Background
The diesel vehicle has the advantages of high efficiency, heat utilization rate, low cost, strong engine horsepower, low carbon dioxide emission, wide application range and the like, is widely focused under the current situation that crude oil is increasingly exhausted and carbon dioxide emission requirements are gradually strict, and diesel oil is one of the trend directions of automobiles under the national energy-saving emission-reduction treatment policy, but the emission of the diesel vehicle also brings adverse effects to the treatment of the atmospheric environment and the health of residents in China. The components of pollutants in the tail gas discharged by the diesel vehicle are very complex, and the pollutants include soot particles, carbon monoxide, hydrocarbon, oxynitride and the like. Wherein, the carbon smoke particles are the pollutant which is the most harmful and difficult to eliminate, and the granularity range is 0.05-1 mu m. Because the particle diameter of carbon smoke particles in the tail gas of the diesel vehicle is smaller, particularly small particles with the particle diameter smaller than 2.5 mu m are not easy to be blocked by nasal cavity villus, and can directly enter bronchi after being inhaled into the lung, so that the gas exchange of the lung is affected, and a series of respiratory tract and cardiovascular diseases are caused. At the same time, soot particles are also an important factor in causing haze.
Currently, the air pollution control work attracts much attention in many countries, and the country is also beginning to apply to the treatment of air pollution. In order to meet the increasingly strict regulatory requirements, three main methods for solving the soot particle pollution of diesel vehicle emission are: firstly, the used fuel is improved or a novel environment-friendly alternative fuel is used; secondly, improving the engine of the diesel vehicle; and thirdly, an exhaust aftertreatment system is improved, and a tail gas purifying system is additionally arranged. The third method is generally considered to be most effective based on technical and economic considerations. In the actual exhaust gas aftertreatment technology, the technology of combining a solid particle catcher with a catalyst is the key point of current research, wherein the development of the catalyst with excellent performance is the core.
CN 107159231a discloses a preparation method of a monocrystal supported catalyst for eliminating soot particles of diesel vehicles at low temperature, which is prepared by immersing monocrystal alpha-phase manganese sesquioxide cubes in a metal salt solution, and the catalyst has the advantages of low cost, simple preparation method, convenience for industrialization, high catalytic activity and capability of well reducing the combustion temperature of soot particles of diesel vehicles. CN 103212414A discloses a preparation method of a supported silver catalyst for reducing the combustion temperature of soot particles, the catalyst comprises an active component and a carrier, the active component is silver, the carrier is cerium dioxide or cerium-based composite oxide, the silver loading is 1% -20% of the carrier mass, the catalyst has good oxidation activity in the combustion of soot particles, and the temperature of the soot particles in the combustion process can be reduced from 642 ℃ to 400 ℃ or so to reach the operating temperature range of a diesel engine. CN 106824161A discloses a preparation method of a micron sheet-shaped soot combustion catalyst, which is prepared by mixing a solution containing a cerium source or a lanthanum source with an alkaline solution, precipitating at low temperature, and calcining insoluble substances, wherein the catalyst has a micron sheet-shaped rare earth metal oxide catalyst which has good crystallization and does not contain any noble metal, and has a micron sheet-shaped morphology, can be in high-efficiency contact with carbon particles, has excellent catalytic oxidation activity, and has potential application prospects in the aspect of combustion degradation of solid pollutants.
Catalysts commonly used in the art for soot particle oxidation, such as: ceO (CeO) 2 Base compounds, perovskite oxides, noble metal based catalysts, etc., are disadvantageous for contact of active sites with carbon particles due to lack of pore structure, high cost of noble metals and easy toxicity, resulting in low catalyst activity and easy deactivation, which limits industrial application of catalysts for oxidation of soot particles.
Disclosure of Invention
In view of the defects of the prior art, the invention aims to provide a catalyst for removing soot particles of a diesel vehicle at a low temperature and a preparation method thereof. The catalyst has good effect on the catalytic oxidation of the soot particles under loose contact, can effectively convert the soot particles into carbon dioxide, and can remarkably reduce the temperature of the thermal oxidation of the soot particles.
