CN113318698A - Alkali metal loaded ceramic catalytic filler and preparation method thereof - Google Patents
Alkali metal loaded ceramic catalytic filler and preparation method thereof Download PDFInfo
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- 239000000919 ceramic Substances 0.000 title claims abstract description 236
- 239000000945 filler Substances 0.000 title claims abstract description 234
- 229910052783 alkali metal Inorganic materials 0.000 title claims abstract description 81
- 150000001340 alkali metals Chemical class 0.000 title claims abstract description 81
- 230000003197 catalytic effect Effects 0.000 title claims abstract description 81
- 238000002360 preparation method Methods 0.000 title claims abstract description 24
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims abstract description 45
- 238000010521 absorption reaction Methods 0.000 claims abstract description 43
- 229910002092 carbon dioxide Inorganic materials 0.000 claims abstract description 32
- 239000001569 carbon dioxide Substances 0.000 claims abstract description 22
- 239000007788 liquid Substances 0.000 claims abstract description 18
- 239000000395 magnesium oxide Substances 0.000 claims abstract description 17
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 claims abstract description 17
- 229910001413 alkali metal ion Inorganic materials 0.000 claims abstract description 14
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 claims abstract description 14
- 238000001035 drying Methods 0.000 claims description 101
- 239000000243 solution Substances 0.000 claims description 65
- 239000011261 inert gas Substances 0.000 claims description 56
- 238000001816 cooling Methods 0.000 claims description 49
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 claims description 45
- 239000011777 magnesium Substances 0.000 claims description 44
- 239000008367 deionised water Substances 0.000 claims description 43
- 229910021641 deionized water Inorganic materials 0.000 claims description 43
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 43
- 238000005470 impregnation Methods 0.000 claims description 39
- 238000010438 heat treatment Methods 0.000 claims description 37
- 238000001354 calcination Methods 0.000 claims description 35
- 238000005406 washing Methods 0.000 claims description 30
- 239000003513 alkali Substances 0.000 claims description 29
- 239000012266 salt solution Substances 0.000 claims description 29
- 150000008044 alkali metal hydroxides Chemical class 0.000 claims description 26
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical group [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 21
- 150000001412 amines Chemical class 0.000 claims description 20
- 238000009835 boiling Methods 0.000 claims description 15
- 239000012535 impurity Substances 0.000 claims description 15
- 235000006408 oxalic acid Nutrition 0.000 claims description 15
- 238000010992 reflux Methods 0.000 claims description 15
- MFUVDXOKPBAHMC-UHFFFAOYSA-N magnesium;dinitrate;hexahydrate Chemical group O.O.O.O.O.O.[Mg+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O MFUVDXOKPBAHMC-UHFFFAOYSA-N 0.000 claims description 14
- 238000004140 cleaning Methods 0.000 claims description 13
- 159000000003 magnesium salts Chemical class 0.000 claims description 13
- 150000003839 salts Chemical class 0.000 claims description 13
- 238000000034 method Methods 0.000 claims description 11
- 229940097364 magnesium acetate tetrahydrate Drugs 0.000 claims description 10
- XKPKPGCRSHFTKM-UHFFFAOYSA-L magnesium;diacetate;tetrahydrate Chemical compound O.O.O.O.[Mg+2].CC([O-])=O.CC([O-])=O XKPKPGCRSHFTKM-UHFFFAOYSA-L 0.000 claims description 10
- 239000006260 foam Substances 0.000 claims description 7
- 239000000126 substance Substances 0.000 claims description 5
- 238000004519 manufacturing process Methods 0.000 claims 4
- 238000011017 operating method Methods 0.000 claims 2
- 150000003512 tertiary amines Chemical class 0.000 abstract description 7
- 230000000052 comparative effect Effects 0.000 description 8
- 238000012856 packing Methods 0.000 description 7
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 6
- 238000006243 chemical reaction Methods 0.000 description 6
- 239000003546 flue gas Substances 0.000 description 6
- PVXVWWANJIWJOO-UHFFFAOYSA-N 1-(1,3-benzodioxol-5-yl)-N-ethylpropan-2-amine Chemical compound CCNC(C)CC1=CC=C2OCOC2=C1 PVXVWWANJIWJOO-UHFFFAOYSA-N 0.000 description 3
- QMMZSJPSPRTHGB-UHFFFAOYSA-N MDEA Natural products CC(C)CCCCC=CCC=CC(O)=O QMMZSJPSPRTHGB-UHFFFAOYSA-N 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 238000011156 evaluation Methods 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 150000003141 primary amines Chemical class 0.000 description 3
- 230000000630 rising effect Effects 0.000 description 3
- 150000003335 secondary amines Chemical class 0.000 description 3
- 238000012795 verification Methods 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 230000002745 absorbent Effects 0.000 description 2
- 239000002250 absorbent Substances 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- 238000009833 condensation Methods 0.000 description 2
- 230000005494 condensation Effects 0.000 description 2
- 230000007547 defect Effects 0.000 description 2
- 238000003795 desorption Methods 0.000 description 2
- 239000002904 solvent Substances 0.000 description 2
- 229910001220 stainless steel Inorganic materials 0.000 description 2
- 239000010935 stainless steel Substances 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- KXDHJXZQYSOELW-UHFFFAOYSA-M Carbamate Chemical compound NC([O-])=O KXDHJXZQYSOELW-UHFFFAOYSA-M 0.000 description 1
