysts thus obtained were designated as NH 3 decomposition catalysts 101 to 105. Except for adding cobalt chloride, ruthenium chloride, rhodium chloride, lanthanum chloride, cerium chloride, titanium chloride, vanadium chloride, chromium chloride, antimony chloride, gallium chloride and niobium chloride in the molar amount as an oxide equal to that of Fe 2 O 3 instead of ferric chloride used in the synthesis of crystalline silicate 101 in the preparation of NH 3 decomposition catalysts 101 to 105 described above, the procedure similar to that employed for crystalline silicate 101 was conducted to obtain crystalline silicates 102 to 112. The crystal structures of these crystalline silicates as X-ray diffraction patterns were shown above in Table 1, with the compositions being represented by the following formula in molar ratios of the oxides (dehydrated form): 0.5Na 2 O•0.5H 2 O•(0.2M 2 O 3 •0.8Al 2 O 3 •0.25CaO)•25SiO 2 , wherein M denotes Co, Ru, Rh, La, Ce, Ti, V, Cr, Sb, Ga or Nb. Then, except for adding magnesium acetate, strontium acetate and barium acetate each in the molar amount as an oxide equal to that of CaO instead of calcium acetate used in the synthesis of crystalline silicate 101, the procedure similar to that employed for crystalline silicate 101 was conducted to obtain crystalline silicates 113 to 115. The crystal structures of these crystalline silicates as X-ray diffraction patterns were shown above in Table 1, with the compositions being represented by the following formula in molar ratios of the oxides (dehydrated form): 0.5Na 2 O•0.5H 2 O•(0.2Fe 2 O 3 •0.8Al 2 O 3 •0.25MeO)•25SiO 2 , wherein Me denotes Mg, Sr or Ba. Using crystalline silicates 102 to 115 obtained above and the procedure similar to that for crystalline silicate 101 (the procedure described above), crystalline silicates 102 to 115 of type H were obtained. These crystalline silicates of type H were impregnated with the aqueous solution of chloroplatinic acid, evaporated to dryness and sintered at 500°C for 3 hours to obtain powder catalysts containing 0.02% by weight of Pt. These powder catalysts were coated to a monolith support for coagulate similarly as for decomposition catalysts 101 to 105, whereby obtaining NH 3 decomposition catalysts 106 to 119. The characteristics of NH 3 decomposition catalysts 101 to 119 are shown in Table 6 below. (Preparation of denitration catalysts 201 to 203 having NH 3 decomposition ability) A powder catalyst consisting of 6% by weight of vanadium pentaoxide (V 2 O 5 ) and 9% by weight of tungsten trioxide (WO 3 ) on titanic (TiO 2 ) was molded into a lattice honeycomb having the pitch of 3.3 mm and the wall thickness of 0.5 mm, which was designated as denitration catalyst 201 having NH 3 decomposition ability. A powder catalyst supporting 9% by weight of molybdenum trioxide (MoO 3 ) instead of tungsten trioxide (WO 3 ) employed in the preparation of denitration catalyst 201 having NH 3 decomposition ability described above was prepared by the method similar to that described above to obtain denitration catalyst 202 having NH 3 decomposition ability. Furthermore, a powder catalyst supporting 3% by weight of vanadium pentaoxide and 0.001% by weight of platinum instead of 6% by weight of vanadium pentaoxide (V 2 O 5 ) employed in the preparation of denitration catalyst 201 having NH 3 decomposition ability described above was prepared by the method similar to that described above to obtain denitration catalyst 203 having NH 3 decomposition ability. (Denitration reaction test: Test No.2-1) Three denitration catalysts 101 having the size of 40 mm x 50 mm x 400 mmL, 1 NH 3 decomposition catalyst 101 having the size of 42 mm x 50 