In order to achieve the above object, the present invention provides a method for preparing a catalyst for removing soot particles of a diesel vehicle at a low temperature, comprising the steps of:
step 1: stirring the soluble metal salt and the ethanol water solution at the stirring rate of 300-500 r/min to form a solution I; adjusting the pH value of the solution I to 9.0-11.0 by using an alkaline aqueous solution, and continuously stirring for 0.5-2 h after adjusting the pH value to obtain a solution II; carrying out hydrothermal reaction on the solution II at 160-180 ℃ for 6-15 h, naturally cooling to 25-30 ℃, filtering insoluble substances, washing with ethanol and water three times respectively, and drying at 80-120 ℃ for 6-12 h to obtain solid powder;
step 2: dispersing the solid powder obtained in the step 1 in water, and forming a suspension a under the conditions that the ultrasonic power is 50-200W, the frequency is 20-130 kHz, the temperature is 20-40 ℃ and the ultrasonic treatment is carried out for 20-60 min; adding silver nitrate into a suspension a stirred at a stirring rate of 300-500 r/min, reacting for 0.5-2 h to obtain a suspension b, stopping stirring, transferring the suspension b to 90-120 ℃ and keeping for 12-18 h, evaporating the water of the suspension b, collecting solid matters, and calcining the solid matters at 400-600 ℃ for 2-5 h; the calcined solid matter is crushed and screened by a 300-500 mesh screen, and the powder under the screen is collected to obtain the catalyst for eliminating the soot particles of the diesel vehicle.
Preferably, the mass ratio of the soluble metal salt to the ethanol aqueous solution in the step 1 is 1: (30-50).
The soluble metal salt is soluble cobalt salt or soluble cerium salt; the soluble cobalt salt is one of cobalt nitrate hexahydrate (II), cobalt acetate tetrahydrate (II) and cobalt chloride hexahydrate (II); the soluble cerium salt is one of cerium (III) nitrate hexahydrate and cerium (III) chloride heptahydrate.
The mass fraction of the ethanol aqueous solution is 60-80%.
The alkaline aqueous solution is one of an aqueous ammonia solution, an aqueous sodium hydroxide solution, an aqueous sodium bicarbonate solution and an aqueous sodium carbonate solution which are 1-3 mol/L.
The catalytic oxidation performance of a single metal oxide catalyst on soot particles is primarily affected by the redox capacity of the metal oxide, the mobility of the surface active species, and the contact with the soot particles. Under general conditions, the catalytic combustion performance of a single metal oxide catalyst on the carbon soot particles is not obviously improved, the carbon soot particles can be effectively combusted only by reaching more than 500 ℃, and the selectivity of the catalytic combustion to form carbon dioxide is also not ideal. The composite metal oxide catalyst is a catalyst formed by compounding two or more metal elements, and the catalytic oxidation performance of the catalyst on soot particles is mainly related to the self-catalytic activity of the metal oxide and the synergistic catalytic effect among different components. Many studies have shown that composite metal oxides benefit from a one-component metal oxide to metal oxide phase change, enhanced oxygen species storage in the structure, and synergistic interaction between the components, which can significantly improve the catalytic combustion performance of the catalyst.
More preferably, the mass ratio of the soluble cobalt salt to the soluble cerium salt in the soluble metal salt in the step 1 is 1: (3-5).
Preferably, the mass ratio of the solid powder to the water in the step 2 is (0.02-0.05): 1, a step of; the mass ratio of the added silver nitrate to the solid powder is (1:10) - (1:30).
The catalytic properties of metal oxides are largely dependent on their structure. In the process of preparing metal oxide by using water heating or solvent heating, the structure regulating substance in the precursor solution can be used for preparing metal oxides with various morphologies. Surfactants are the most commonly used structure-modifying substances. However, surfactants are difficult to remove, and some surfactants with specific functions are expensive. The low molecular sugar can generate polymerization reaction under the temperature and pressure of hydrothermal or solvothermal to generate oligomer, and the oligomer has structure regulation and control effect on metal ions in a liquid phase environment. Therefore, sugar is added into the metal precursor solution, and the formed metal oxidation structure can be regulated and controlled under certain reaction conditions.
Some low-molecular nitrogen-containing substances have strong coordination to metal ions in a liquid phase environment, can regulate and control the growth rate and direction of crystal nuclei of early-formed metal oxide precursors, and can also play a role in regulating and controlling the structure of metal oxidation.