- -1 MEA) Chemical class 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 238000002479 acid--base titration Methods 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000005431 greenhouse gas Substances 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 125000004435 hydrogen atom Chemical class [H]* 0.000 description 1
- 238000009413 insulation Methods 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 125000004433 nitrogen atom Chemical group N* 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 230000036632 reaction speed Effects 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000002791 soaking Methods 0.000 description 1
Classifications
-
- 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
- B01J19/00—Chemical, physical or physico-chemical processes in general; Their relevant apparatus
- B01J19/30—Loose or shaped packing elements, e.g. Raschig rings or Berl saddles, for pouring into the apparatus for mass or heat transfer
-
- 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
- B01D53/46—Removing components of defined structure
- B01D53/62—Carbon oxides
-
- 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
- B01D53/77—Liquid phase processes
- B01D53/78—Liquid phase processes with gas-liquid contact
-
- 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
-
- 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
- B01J23/02—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the alkali- or alkaline earth metals or beryllium
- B01J23/04—Alkali metals
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/80—Organic bases or salts
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/202—Alkali metals
- B01D2255/2022—Potassium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/204—Alkaline earth metals
- B01D2255/2047—Magnesium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/50—Carbon oxides
- B01D2257/504—Carbon dioxide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0283—Flue gases
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Abstract
The invention discloses an alkali metal loaded ceramic catalytic filler and a preparation method thereof, the alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, the active component comprises alkali metal ions and magnesium oxide, the filler can accelerate the rate of tertiary amine absorbing carbon dioxide, and can avoid the problems of insufficient space of an absorption tower, overweight internal parts and gas-liquid flow, and the preparation method is simple.
Description
Technical Field
The invention belongs to the technical field of emission reduction of greenhouse gas carbon dioxide, and relates to an alkali metal loaded ceramic catalytic filler and a preparation method thereof.
Background
The chemical absorption method is more commonly used, organic amine mainly comprises primary amine (such as MEA), secondary amine (such as DEA) and tertiary amine (such as MDEA, TEA and the like), the primary amine and the secondary amine react with carbon dioxide relatively quickly, and the generated carbamate has relatively stable chemical property, but has the defects of small saturated capacity of the carbon dioxide, large heat of desorption reaction and the like; compared with primary amine and secondary amine, the tertiary amine has large carbon dioxide saturation capacity and small heat of desorption reaction, but because the N atom of the tertiary amine does not contain active hydrogen, the tertiary amine can only indirectly react with CO2The rate of absorption of carbon dioxide by tertiary amines is relatively slow as a result of molecular reactions.
The organic amine solution chemical absorption of carbon dioxide usually adopts a filler absorption tower, and stainless steel, plastic or ceramic filler is arranged in the absorption tower to increase the gas-liquid contact area and the mass transfer efficiency. If the catalyst and the filler are respectively arranged in the absorption tower, the problems of insufficient space, heavy internal parts, gas-liquid flow and the like of the absorption tower can be caused.
Disclosure of Invention
The invention aims to overcome the defects of the prior art and provides an alkali metal-loaded ceramic catalytic filler and a preparation method thereof, wherein the filler can accelerate the rate of tertiary amine absorbing carbon dioxide, can avoid the problems of insufficient space of an absorption tower, overweight internal parts and gas-liquid flow, and is simple in preparation method.
In order to achieve the above object, the alkali metal-loaded ceramic catalytic filler of the present invention comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is honeycomb porous ceramic filler or foam porous ceramic filler.
The porous ceramic filler is pall ring, Raschig ring, ceramic ball or corrugated plate.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) pretreating the porous ceramic filler;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 5-20%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 5-20%;
3) immersing the porous ceramic filler in Mg salt solution, and then carrying out ultrasonic impregnation, drying, calcining and cooling;
4) immersing the porous ceramic filler treated in the step 3) in an alkali solution, and then carrying out ultrasonic impregnation, drying, calcining and cooling to obtain the alkali metal loaded ceramic catalytic filler.
The magnesium salt is magnesium nitrate hexahydrate or magnesium acetate tetrahydrate.
