WO2009130934A1 - 脱硝触媒製造用スラリー、同スラリーの製造方法、同スラリーを用いる脱硝触媒の製造方法および同方法により製造された脱硝触媒 - Google Patents
脱硝触媒製造用スラリー、同スラリーの製造方法、同スラリーを用いる脱硝触媒の製造方法および同方法により製造された脱硝触媒 Download PDFInfo
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- WO2009130934A1 WO2009130934A1 PCT/JP2009/052469 JP2009052469W WO2009130934A1 WO 2009130934 A1 WO2009130934 A1 WO 2009130934A1 JP 2009052469 W JP2009052469 W JP 2009052469W WO 2009130934 A1 WO2009130934 A1 WO 2009130934A1
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- denitration catalyst
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/16—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
- B01J23/24—Chromium, molybdenum or tungsten
- B01J23/30—Tungsten
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8621—Removing nitrogen compounds
- B01D53/8625—Nitrogen oxides
- B01D53/8628—Processes characterised by a specific catalyst
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/88—Handling or mounting catalysts
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J21/00—Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
- B01J21/06—Silicon, titanium, zirconium or hafnium; Oxides or hydroxides thereof
- B01J21/063—Titanium; Oxides or hydroxides thereof
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/002—Mixed oxides other than spinels, e.g. perovskite
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/02—Impregnation, coating or precipitation
- B01J37/0215—Coating
- B01J37/0219—Coating the coating containing organic compounds
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/20—Reductants
- B01D2251/206—Ammonium compounds
- B01D2251/2062—Ammonia
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20707—Titanium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20723—Vanadium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20776—Tungsten
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/30—Silica
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2523/00—Constitutive chemical elements of heterogeneous catalysts
Definitions
- the present invention relates to a slurry for producing a denitration catalyst used when producing a catalyst for denitration treatment of exhaust gas from a power generation gas turbine, coal-fired boiler, various chemical plants, incinerators, etc., a method for producing the slurry,
- the present invention relates to a method for producing a denitration catalyst to be used and a denitration catalyst produced by the method.
- Patent Documents 1 to 3 Methods for producing a denitration catalyst using a slurry containing a catalyst component such as vanadium are described in Patent Documents 1 to 3, for example.
- a conventional denitration catalyst is manufactured, for example, through the steps summarized below.
- a ceramic fiber honeycomb structure is immersed in a slurry in which titania fine particles are suspended in silica sol, thereby supporting titania on the honeycomb structure. Thereafter, the honeycomb structure is taken out of the slurry and dried. Bake.
- honeycomb structure after the treatment of (1) is immersed in an aqueous solution of ammonium metavanadate (hereinafter referred to as AMV), the honeycomb structure is taken out from the aqueous solution, and then dried and fired.
- AMV ammonium metavanadate
- honeycomb structure after the above treatment (2) is immersed in an aqueous solution of ammonium metatungstate (hereinafter referred to as AMT), and the honeycomb structure is taken out from the aqueous solution, and then dried and fired.
- AMT ammonium metatungstate
- titania can be supported up to the inside of the ceramic fiber sheet forming the honeycomb structure.
- vanadium is supported on titania through a process in which AMV is adsorbed to titania. Therefore, vanadium is easily supported on titania existing near the surface of the ceramic fiber sheet, but is difficult to be supported on the inside of the ceramic fiber sheet. . For this reason, vanadium tended to be supported only on titania present near the surface of the ceramic fiber sheet.
- Catalyst performance is not demonstrated by titania alone, but only when vanadium is supported on titania. Therefore, in the catalyst manufactured by the conventional method, only the surface area of the ceramic fiber sheet functions as a catalyst. In general, in the denitration reaction, since the gas movement of the laminar boundary film is reaction-controlled, even a catalyst produced by a conventional method and functioning only as a surface area catalyst is usually used. There is no effect on the NOx removal performance.
- the present invention has been made in order to solve the above-mentioned problems, and it is possible to extend the life of a catalyst by making the active component of the catalyst exist even in the inner region of the ceramic fiber sheet, and the production cost can be increased.