Further preferably, the preparation method of the catalyst for removing soot particles of the diesel vehicle at low temperature comprises the following steps:
step 1: stirring a soluble cobalt salt, a soluble cerium salt, sugar and ethanol water solution at a stirring rate of 300-500 r/min to form a solution I; adjusting the pH value of the solution I to 9.0-11.0 by using an alkaline aqueous solution, adding a nitrogen-containing substance after adjusting the pH value, and continuously stirring for 0.5-2 h to obtain a solution II; and carrying out hydrothermal reaction on the solution II for 6-15 h at 160-180 ℃, naturally cooling to 25-30 ℃, filtering insoluble substances, washing with ethanol and water three times respectively, and drying at 80-120 ℃ for 6-12 h to obtain solid powder.
Step 2: dispersing the solid powder obtained in the step 1 in water, and forming a suspension a under the conditions that the ultrasonic power is 50-200W, the frequency is 20-130 kHz, the temperature is 20-40 ℃ and the ultrasonic treatment is carried out for 20-60 min; adding silver nitrate into a suspension a stirred at a stirring rate of 300-500 r/min, reacting for 0.5-2 h to obtain a suspension b, stopping stirring, keeping the suspension b at 90-120 ℃ for 12-18 h, evaporating the water of the suspension b, collecting solid matters, and calcining the solid matters at 400-600 ℃ for 2-5 h; the calcined solid matter is crushed and screened by a 300-500 mesh screen, and the powder under the screen is collected to obtain the catalyst for eliminating the soot particles of the diesel vehicle.
Preferably, the mass ratio of the soluble cerium salt, the soluble cobalt salt, the soluble cerium salt sugar and the ethanol aqueous solution added in the step 1 is (0.2-2): (0.2-2): (0.1-0.5): (30-50).
The soluble cobalt salt is one of cobalt nitrate hexahydrate (II), cobalt acetate tetrahydrate (II) and cobalt chloride hexahydrate (II), and the soluble cerium salt is one of cerium nitrate hexahydrate (III) and cerium chloride heptahydrate (III).
The sugar is one or a combination of two or more of glucose, sucrose and lactose.
The mass fraction of the ethanol aqueous solution is 60-80%.
The alkaline aqueous solution is one of an aqueous ammonia solution, an aqueous sodium hydroxide solution, an aqueous sodium bicarbonate solution and an aqueous sodium carbonate solution which are 1-3 mol/L.
The mass ratio of the nitrogen-containing substance to the soluble metal salt is (2-5): 1, a step of; the nitrogen-containing substance is one or the combination of two or more of hexamethylenetetramine, urea, glycine, ethylenediamine, hexamethyldisilazane and tetramethyl divinyl disilazane.
Preferably, the mass ratio of the solid powder to the water in the step 2 is (0.02-0.05): 1, a step of; the mass ratio of the added silver nitrate to the solid powder is (1:10) - (1:30).
The invention has the beneficial effects that:
(1) The preparation method prepares the structured cerium cobalt oxide precursor through simple hydrothermal reaction, impregnates silver nitrate, then calcines the precursor, successfully anchors silver species on the surface of the structured cerium cobalt oxide, successfully prepares the catalyst for removing soot particles of diesel vehicles at low temperature, has simple preparation process, easily obtained raw materials, no toxicity or low toxicity, and is suitable for industrial scale-up production.
(2) The carbon smoke particle catalyst prepared by the invention can effectively convert carbon smoke particles into carbon dioxide for simulating the catalysis of the carbon smoke particles of the tail gas of the diesel vehicle; based on the synergistic effect of structured cerium oxide, cobaltosic oxide and silver, the catalyst prepared by the invention has high catalytic activity on the carbon smoke particles under the conditions of loose contact state with the carbon smoke particles and no existence of nitrogen oxides; and can reduce the combustion temperature of the soot particles to 325 ℃.
Detailed Description
The present invention will be further described in detail with reference to the following specific examples in order to make the objects, technical solutions and advantages of the present invention more apparent. It should be understood that the specific embodiments described herein are for purposes of illustration only and are not intended to limit the scope of the invention. In addition, the technical features of the embodiments of the present invention described below may be combined with each other as long as they do not collide with each other.