The alkali metal hydroxide is NaOH or KOH.
The specific operation process of the step 1) is as follows:
removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing liquid is 7, and finally drying for 12h in an oven at the temperature of 110 ℃.
The specific operation process of the step 3) is as follows:
immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 2-4 times, wherein the ultrasonic impregnation is carried out for 1-3 h, the drying temperature is 110 ℃, the drying time is 12h, then heating to 500-fold at the heating rate of 5 ℃/min under the atmosphere of inert gas, calcining at constant temperature for 2h, and then naturally cooling to room temperature under the atmosphere of inert gas.
The specific operation of the step 4) is as follows:
immersing the calcined porous ceramic filler in an alkali solution, performing ultrasonic impregnation and drying for 2-4 times, wherein the ultrasonic impregnation is performed for 1-3 h, the drying temperature is 110 ℃, the drying time is 12h, then heating to 500-fold at the heating rate of 5 ℃/min under the atmosphere of inert gas, calcining at constant temperature for 2h, and then naturally cooling to room temperature under the atmosphere of inert gas to obtain the alkali metal loaded ceramic catalytic filler.
The invention has the following beneficial effects:
the alkali metal loaded ceramic catalytic filler and the preparation method thereof have the advantages that during specific operation, the active component is attached to the porous ceramic filler, and the CO is accelerated while the gas-liquid distribution and mass transfer functions of the conventional filler are not influenced2The reaction rate with organic amine molecules is increased, and CO is increased2The absorption speed and the absorption capacity of the organic amine, and the solution of organic amine absorption solvent and CO2Low reaction speed, high energy consumption and the like, and can reduce CO2The amine solvent circulation amount of the trapping device, the system power consumption and the subsequent solution heating regeneration steam consumption. Meanwhile, a catalyst and a filler do not need to be separately arranged in the absorption tower, so that the problems of insufficient space of the absorption tower, overweight internal parts and gas-liquid flow are avoided, and in addition, the preparation method is simpler by adopting the processes of ultrasonic impregnation, drying and calcination.
Detailed Description
In order to make those skilled in the art better understand the technical solution of the present invention, the following will clearly and completely describe the technical solution of the present invention with reference to the embodiments, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, not all of the embodiments, and are not intended to limit the scope of the disclosure of the present invention. Moreover, in the following description, descriptions of well-known structures and techniques are omitted so as to not unnecessarily obscure the concepts of the present disclosure. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.
The alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is honeycomb porous ceramic filler or foam porous ceramic filler.
The porous ceramic filler is pall ring, Raschig ring, ceramic ball or corrugated plate.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) pretreating the porous ceramic filler;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 5-20%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 5-20%;
3) immersing the porous ceramic filler in Mg salt solution, and then carrying out ultrasonic impregnation, drying, calcining and cooling;
4) immersing the porous ceramic filler treated in the step 3) in an alkali solution, and then carrying out ultrasonic impregnation, drying, calcining and cooling to obtain the alkali metal loaded ceramic catalytic filler.
The magnesium salt is magnesium nitrate hexahydrate or magnesium acetate tetrahydrate.
The alkali metal hydroxide is NaOH or KOH.
The specific operation process of the step 1) is as follows:
removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing liquid is 7, and finally drying for 12h in an oven at the temperature of 110 ℃.
The specific operation process of the step 3) is as follows:
immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 2-4 times, wherein the ultrasonic impregnation is carried out for 1-3 h, the drying temperature is 110 ℃, the drying time is 12h, then heating to 500-fold at the heating rate of 5 ℃/min under the atmosphere of inert gas, calcining at constant temperature for 2h, and then naturally cooling to room temperature under the atmosphere of inert gas.
The specific operation of the step 4) is as follows:
immersing the calcined porous ceramic filler in an alkali solution, performing ultrasonic impregnation and drying for 2-4 times, wherein the ultrasonic impregnation is performed for 1-3 h, the drying temperature is 110 ℃, the drying time is 12h, then heating to 500-fold at the heating rate of 5 ℃/min under the atmosphere of inert gas, calcining at constant temperature for 2h, and then naturally cooling to room temperature under the atmosphere of inert gas to obtain the alkali metal loaded ceramic catalytic filler.
Example one
The alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is honeycomb porous ceramic filler.