mm x 150 mmL and 2 denitration catalysts 201 having NH 3 decomposition ability which had the size of 40 mm x 50 mm x 400 mmL were all attached serially and subjected as system 301 to the denitration reaction test in the condition indicated in Table 7 shown below. Exhaust gas composition Gas amount Temperature Inlet NO: 50 ppm 22 Nm 3 /h 360°C Inlet NH 3 : 60 ppm, 80 ppm Inlet O 2 : 14.7% Inlet H 2 O: 6% (Denitration reaction test: Test No.2-2) Systems 302 to 319 were obtained by providing NH 3 decomposition catalysts 102 to 119 instead of NH 3 decomposition catalyst 1 employed in Test No. 2-1, and subjected to the denitration reaction test in the condition similar to that in Test No. 2-1. (Denitration reaction test: Test No.2-3) Systems 320 and 321 were obtained by providing denitration catalysts 202 and 203 having NH 3 decomposition ability instead of denitration catalyst 201 having NH 3 decomposition ability employed in Test No.2-1, and subjected to the denitration reaction test in the condition similar to that in Test No. 2-1. The results of the tests of systems 301 to 321 are shown in Table 8. (Comparative denitration reaction test No. 1) In a comparative test, system 322 was obtained by providing only denitration catalyst 101 employed in Test No.2-1 and subjected to the denitration performance test similarly as in Test No.2-1. In addition, system 323 was obtained by providing only denitration catalyst 101 and NH 3 decomposition catalyst 101 employed in Test No.2-1 and subjected to the denitration performance test similarly as in Test No.2-1. Furthermore, system 324 was obtained by providing two denitration catalysts 101 identical to the first layer in Test No.2-1 instead of denitration catalyst 201 having NH 3 decomposition ability provided as the third layer in Test No.2-1, and subjected to the denitration performance test similarly as in Test No.2-1. The results of the tests of systems 322 to 324 are shown also in Table 8. As evident from the results shown in Table 8, systems 301 to 321 according to the method of the present invention achieved a concentration of NOx at the outlet of the third catalyst layer of 0.02 to 0.04 ppm, indicating a very high denitration efficiency, while reducing the leak of NH 3 to a level as low as 0.7 to 2.3 ppm. On the other hand, system 322 corresponding to a conventional denitration method involved the problem of the NH 3 emission as high as 10 to 30 ppm although it achieved a NOx level of 0.02 to 0.03 ppm, as shown in Comparative test No.1. System 323 wherein only NH 3 decomposition catalyst was provided as the second layer provided the concentrations of NOx and NH 3 ranging from 0.7 to 1.6 ppm and 2.4 to 7.8 ppm, respectively, which did not indicate a high denitration efficiency and were not NOx emission level corresponding to an atmospheric level. Furthermore, system 324 wherein the denitration catalyst having no NH 3 decomposition ability identical to the first layer was provided as the third layer provided the NOx level at the outlet ranging from 0.02 to 0.03 ppm, but it provided a NH 3 level at the outlet ranging from 1.5 to 6.2 ppm, indicating that it involved the disadvantage of the leak of NH 3 exceeding 5 ppm in case of the NH 3 level at the inlet as high as 80 ppm. Test No. System No. (First step) Denitration catalyst No. (Second step) NH 3 decomposition catalyst No. (Third step) Denitration catalyst having NH 3 decomposition ability No. Inlet NH 3 (ppm) Third step catalyst layer outlet NO x (ppm) NH 3 (ppm) 2-1 301 101 101 201 60 0.02 0.7 80 0.02 2.1 2-2 302 " 102 " 60 0.03 0.8 80 0.03 1.9 " 303 " 103 " 60 0.02 0.9 80 0.02 2.2 " 304 " 104 " 60 0.03 1.0 80 0.03 1.9 " 305 " 105 " 60 0.03 1.1 80 