Example 1A method for preparing a soot particulate catalyst
(1) 3.5g of cobalt nitrate hexahydrate is dissolved in 100g of ethanol aqueous solution with the mass fraction of 70% at the stirring rate of 300r/min to form solution I; adjusting the pH value of the solution I to 9.5 by using 2mol/L aqueous ammonia solution, and continuously stirring for 1h at a stirring rate of 300r/min to form a solution II; transferring the solution II to a polytetrafluoroethylene liner, loading into a stainless steel reaction kettle, placing the reaction kettle at 180 ℃ for reaction for 8 hours, naturally cooling to 25 ℃, filtering insoluble substances, washing with ethanol and water three times respectively, and drying at 80 ℃ in a constant temperature oven for 6 hours to obtain solid powder;
(2) Dispersing 5g of the solid powder obtained in the step 1 in a beaker containing 100g of water, and carrying out ultrasonic treatment for 30min at the ultrasonic power of 100W, the frequency of 50kHz and the temperature of 25 ℃ to obtain a suspension a; dissolving 0.2g of silver nitrate in a suspension a stirred at a stirring rate of 300r/min, stirring and reacting for 1h to obtain a suspension b, stopping stirring, transferring a beaker containing the suspension b to a constant temperature oven, drying at 120 ℃ for 12h, evaporating the moisture of the suspension b, collecting the residual solid matters, and placing the solid matters under a muffle furnace at 550 ℃ for calcination for 2h; crushing the calcined solid material, sieving with a 300-mesh sieve, and collecting powder under the sieve to obtain silver-doped tricobalt tetraoxide, namely the catalyst prepared in the embodiment.
Example 2A method for preparing a soot particulate catalyst
(1) 3.5g of cerium nitrate hexahydrate is dissolved in 100g of ethanol aqueous solution with the mass fraction of 70% at the stirring rate of 300r/min to form a solution I; adjusting the pH value of the solution I to 9.5 by using 2mol/L aqueous ammonia solution, and continuously stirring for 1h at a stirring rate of 300r/min to form a solution II; transferring the solution II to a polytetrafluoroethylene liner, loading into a stainless steel reaction kettle, placing the reaction kettle at 180 ℃ for reaction for 8 hours, naturally cooling to 25 ℃, filtering insoluble substances, washing with ethanol and water three times respectively, and drying at 80 ℃ in a constant temperature oven for 6 hours to obtain solid powder;
(2) Dispersing 5g of the solid powder obtained in the step 1 in a beaker containing 100g of water, and carrying out ultrasonic treatment for 30min at the ultrasonic power of 100W, the frequency of 50kHz and the temperature of 25 ℃ to obtain a suspension a; dissolving 0.2g of silver nitrate in a suspension a stirred at a stirring rate of 300r/min, stirring and reacting for 1h to obtain a suspension b, stopping stirring, transferring a beaker containing the suspension b to a constant temperature oven, drying at 120 ℃ for 12h, evaporating the moisture of the suspension b, collecting the residual solid matters, and placing the solid matters under a muffle furnace at 550 ℃ for calcination for 2h; and (3) crushing the calcined solid matters, sieving with a 300-mesh sieve, and collecting powder under the sieve to obtain silver-doped cerium oxide, namely the catalyst prepared in the embodiment.
Example 3A method for preparing a soot particulate catalyst
(1) 2.8g of cerium nitrate hexahydrate and 0.7g of cobalt nitrate hexahydrate are dissolved in 100g of ethanol aqueous solution with the mass fraction of 70% at the stirring rate of 300r/min to form a solution I; adjusting the pH value of the solution I to 9.5 by using 2mol/L aqueous ammonia solution, and continuously stirring for 1h at a stirring rate of 300r/min to form a solution II; transferring the solution II to a polytetrafluoroethylene liner, loading into a stainless steel reaction kettle, placing the reaction kettle at 180 ℃ for reaction for 8 hours, naturally cooling to 25 ℃, filtering insoluble substances, washing with ethanol and water three times respectively, and drying at 80 ℃ in a constant temperature oven for 6 hours to obtain solid powder;
(2) Dispersing 5g of the solid powder obtained in the step 1 in a beaker containing 100g of water, and carrying out ultrasonic treatment for 30min at the ultrasonic power of 100W, the frequency of 50kHz and the temperature of 25 ℃ to obtain a suspension a; dissolving 0.2g of silver nitrate in a suspension a stirred at a stirring rate of 300r/min, stirring and reacting for 1h to obtain a suspension b, stopping stirring, transferring a beaker containing the suspension b to a constant temperature oven, drying at 120 ℃ for 12h, evaporating the moisture of the suspension b, collecting the residual solid matters, and placing the solid matters under a muffle furnace at 550 ℃ for calcination for 2h; crushing the calcined solid material, sieving with a 300-mesh sieve, and collecting powder under the sieve to obtain the silver-doped cobalt-cerium bimetallic oxide, namely the catalyst prepared in the embodiment.