The porous ceramic filler is pall ring.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing solution is 7, and finally drying for 12h in an oven at the temperature of 110 ℃;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 10%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 20%;
3) immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 3 times, wherein the ultrasonic impregnation is carried out for 2 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then heating to 600 ℃ at the heating rate of 5 ℃/min under the inert gas atmosphere, then carrying out constant-temperature calcination for 2 hours, and then naturally cooling to the room temperature under the inert gas atmosphere;
4) immersing the calcined porous ceramic filler in an alkali solution, and then ultrasonically immersing and drying for 3 times, wherein the ultrasonic immersing is carried out for 1h-3h, the drying temperature is 110 ℃, the drying time is 12h, then the temperature is raised to 600 ℃ at the temperature raising speed of 5 ℃/min under the atmosphere of inert gas, then the constant-temperature calcining is carried out for 2h, and then the natural cooling is carried out to the room temperature under the atmosphere of inert gas, so as to obtain the alkali metal loaded ceramic catalytic filler, and obtain the alkali metal loaded ceramic catalytic filler.
The magnesium salt is magnesium nitrate hexahydrate.
The alkali metal hydroxide is KOH.
Example two
The alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is foam porous ceramic filler.
The porous ceramic filler is pall ring.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing solution is 7, and finally drying for 12h in an oven at the temperature of 110 ℃;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 15%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 10%;
3) immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 2 times, wherein the ultrasonic impregnation is carried out for 2 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then heating to 600 ℃ at the heating rate of 5 ℃/min under the inert gas atmosphere, then carrying out constant-temperature calcination for 2 hours, and then naturally cooling to the room temperature under the inert gas atmosphere;
4) immersing the calcined porous ceramic filler in an alkali solution, and then ultrasonically immersing and drying for 2 times, wherein the ultrasonic immersing is carried out for 2 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then the temperature is raised to 600 ℃ at the temperature raising speed of 5 ℃/min under the atmosphere of inert gas, then the constant-temperature calcining is carried out for 2 hours, and then the natural cooling is carried out to the room temperature under the atmosphere of inert gas, so as to obtain the ceramic catalytic filler loaded by alkali metal, and obtain the ceramic catalytic filler loaded by alkali metal.
The magnesium salt is magnesium nitrate hexahydrate.
The alkali metal hydroxide is KOH.
EXAMPLE III
The alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is honeycomb porous ceramic filler.
The porous ceramic filler is Raschig ring.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing solution is 7, and finally drying for 12h in an oven at the temperature of 110 ℃;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 10%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 10%;
3) immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 3 times, wherein the ultrasonic impregnation is carried out for 2 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then heating to 600 ℃ at the heating rate of 5 ℃/min under the inert gas atmosphere, then carrying out constant-temperature calcination for 2 hours, and then naturally cooling to the room temperature under the inert gas atmosphere;
4) immersing the calcined porous ceramic filler in an alkali solution, and then ultrasonically immersing and drying for 2 times, wherein the ultrasonic immersing is carried out for 2 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then the temperature is raised to 600 ℃ at the temperature raising speed of 5 ℃/min under the atmosphere of inert gas, then the constant-temperature calcining is carried out for 2 hours, and then the natural cooling is carried out to the room temperature under the atmosphere of inert gas, so as to obtain the ceramic catalytic filler loaded by alkali metal, and obtain the ceramic catalytic filler loaded by alkali metal.
The magnesium salt is magnesium acetate tetrahydrate.
The alkali metal hydroxide is KOH.
Example four
The alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is foam porous ceramic filler.
The porous ceramic filler is Raschig ring.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing solution is 7, and finally drying for 12h in an oven at the temperature of 110 ℃;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 15%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 20%;
3) immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 3 times, wherein the ultrasonic impregnation is carried out for 2 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then heating to 600 ℃ at the heating rate of 5 ℃/min under the inert gas atmosphere, then carrying out constant-temperature calcination for 2 hours, and then naturally cooling to the room temperature under the inert gas atmosphere;
4) immersing the calcined porous ceramic filler in an alkali solution, and then ultrasonically immersing and drying for 3 times, wherein the ultrasonic immersing is carried out for 2 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then the temperature is raised to 600 ℃ at the temperature raising speed of 5 ℃/min under the atmosphere of inert gas, then the constant-temperature calcining is carried out for 2 hours, and then the natural cooling is carried out to the room temperature under the atmosphere of inert gas, so as to obtain the ceramic catalytic filler loaded by alkali metal, and obtain the ceramic catalytic filler loaded by alkali metal.
The magnesium salt is magnesium acetate tetrahydrate.
The alkali metal hydroxide is KOH.
Comparative example 1
This comparative example provides a catalyst-free ceramic blank comprising the steps of:
1) selecting phi 25 pall ring porous ceramic filler, removing surface impurities, pretreating the porous ceramic filler by adopting an oxalic acid solution with the mass fraction of 30%, and carrying out condensation reflux boiling for 1 h; cooling, washing with deionized water until the pH value of the washing liquid is 7, and drying in an oven at 110 ℃ for 12h for later use;
2) and (3) heating the dried ceramic filler to 600 ℃ in a muffle furnace at a heating rate of 5 ℃/min under the atmosphere of inert gas, calcining for 2h, and naturally cooling to room temperature under the atmosphere of inert gas to obtain the hollow ceramic filler.