- the present invention provides a slurry for producing a denitration catalyst, a method for producing the slurry, a method for producing a denitration catalyst using the slurry, and a denitration catalyst produced by the method. With the goal.
- AMV is added to a slurry in which titania fine particles are suspended in silica sol, and AMV is adsorbed and supported on titania in the slurry; (2) Add AMT to the slurry obtained in (1); (3) An organic acid ammonium salt such as ammonium polyacrylate is added to the slurry obtained in (2); (4) A catalyst in which titania, vanadium oxide, and tungsten oxide are supported on the honeycomb structure by immersing the honeycomb structure in the slurry obtained in (3), removing the honeycomb structure from the slurry, and drying and firing. Are prepared simultaneously in a single step.
- the present invention is a slurry for producing a denitration catalyst comprising silica sol, titania particles, metavanadate particles supported on the titania particles, metatungstic acid particles, and an organic acid ammonium salt.
- an aqueous ammonia solution is preferably added so that the pH is 4-7.
- the concentration of the organic acid ammonium salt is 25 to 125 mL per liter of the entire slurry volume.
- the organic acid ammonium salt is ammonium polyacrylate.
- the titania particle powder is mixed with silica sol to form a suspension, and AMV is added thereto so that the metavanadate is supported on the surface of the titania particles, and then AMT is added, Next, an organic acid ammonium salt is added, which is a method for producing a slurry for producing a denitration catalyst.
- an aqueous ammonia solution so that the pH is 4 to 7 after the addition of AMT and before the addition of the organic acid ammonium salt.
- the concentration of the organic acid ammonium salt is 25 to 125 mL per liter of the total volume of the final slurry.
- the organic acid ammonium salt is ammonium polyacrylate.
- the present invention also relates to a method for producing a denitration catalyst, wherein the catalyst substrate is immersed in the slurry for producing a denitration catalyst or the slurry for producing a denitration catalyst produced by the method for producing a slurry for producing a denitration catalyst. It is characterized by.
- the catalyst substrate is preferably a honeycomb substrate, and the honeycomb substrate is preferably composed of an inorganic fiber sheet.
- the present invention is a denitration catalyst produced by the above method.
- vanadium oxide is supported on the titania particles in the suspension by adding AMV to the suspension obtained by mixing the titania powder in the silica sol.
- titania carrying AMV adsorbed and supported can be arranged up to the inside of the ceramic fiber sheet, and a denitration catalyst that can function as the catalyst inside the sheet can be obtained.
- an organic acid ammonium salt is added, whereby the solid content aggregated in the slurry production stage is redispersed, so that the solid content particles supported on the honeycomb substrate as a catalyst The diameter is reduced, the catalytic activity point is increased, and the catalyst performance is improved.
- the catalyst activity is not adversely affected and a catalyst having improved durability can be manufactured. Therefore, productivity is improved and cost is reduced.
- Example 1 A slurry was prepared by adding titania fine particles to a silica sol so that the solid content ratio was 45% by weight and the weight ratio of silica and titania was 20:80. Then, the AMV was adsorbed to titania in the slurry by stirring for 1 hour.
- AMT aqueous solution (3.88 mol / L as tungsten) was further added to the slurry obtained in 1) so as to be 28 mL per 1 kg of slurry, and the mixture was stirred for 1 hour.
- Examples 2 to 5 The amount of ammonium polyacrylate added in step 3) of Example 1 above is 50 mL (Example 2), 75 mL (Example 3), 100 mL (Example 4) or 125 mL (Example 5) with respect to 1 L of slurry.
- a slurry was prepared in the same manner as in Example 1 except for changing to.
- Example 6 A slurry is prepared by adding titania fine particles to silica sol so that the solid content ratio is 45% by weight and the weight ratio of silica and titania is 20:80. Further, AMV powder is added to this slurry in 1 kg of the above slurry. Then, the AMV was adsorbed to titania in the slurry by stirring for 1 hour.
- Examples 7 to 10 The amount of ammonium polyacrylate added in step 3) of Example 6 above is 50 mL (Example 7), 75 mL (Example 8), 100 mL (Example 9) or 125 mL (Example 10) with respect to 1 L of slurry.