Example 4A method for preparing a soot particulate catalyst
(1) 2.8g of cerium nitrate hexahydrate, 0.7g of cobalt nitrate hexahydrate and 1g of glucose are dissolved in 100g of ethanol aqueous solution with the mass fraction of 70% under the stirring rate of 300r/min to form a solution I; adjusting the pH value of the solution I to 9.5 by using 2mol/L aqueous ammonia solution, and continuously stirring for 1h at a stirring rate of 300r/min to form a solution II; transferring the solution II to a polytetrafluoroethylene liner, loading into a stainless steel reaction kettle, placing the reaction kettle at 180 ℃ for reaction for 8 hours, naturally cooling to 25 ℃, filtering insoluble substances, washing with ethanol and water three times respectively, and drying at 80 ℃ in a constant temperature oven for 6 hours to obtain solid powder;
(2) Dispersing 5g of the solid powder obtained in the step 1 in a beaker containing 100g of water, and carrying out ultrasonic treatment for 30min at the ultrasonic power of 100W, the frequency of 50kHz and the temperature of 25 ℃ to obtain a suspension a; dissolving 0.2g of silver nitrate in a suspension a stirred at a stirring rate of 300r/min, stirring and reacting for 1h to obtain a suspension b, stopping stirring, transferring a beaker containing the suspension b to a constant temperature oven, drying at 120 ℃ for 12h, evaporating the moisture of the suspension b, collecting the residual solid matters, and placing the solid matters under a muffle furnace at 550 ℃ for calcination for 2h; crushing the calcined solid material, sieving with a 300-mesh sieve, and collecting powder under the sieve to obtain the flaky silver cobalt-doped cerium bimetallic oxide, namely the catalyst prepared in the embodiment.
Example 5A method for preparing a soot particulate catalyst
(1) 2.8g of cerium nitrate hexahydrate and 0.7g of cobalt nitrate hexahydrate are dissolved in 100g of ethanol aqueous solution with the mass fraction of 70% at the stirring rate of 300r/min to form a solution I; adjusting the pH of the solution I to 9.5 by using 2mol/L aqueous ammonia solution, adding 8g of tetramethyl divinyl disilazane, and continuously stirring at a stirring rate of 300r/min for 1h to form a solution II; transferring the solution II to a polytetrafluoroethylene liner, loading into a stainless steel reaction kettle, placing the reaction kettle at 180 ℃ for reaction for 8 hours, naturally cooling to 25 ℃, filtering insoluble substances, washing with ethanol and water three times respectively, and drying at 80 ℃ in a constant temperature oven for 6 hours to obtain solid powder;
(2) Dispersing 5g of the solid powder obtained in the step 1 in a beaker containing 100g of water, and carrying out ultrasonic treatment for 30min at the ultrasonic power of 100W, the frequency of 50kHz and the temperature of 25 ℃ to obtain a suspension a; dissolving 0.2g of silver nitrate in a suspension a stirred at a stirring rate of 300r/min, stirring and reacting for 1h to obtain a suspension b, stopping stirring, transferring a beaker containing the suspension b to a constant temperature oven, drying at 120 ℃ for 12h, evaporating the moisture of the suspension b, collecting the residual solid matters, and placing the solid matters under a muffle furnace at 550 ℃ for calcination for 2h; crushing the calcined solid material, sieving with a 300-mesh sieve, and collecting powder under the sieve to obtain the flaky silver cobalt-doped cerium bimetallic oxide, namely the catalyst prepared in the embodiment.