Comparative example No. two
The comparative example provides a method for preparing an alkali metal-loaded ceramic catalytic filler, comprising the steps of:
1) selecting phi 25 pall ring porous ceramic filler, removing surface impurities, pretreating the porous ceramic filler by adopting an oxalic acid solution with the mass fraction of 30%, and carrying out condensation reflux boiling for 1 h; cooling, washing with deionized water until the pH value of the washing liquid is 7, and drying in an oven at 110 ℃ for 12h for later use;
2) 209g of magnesium nitrate hexahydrate (Mg (NO) were taken3)2.6H2O) is put into a container, 1L of deionized water is added, the mixture is stirred until the deionized water is completely dissolved, and Mg (NO) with the mass concentration of 10 percent is prepared3)2Solution, denoted as solution a 6.
3) Immersing the ceramic filler in the solution A6, ultrasonically immersing for 2h, and then placing the immersed ceramic filler in an oven to dry for 12h at 110 ℃; repeating the soaking and drying for 3 times; heating the soaked and dried ceramic filler to 600 ℃ at a heating rate of 5 ℃/min in an inert gas atmosphere in a muffle furnace, calcining for 2h, and naturally cooling to room temperature in the inert gas atmosphere to obtain the MgO-loaded ceramic filler;
small CO in laboratory for ceramic fillers prepared in examples one to two2Absorption evaluation device for effect verification, CO2The absorption tower used by the absorption evaluation device is a stainless steel reactor with the inner diameter of 95mm, random packing is filled, the length of the packing section is 1m, and a heat insulation layer is arranged outside the absorption tower. The measurement conditions adopted by the present invention are as follows: carbon dioxide (CO)2) 12% by volume of nitrogen (N)2) The volume fraction is 88 percent, and the gas amount is 8L/min; the liquid-gas ratio is 5L/m3(ii) a The temperature of the absorption liquid is 50 ℃; for comparison, the absorption liquid used for evaluation is a newly prepared organic amine aqueous solution and consists of MEA with 5% of mass concentration and MDEA with 15% of mass concentration.
When the reaction conditions are stably achieved, continuously measuring the CO in the outlet gas of the packed tower2Volume fraction and rich liquid CO at rich liquid outlet at bottom of packed tower2Load, CO2The absorption efficiency calculation formula is:
the removal efficiency is high (original flue gas CO)2Volume concentration of raw flue gas flow-clean flue gas CO2Volume concentration net flue gas flow)/(raw flue gas CO2Volume concentration x primary flue gas flow) x 100%;
absorption liquid CO2Absorption liquid CO2Molarity/molarity of solution absorbent;
absorption liquid CO2The molar concentration is obtained by chemical analysis of the excess acid reaction, and the molar concentration of the absorbent is obtained by acid-base titration.
In the effect verification experiment, the pall ring or raschig ring packing loaded in the absorption tower is the CP1, CP2, CP3 and CP4 loaded ceramic packing prepared in the first to fourth examples, and the packing loaded in the first and second comparative absorption towers is the CP5 and CP6 comparative ceramic packing respectively, the volume and other conditions of the packing are the same, and the effect verification result is shown in table 1.
TABLE 1
As can be seen from Table 1, the first to fourth examples enhance the CO content of the MDEA/MEA solution by using the K/MgO-loaded ceramic filler, as compared to the blank ceramic filler of the first comparative example, which is not loaded, and the MgO-only ceramic filler of the second comparative example2Absorption performance, absorption efficiency in absorption column and CO of solution2The load is obviously improved.
EXAMPLE five
The alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is foam porous ceramic filler.
The porous ceramic filler is ceramic balls.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing solution is 7, and finally drying for 12h in an oven at the temperature of 110 ℃;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 5%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 5%;
3) immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 2 times, wherein the ultrasonic impregnation is carried out for 1h, the drying temperature is 110 ℃, the drying time is 12h, then heating to 500 ℃ at the heating rate of 5 ℃/min under the inert gas atmosphere, then carrying out constant-temperature calcination for 2h, and then naturally cooling to room temperature under the inert gas atmosphere;
4) immersing the calcined porous ceramic filler in an alkali solution, and then ultrasonically immersing and drying for 2 times, wherein the ultrasonic immersing is performed for 1h, the drying temperature is 110 ℃, the drying time is 12h, then the temperature is increased to 500 ℃ at the temperature rising speed of 5 ℃/min under the atmosphere of inert gas, then the constant-temperature calcining is performed for 2h, and then the natural cooling is performed to the room temperature under the atmosphere of inert gas, so that the alkali metal loaded ceramic catalytic filler is obtained, and the alkali metal loaded ceramic catalytic filler is obtained.