0.03 2.0 " 306 " 106 " 60 0.03 0.9 80 0.02 1.8 " 307 " 107 " 60 0.03 1.0 80 0.02 1.7 " 308 " 108 " 60 0.02 0.9 80 0.04 1.8 " 309 " 109 " 60 0.03 1.0 80 0.04 1.8 " 310 " 110 " 60 0.03 1.0 80 0.04 1.7 " 311 " 111 " 60 0.03 0.9 80 0.03 1.9 " 312 " 112 " 60 0.03 1.0 80 0.04 2.0 2-2 313 101 13 201 60 0.03 1.0 80 0.02 2.1 " 314 " 14 " 60 0.02 1.1 80 0.02 1.9 " 315 " 15 " 60 0.04 1.2 80 0.02 2.1 " 316 " 16 " 60 0.04 1.1 80 0.03 2.0 " 317 " 17 " 60 0.03 1.0 80 0.03 1.9 " 318 " 18 " 60 0.03 0.9 80 0.04 2.0 " 319 " 19 " 60 0.03 1.0 80 0.03 1.9 2-3 320 " 1 202 60 0.03 0.8 80 0.02 2.2 " 321 " 1 203 60 0.03 0.7 80 0.03 2.3 1 322 101 - - 60 0.02 10.1 80 0.03 29.7 " 323 101 101 - 60 0.7 2.4 80 1.6 7.8 " 324 101 101 Denitration catalyst similar to that in 1st step 101 60 0.02 1.5 80 0.03 6.2

Claims: A method for removing nitrogen oxides from an exhaust gas comprising: (a) flowing the exhaust gas containing the nitrogen oxides through a reaction vessel packed with a first denitration catalyst layer, an ammonia decomposition catalyst layer downstream of the first denitration catalyst layer and which contains a catalyst capable of oxidatively decomposing ammonia into nitrogen and nitrogen oxides, and a second denitration catalyst layer downstream of the ammonia decomposition catalyst layer; and (b) adding ammonia as a reducing agent to the exhaust gas prior to the first denitration catalyst layer in an amount not less than the reaction equivalence for the nitrogen oxides contained in the exhaust gas; wherein the ammonia decomposition catalyst has: (i) a crystalline silicate carrier which in its dehydrated form has the formula: (1.0±0.8)R 2 O· [aM 2 O 3 ·bAl 2 O 3 ] ·cMeO·ySiO 2 wherein R is an alkaline metal ion and/or hydrogen ion; M is at least one of a group VIII element, a rare earth element, titanium, vanadium, chromium, niobium, antimony and gallium; Me is an alkaline earth metal, a≥0, b≥0, c≥0, a+b=1, y>12, and y/c>12; the silicate having an X-ray diffraction pattern as shown in Table 1 in the specification, and (ii) at least one active metal selected from platinum, palladium, ruthenium, iridium, and rhodium. A method according to Claim 1, wherein the ammonia is added in step (b) to the exhaust gas at the inlet of the first denitration catalyst layer. A method according to Claim 1 or Claim 2, wherein the ammonia decomposition catalyst is a catalyst having a performance of 70% or higher as % nitrogen selection defined as follows: % nitrogen selection =[1-{NOx (ppm) at outlet of ammonia decomposition catalyst - NOx (ppm at inlet of ammonia decomposition catalyst/NH 3 (ppm) at inlet of ammonia decomposition catalyst - NH 3 (ppm) at outlet of ammonia decomposition catalyst)]. A method according to any preceding Claim, wherein the first and second denitration catalyst layers contain TiO 2 -based catalysts containing V, W or Mo as an active component. A method according to any of Claims 1-3, wherein the second denitration catalyst layer is capable of decomposing ammonia and contains a TiO 2 -based catalyst supporting either 4.5% by wt. or more of V 2 O 5 or 0.0001% by wt. or more of Pt, Pd, Ru, Rh or Ir.

Inventors: IIDA KOUZO, KOBAYASHI NORIHISA, NOJIMA SHIGERU, OBAYASHI YOSHIAKI, SERIZAWA SATORU, IIDA, KOUZO, KOBAYASHI, NORIHISA, NOJIMA, SHIGERU, OBAYASHI, YOSHIAKI, SERIZAWA, SATORU, IIDA, KOUZO, MITSUBISHI JUKOGYO K.K., KOBAYASHI, NORIHISA, C/O MITSUBISHI JUKOGYO K.K., NOJIMA, SHIGERU, MITSUBISHI JUKOGYO K.K., OBAYASHI, YOSHIAKI, MITSUBISHI JUKOGYO K.K., Serizawa, Satoru, c/o Nagasaki Shipyard &amp; Mach. W.
Applicants: MITSUBISHI HEAVY IND LTD, MITSUBISHI JUKOGYO KABUSHIKI KAISHA
Application year: 1995
Main classification: B01D53
IPC codes: B01J29, B01D53