Example 6 preparation of a soot particulate catalyst
(1) 2.8g of cerium nitrate hexahydrate, 0.7g of cobalt nitrate hexahydrate and 1g of glucose are dissolved in 100g of ethanol aqueous solution with the mass fraction of 70% under the stirring rate of 300r/min to form a solution I; adjusting the pH of the solution I to 9.5 by using 2mol/L aqueous ammonia solution, adding 8g of tetramethyl divinyl disilazane, and continuously stirring at a stirring rate of 300r/min for 1h to form a solution II; transferring the solution II to a polytetrafluoroethylene liner, loading into a stainless steel reaction kettle, placing the reaction kettle at 180 ℃ for reaction for 8 hours, naturally cooling to 25 ℃, filtering insoluble substances, washing with ethanol and water three times respectively, and drying at 80 ℃ in a constant temperature oven for 6 hours to obtain solid powder;
(2) Dispersing 5g of the solid powder obtained in the step 1 in a beaker containing 100g of water, and carrying out ultrasonic treatment for 30min at the ultrasonic power of 100W, the frequency of 50kHz and the temperature of 25 ℃ to obtain a suspension a; dissolving 0.2g of silver nitrate in a suspension a stirred at a stirring rate of 300r/min, stirring and reacting for 1h to obtain a suspension b, stopping stirring, transferring a beaker containing the suspension b to a constant temperature oven, drying at 120 ℃ for 12h, evaporating the moisture of the suspension b, collecting the residual solid matters, and placing the solid matters under a muffle furnace at 550 ℃ for calcination for 2h; and (3) crushing the calcined solid matters, sieving with a 300-mesh sieve, and collecting powder under the sieve to obtain the silver cobalt-cerium doped bimetallic oxide with the three-dimensional interconnected porous structure, namely the catalyst prepared in the embodiment.
Test example 1 morphology of catalyst
The catalysts prepared in example 3, example 4, example 5 and example 6 were characterized by scanning electron microscopy, and the results are shown in fig. 1.
For example 3, example 4, implementationThe catalysts prepared in example 5 and example 6 were tested for specific surface area and pore structure. The specific surface area was calculated using Brunauer-Emmett-Teller (BET) model, and the pore size (D) was calculated using Barren-Joyner-Halenda (BJH) model p ) Distribution. The results are shown in Table 1.
TABLE 1 results of specific surface area test
|
BET specific surface area (m) 2 /g)
|
D p (nm)
|
Example 3
|
68.7
|
12.8
|
Example 4
|
83.6
|
14.6
|
Example 5
|
98.1
|
18.3
|
Example 6
|
127.3
|
25.6 |
It can be seen from fig. 1 that example 3, in which glucose and tetramethyl divinyl disilazane were not added, exhibited a lump shape; example 4, prepared with the addition of glucose, and example 5, prepared with the addition of tetramethyl divinyl disilazane, exhibited a distinct lamellar structure. This is because under hydrothermal conditions, the coordination attraction of the oligomer formed by polymerization of glucose and tetramethyl divinyl disilazane mediates the nucleation and growth of the metal oxide precursor in the planar direction. In addition, example 6, prepared by adding glucose and tetramethyl divinyl disilazane, exhibited a distinct three-dimensional interconnected porous structure with distinct macropores (> 50 nm) present. This suggests that glucose and tetramethyl divinyl disilazane have a synergistic modulating effect on the structure of the complex metal oxide. It is possible that the polymerization of glucose into oligomer at high temperature has an adjusting effect on the structure of the metal oxide precursor, and the crystal nucleus of the metal oxide precursor can be polymerized into a sheet shape and continuously grow, and the sheet-shaped metal oxide precursor is formed after the hydrothermal reaction is finished; the addition of the tetramethyl divinyl disilazane enables the metal oxide precursor crystal nucleus to grow rapidly along with the layered structure coordinated by the alcohol and the metal ions, the flaky structure further grows along with the reaction, the three-dimensional porous structured metal oxide precursor is formed through self-assembly polymerization, and the silver-doped three-dimensional porous structured metal oxide catalyst is prepared through final calcination treatment.
The specific surface area test is consistent with the scanning electron microscope test result, and the specific surface area and the pore size distribution of the catalyst are improved by adding glucose and tetramethyl divinyl disilazane. Example 6 the unique three-dimensional interconnected porous structure can accommodate more soot particles, provide more active sites, and may be more suitable for catalytic combustion of soot particles.