The magnesium salt is magnesium acetate tetrahydrate.
The alkali metal hydroxide is NaOH.
EXAMPLE six
The alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is honeycomb porous ceramic filler.
The porous ceramic filler is a corrugated plate.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing solution is 7, and finally drying for 12h in an oven at the temperature of 110 ℃;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 20%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 20%;
3) immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 4 times, wherein the ultrasonic impregnation is carried out for 3 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then heating to 700 ℃ at the heating rate of 5 ℃/min under the inert gas atmosphere, then carrying out constant-temperature calcination for 2 hours, and then naturally cooling to the room temperature under the inert gas atmosphere;
4) immersing the calcined porous ceramic filler in an alkali solution, and then ultrasonically immersing and drying for 4 times, wherein the ultrasonic immersing is carried out for 3 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then the temperature is raised to 700 ℃ at the temperature raising speed of 5 ℃/min under the atmosphere of inert gas, then the constant-temperature calcining is carried out for 2 hours, and then the natural cooling is carried out to the room temperature under the atmosphere of inert gas, so as to obtain the ceramic catalytic filler loaded by alkali metal, and obtain the ceramic catalytic filler loaded by alkali metal.
The magnesium salt is magnesium acetate tetrahydrate.
The alkali metal hydroxide is KOH.
EXAMPLE seven
The alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is honeycomb porous ceramic filler.
The porous ceramic filler is a corrugated plate.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing solution is 7, and finally drying for 12h in an oven at the temperature of 110 ℃;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 15%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 15%;
3) immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 3 times, wherein the ultrasonic impregnation is carried out for 2.5 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then heating to 650 ℃ at the heating rate of 5 ℃/min under the atmosphere of inert gas, then carrying out constant-temperature calcination for 2 hours, and then naturally cooling to room temperature under the atmosphere of inert gas;
4) immersing the calcined porous ceramic filler in an alkali solution, and then ultrasonically immersing and drying for 3 times, wherein the ultrasonic immersing is carried out for 2.5 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then the temperature is raised to 650 ℃ at the temperature raising speed of 5 ℃/min under the atmosphere of inert gas, then the constant-temperature calcining is carried out for 2 hours, and then the natural cooling is carried out to the room temperature under the atmosphere of inert gas, so as to obtain the ceramic catalytic filler loaded by alkali metal, and obtain the ceramic catalytic filler loaded by alkali metal.
The magnesium salt is magnesium acetate tetrahydrate.
The alkali metal hydroxide is NaOH.
Example eight
The alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is honeycomb porous ceramic filler.
The porous ceramic filler is ceramic balls.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing solution is 7, and finally drying for 12h in an oven at the temperature of 110 ℃;
2) adding Mg salt into deionized water to prepare an Mg salt solution with the mass percentage concentration of 8%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 8%;
3) immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 4 times, wherein the ultrasonic impregnation is carried out for 1.5h, the drying temperature is 110 ℃, the drying time is 12h, then heating to 550 ℃ at the heating rate of 5 ℃/min under the inert gas atmosphere, then carrying out constant-temperature calcination for 2h, and then naturally cooling to the room temperature under the inert gas atmosphere;
4) immersing the calcined porous ceramic filler in an alkali solution, and then ultrasonically immersing and drying for 4 times, wherein the ultrasonic immersing is performed for 1.5h, the drying temperature is 110 ℃, the drying time is 12h, then the temperature is increased to 550 ℃ at the temperature rising speed of 5 ℃/min under the atmosphere of inert gas, then the constant-temperature calcining is performed for 2h, and then the natural cooling is performed to the room temperature under the atmosphere of inert gas, so that the alkali metal loaded ceramic catalytic filler is obtained, and the alkali metal loaded ceramic catalytic filler is obtained.
The magnesium salt is magnesium acetate tetrahydrate.
The alkali metal hydroxide is NaOH.
Example nine
The alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is foam porous ceramic filler.
The porous ceramic filler is Raschig ring.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing solution is 7, and finally drying for 12h in an oven at the temperature of 110 ℃;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 10%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 10%;
3) immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 2 times, wherein the ultrasonic impregnation is carried out for 3 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then heating to 700 ℃ at the heating rate of 5 ℃/min under the inert gas atmosphere, then carrying out constant-temperature calcination for 2 hours, and then naturally cooling to the room temperature under the inert gas atmosphere;
4) immersing the calcined porous ceramic filler in an alkali solution, and then ultrasonically immersing and drying for 2 times, wherein the ultrasonic immersing is carried out for 3 hours, the drying temperature is 110 ℃, the drying time is 12 hours, then the temperature is raised to 700 ℃ at the temperature raising speed of 5 ℃/min under the atmosphere of inert gas, then the constant-temperature calcining is carried out for 2 hours, and then the natural cooling is carried out to the room temperature under the atmosphere of inert gas, so as to obtain the ceramic catalytic filler loaded by alkali metal, and obtain the ceramic catalytic filler loaded by alkali metal.