- a slurry was prepared in the same manner as in Example 6 except for changing to.
- a denitration catalyst was produced using each of the slurries prepared in Examples 1-10.
- the catalyst was produced according to the following process.
- a honeycomb structure was manufactured by alternately laminating corrugated ceramic fiber sheets and flat ceramic fiber sheets.
- honeycomb structure of 1) was dipped in each of the slurries of Examples 1 to 10, taken out from the slurry, dried at 110 ° C., and then fired at 400 ° C. for 1 hour, whereby each catalyst was completed.
- Example 1 The slurry prepared by adding titania fine particles to the silica sol so that the solid content ratio was 45% by weight and the weight ratio of silica to titania was 20:80 was used in Examples 1 to 10 above.
- the same honeycomb structure is immersed, taken out from the slurry and fired at 450 ° C., then the honeycomb structure is immersed in an AMV aqueous solution (2.75 g / L), taken out and dried at 200 ° C.,
- the catalyst was obtained by calcination at 450 ° C., which was taken out by immersion in an AMT aqueous solution (0.2 mol / L as tungsten).
- “Balance” in Table 1 indicates that the gas composition is added so that the total gas composition becomes 100%, and the gas composition other than NH 3 , NO, and H 2 O is air (indicated as Air in the table). ).
- the supported amount means the total supported amount of the catalyst components (titania, vanadium oxide, tungsten oxide), and the step of immersing the honeycomb structure in each slurry, taking it out of the slurry and firing it was completed. It is measured by the weight difference calculated by subtracting the weight of the starting honeycomb structure before performing the step of immersing in the slurry from the weight of the subsequent honeycomb structure.
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- Chemical Kinetics & Catalysis (AREA)
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Abstract
Description
(2)(1)で得られたスラリーにAMTを添加する;
(3)(2)で得られたスラリーにポリアクリル酸アンモニウム等の有機酸アンモニウム塩を添加する;
(4)(3)で得られたスラリーにハニカム構造体を浸漬し、これをスラリーから取り出した後、乾燥・焼成することにより、ハニカム構造体にチタニア、酸化バナジウムおよび酸化タングステンが担持された触媒を単一工程で同時に調製する。
1)固形分比率が45重量%、シリカとチタニアとの重量比率が20:80になるようにチタニア微粒子をシリカゾルに添加してスラリーを調製し、さらに、このスラリーに、AMV粉末を上記スラリー1kg当たり50gになるように添加し、その後、これを1時間攪拌することにより、AMVをスラリー中のチタニアに吸着させた。
上記の実施例1の工程3)におけるポリアクリル酸アンモニウムの添加量をスラリー1Lに対して50mL(実施例2)、75mL(実施例3)、100mL(実施例4)または125mL(実施例5)に変更した以外は、実施例1と同様にしてスラリーを調製した。
1)固形分比率が45重量%、シリカとチタニアとの重量比率が20:80になるようにチタニア微粒子をシリカゾルに添加してスラリーを調製し、さらに、このスラリーに、AMV粉末を上記スラリー1kg当たり50gになるように添加し、その後、これを1時間攪拌することにより、AMVをスラリー中のチタニアに吸着させた。
上記の実施例6の工程3)におけるポリアクリル酸アンモニウムの添加量をスラリー1Lに対して50mL(実施例7)、75mL(実施例8)、100mL(実施例9)または125mL(実施例10)に変更した以外は、実施例6と同様にしてスラリーを調製した。