The magnesium salt is magnesium nitrate hexahydrate.
The alkali metal hydroxide is NaOH.
Example ten
The alkali metal loaded ceramic catalytic filler comprises a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
The porous ceramic filler is honeycomb porous ceramic filler.
The porous ceramic filler is pall ring.
The alkali metal-loaded ceramic catalytic filler is applied to an absorption tower for chemically absorbing carbon dioxide by organic amine.
The preparation method of the alkali metal loaded ceramic catalytic filler comprises the following steps:
1) removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing solution is 7, and finally drying for 12h in an oven at the temperature of 110 ℃;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 5%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 20%;
3) immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 4 times, wherein the ultrasonic impregnation is carried out for 1h, the drying temperature is 110 ℃, the drying time is 12h, then heating to 500 ℃ at the heating rate of 5 ℃/min under the inert gas atmosphere, then carrying out constant-temperature calcination for 2h, and then naturally cooling to room temperature under the inert gas atmosphere;
4) immersing the calcined porous ceramic filler in an alkali solution, and then ultrasonically immersing and drying for 4 times, wherein the ultrasonic immersing is performed for 1h, the drying temperature is 110 ℃, the drying time is 12h, then the temperature is increased to 500 ℃ at the temperature rising speed of 5 ℃/min under the atmosphere of inert gas, then the constant-temperature calcining is performed for 2h, and then the natural cooling is performed to the room temperature under the atmosphere of inert gas, so that the alkali metal loaded ceramic catalytic filler is obtained, and the alkali metal loaded ceramic catalytic filler is obtained.
The magnesium salt is magnesium acetate tetrahydrate.
The alkali metal hydroxide is KOH.
Claims (10)
1. An alkali metal supported ceramic catalytic filler comprising a porous ceramic filler and an active component attached to the porous ceramic filler, wherein the active component comprises alkali metal ions and magnesium oxide.
2. The alkali metal supported ceramic catalytic filler of claim 1, wherein the porous ceramic filler is a honeycomb porous ceramic filler or a foam porous ceramic filler.
3. The alkali metal-loaded ceramic catalytic filler according to claim 1, wherein the porous ceramic filler is a pall ring, a raschig ring, a ceramic ball or a corrugated plate.
4. The method of making an alkali metal-loaded ceramic catalytic filler according to claim 1, wherein the alkali metal-loaded ceramic catalytic filler is applied in an absorption column for the chemical absorption of carbon dioxide by organic amines.
5. A method of making an alkali metal supported ceramic catalytic filler as claimed in claim 1, comprising the steps of:
1) pretreating the porous ceramic filler;
2) adding Mg salt into deionized water to prepare a Mg salt solution with the mass percentage concentration of 5-20%; adding alkali metal hydroxide into deionized water to prepare an alkali solution with the mass percentage concentration of 5-20%;
3) immersing the porous ceramic filler in Mg salt solution, and then carrying out ultrasonic impregnation, drying, calcining and cooling;
4) immersing the porous ceramic filler treated in the step 3) in an alkali solution, and then carrying out ultrasonic impregnation, drying, calcining and cooling to obtain the alkali metal loaded ceramic catalytic filler.
6. The method of making an alkali metal supported ceramic catalytic filler as claimed in claim 5 wherein the magnesium salt is magnesium nitrate hexahydrate or magnesium acetate tetrahydrate.
7. The method of making an alkali metal supported ceramic catalytic filler according to claim 5, wherein the alkali metal hydroxide is NaOH or KOH.
8. The process for the preparation of an alkali metal supported ceramic catalytic filler according to claim 5, characterized in that the specific operating procedure of step 1) is:
removing impurities on the surface of the porous ceramic filler, cleaning the porous ceramic filler by adopting an oxalic acid solution with the mass percentage concentration of 30%, then condensing, refluxing and boiling for 1h, cooling, washing by using deionized water until the pH value of a washing liquid is 7, and finally drying for 12h in an oven at the temperature of 110 ℃.
9. The process for the preparation of an alkali metal supported ceramic catalytic filler according to claim 5, characterized in that the specific operating procedure of step 3) is:
immersing the porous ceramic filler in Mg salt solution, carrying out ultrasonic impregnation and drying for 2-4 times, wherein the ultrasonic impregnation is carried out for 1-3 h, the drying temperature is 110 ℃, the drying time is 12h, then heating to 500-fold at the heating rate of 5 ℃/min under the atmosphere of inert gas, calcining at constant temperature for 2h, and then naturally cooling to room temperature under the atmosphere of inert gas.
10. The process for the preparation of an alkali metal supported ceramic catalytic filler according to claim 5, characterized in that the specific operations of step 4) are:
immersing the calcined porous ceramic filler in an alkali solution, performing ultrasonic impregnation and drying for 2-4 times, wherein the ultrasonic impregnation is performed for 1-3 h, the drying temperature is 110 ℃, the drying time is 12h, then heating to 500-fold at the heating rate of 5 ℃/min under the atmosphere of inert gas, calcining at constant temperature for 2h, and then naturally cooling to room temperature under the atmosphere of inert gas to obtain the alkali metal loaded ceramic catalytic filler.
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Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5492878A (en) * | 1992-03-31 | 1996-02-20 | Mitsui Mining & Smelting Co., Ltd. | Catalyst for cleaning exhaust gas with alumina, ceria, zirconia, nickel oxide, alkaline earth oxide, and noble metal catalyst, and method for preparing |
CN1394678A (en) * | 2002-06-17 | 2003-02-05 | 中国科学院山西煤炭化学研究所 | Catalyst for synthesizing dimethyl carbonate and its preparation method |
CN102039202A (en) * | 2010-12-15 | 2011-05-04 | 东南大学 | Solid-base monolithic catalyst with regular porous channels and preparation method of solid-base monolithic catalyst |
CN102658023A (en) * | 2012-05-17 | 2012-09-12 | 东南大学 | Carbon dioxide solid absorbent capable of effectively inhibiting active components from losing effect |
CN102908979A (en) * | 2012-11-12 | 2013-02-06 | 江西理工大学 | Preparation method of efficient adsorbent porous magnesium oxide |
US20130108532A1 (en) * | 2010-03-30 | 2013-05-02 | University Of Regina | Catalytic method and apparatus for separating a gaseous component from an incoming gas stream |
CN103191638A (en) * | 2013-04-16 | 2013-07-10 | 浙江大学 | Novel desulfurizer packing material for seawater desulfurization and preparation method thereof |
KR20130131970A (en) * | 2012-05-25 | 2013-12-04 | 한국에너지기술연구원 | Solid carbon dioxide absorbent and elimination and concentration method of carbon dioxide using the absorbent |
CN103638895A (en) * | 2013-11-19 | 2014-03-19 | 苏州丹百利电子材料有限公司 | Preparation method of supported acid gas absorbent |
CN109592773A (en) * | 2018-12-12 | 2019-04-09 | 天津大学 | A method of degradation water body glyphosate |
-
2021
- 2021-06-29 CN CN202110730516.1A patent/CN113318698A/en active Pending
Patent Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5492878A (en) * | 1992-03-31 | 1996-02-20 | Mitsui Mining & Smelting Co., Ltd. | Catalyst for cleaning exhaust gas with alumina, ceria, zirconia, nickel oxide, alkaline earth oxide, and noble metal catalyst, and method for preparing |
CN1394678A (en) * | 2002-06-17 | 2003-02-05 | 中国科学院山西煤炭化学研究所 | Catalyst for synthesizing dimethyl carbonate and its preparation method |
US20130108532A1 (en) * | 2010-03-30 | 2013-05-02 | University Of Regina | Catalytic method and apparatus for separating a gaseous component from an incoming gas stream |
CN102039202A (en) * | 2010-12-15 | 2011-05-04 | 东南大学 | Solid-base monolithic catalyst with regular porous channels and preparation method of solid-base monolithic catalyst |
CN102658023A (en) * | 2012-05-17 | 2012-09-12 | 东南大学 | Carbon dioxide solid absorbent capable of effectively inhibiting active components from losing effect |
KR20130131970A (en) * | 2012-05-25 | 2013-12-04 | 한국에너지기술연구원 | Solid carbon dioxide absorbent and elimination and concentration method of carbon dioxide using the absorbent |
CN102908979A (en) * | 2012-11-12 | 2013-02-06 | 江西理工大学 | Preparation method of efficient adsorbent porous magnesium oxide |
CN103191638A (en) * | 2013-04-16 | 2013-07-10 | 浙江大学 | Novel desulfurizer packing material for seawater desulfurization and preparation method thereof |
CN103638895A (en) * | 2013-11-19 | 2014-03-19 | 苏州丹百利电子材料有限公司 | Preparation method of supported acid gas absorbent |
CN109592773A (en) * | 2018-12-12 | 2019-04-09 | 天津大学 | A method of degradation water body glyphosate |
Non-Patent Citations (1)
Title |
---|
成都科技大学《化工原理》编写组: "《化工原理(第二版)下册》", 30 June 1993, 成都科技大学出版社 * |
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