固形分比率が45重量%、シリカとチタニアとの重量比率が20:80になるようにチタニア微粒子をシリカゾルに添加することにより調製されたスラリーに、上記実施例1~10において用いられたのと同一のハニカム構造体を浸漬し、これをスラリーから取り出し、450℃で焼成した後、ハニカム構造体をAMV水溶液(2.75g/L)に浸漬し、これを取り出して200℃で乾燥させ、次いで、AMT水溶液(タングステンとして0.2mol/L)に浸漬して取り出した、450℃で焼成することにより、触媒を得た。
Claims (12)
- シリカゾルと、チタニア粒子と、該チタニア粒子上に担持されたメタバナジン酸粒子と、メタタングステン酸粒子と、有機酸アンモニウム塩とを含む脱硝触媒製造用スラリー。
- pHが4~7になるようにアンモニア水溶液が添加されている、請求項1に記載の脱硝触媒製造用スラリー。
- 有機酸アンモニウム塩の濃度は、スラリー全体の容積1L当たり25~125mLである、請求項1または2に記載の脱硝触媒製造用スラリー。
- 有機酸アンモニウム塩がポリアクリル酸アンモニウムである、請求項1~3のいずれか1つに記載の脱硝触媒製造用スラリー。
- シリカゾルにチタニア粒子粉末を混合して懸濁液とし、これにメタバナジン酸アンモニウム粉末を加えて該チタニア粒子表面上に該メタバナジン酸が担持されるようにし、その後に、メタタングステン酸アンモニウムを添加し、次いで、有機酸アンモニウム塩を添加することを特徴とする脱硝触媒製造用スラリーの製造方法。
- メタタングステン酸アンモニウムの添加後、有機酸アンモニウム塩の添加前に、pHが4~7になるようにアンモニア水溶液を添加する、請求項3に記載の脱硝触媒製造用スラリーの製造方法。
- 有機酸アンモニウム塩の濃度は、最終スラリー全体の容積1L当たり25~125mLである、請求項5または6に記載の脱硝触媒製造用スラリーの製造方法。
- 有機酸アンモニウム塩がポリアクリル酸アンモニウムである、請求項5~7のいずれか1つに記載の脱硝触媒製造用スラリーの製造方法。
- 脱硝触媒の製造方法であって、請求項1~4のいずれか1つに記載の脱硝触媒製造用スラリーまたは請求項5~8のいずれか1つに記載の脱硝触媒製造用スラリーの製造方法によって製造された脱硝触媒製造用スラリーに触媒基材を浸漬することを特徴とする方法。
- 前記触媒基材がハニカム基材である、請求項9に記載の方法。
- 前記ハニカム基材は、無機繊維シートで構成される、請求項10に記載の方法。
- 請求項9~11のいずか1つに記載の方法により製造された脱硝触媒。
Priority Applications (3)
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US12/936,531 US8133833B2 (en) | 2008-04-22 | 2009-02-16 | Slurry for production of denitration catalyst, process for producing the slurry, process for producing denitration catalyst using the slurry, and denitration catalyst produced by the process |
CN200980113988.XA CN102015098B (zh) | 2008-04-22 | 2009-02-16 | 脱硝催化剂制备用浆液、该浆液的制备方法、使用该浆液的脱硝催化剂的制备方法及通过该方法制备的脱硝催化剂 |
DK201070491A DK178346B1 (en) | 2008-04-22 | 2010-11-16 | Slurry for production of denitration catalyst, process for producing the slurry, process for producing denitration catalyst using the slurry and denitration catalyst produced by the process |
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JP2008111401A JP5401049B2 (ja) | 2008-04-22 | 2008-04-22 | 脱硝触媒製造用スラリー、同スラリーの製造方法、同スラリーを用いる脱硝触媒の製造方法および同方法により製造された脱硝触媒 |
JP2008-111401 | 2008-04-22 |
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JP (1) | JP5401049B2 (ja) |
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WO2012132540A1 (ja) * | 2011-03-25 | 2012-10-04 | 日立造船株式会社 | 脱硝触媒の調製方法 |
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CN110354912A (zh) * | 2019-08-08 | 2019-10-22 | 杭州玺富环保科技有限公司 | 催化型陶瓷纤维滤管生产线和生产工艺 |
Also Published As
Publication number | Publication date |
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DK201070491A (en) | 2010-11-18 |
DK178346B1 (en) | 2015-12-21 |
US20110028309A1 (en) | 2011-02-03 |
US8133833B2 (en) | 2012-03-13 |
JP5401049B2 (ja) | 2014-01-29 |
CN102015098B (zh) | 2013-10-16 |
JP2009262006A (ja) | 2009-11-12 |
CN102015098A (zh) | 2011-04-13 |
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