Test example 2 catalytic Activity of the catalyst
The catalytic activity evaluation of the catalyst is carried out by a temperature programming oxidation technology, a tubular heating furnace is utilized for temperature programming, oxygen, nitric oxide, water vapor and nitrogen are continuously introduced into the reactor, and the gas at the outlet is tested by a Fourier infrared spectrum gas tester.
Mixing 5mg of carbon smoke particles with 50mg of catalyst to form loose contact, diluting the mixed sample with 100mg of inert silicon dioxide, and placing the diluted sample into a quartz tube with the inner diameter of 10 mm; and placing the quartz tube in a temperature programming oxidation reactor, and carrying out temperature programming and reaction temperature control through a tubular electric heating furnace in the reactor. The temperature range of the temperature programming experiment is 50-650 ℃, the temperature increasing rate is 2.5 ℃/min, and the temperature is maintained for 30min after reaching the target temperature. The catalytic tests of the soot particles were carried out in 2 different atmospheres, respectively, (1) 10% oxygen, 10% water vapor, nitrogen balance gas, total gas flow 100mL/min, (2) 1000ppm nitric oxide, 10% water vapor, 10% oxygen and nitrogen balance gas, total gas flow 100mL/min.
The combustion process of the soot particles was monitored using an on-line mass spectrum, with an m/z=44 signal for monitoring the amount of carbon dioxide and an m/z=28 signal for monitoring the amount of carbon monoxide. The selectivity of catalytic oxidation of soot particles to carbon dioxide is determined by the following equation:
in the middle ofAnd C CO The carbon dioxide concentration and the carbon monoxide concentration of the outlet are respectively; />Indicating the selectivity to carbon dioxide.
The activity evaluation indexes of the catalyst for catalyzing the combustion of the particulate matters are as follows: the selectivity of carbon dioxide; the reaction temperatures at which the soot particle conversion rates were 10%, 50% and 90%, respectively, are denoted as T 10 、T 50 、T 90 。
The results of the catalytic combustion of soot particles by the catalysts prepared in the examples of the present invention are shown in table 1 below.
TABLE 1 results of catalyst performance under an atmosphere of 10% oxygen, 10% steam and nitrogen balance
As can be seen from the results of examples 1 to 3, the catalytic combustion performance of the soot particles of the silver-doped ceria catalyst is better than that of the silver-doped tricobalt tetraoxide catalyst, and the selectivity of the two catalysts for oxidizing combustion of the soot particles to carbon dioxide is not ideal; and the selectivity of carbon dioxide of the silver-doped cobalt-cerium bimetallic oxide catalyst prepared in the embodiment 3 is obviously improved, and the temperature of carbon smoke oxidation combustion is also obviously reduced. This is probably because cobalt is successfully incorporated into the unit cell structure of ceria and forms a solid solution, reducing the grain size of ceria; the introduction of cobalt also increases oxygen vacancies and defects of the ceria crystals, increasing the reactive sites.
From the test results of examples 3-6, it can be seen that the addition of glucose and tetramethyl divinyl disilazane during the preparation process increases the performance of the catalyst and decreases the temperature required for combustion of the soot particles. This is probably because the polymerization of glucose into oligomer at high temperature has an adjusting effect on the structure of the metal oxide precursor, and the crystal nucleus of the metal oxide precursor can be polymerized into a sheet shape and continuously grow, and the sheet-shaped metal oxide precursor is formed after the hydrothermal reaction is finished; the addition of the tetramethyl divinyl disilazane enables the metal oxide precursor crystal nucleus to grow rapidly along with the layered structure coordinated by the alcohol and the metal ions, the flaky structure further grows along with the reaction, the three-dimensional porous structured metal oxide precursor is formed through self-assembly polymerization, and the silver-doped three-dimensional porous structured metal oxide catalyst is prepared through final calcination treatment. Such a three-dimensional porous structure facilitates adsorption of soot particles on the catalyst surface and further promotes the progress of the catalytic reaction.
In order to further approach the practical use environment, the catalyst prepared in the embodiment of the invention is subjected to catalytic test under the conditions of 1000ppm of nitric oxide, 10% of water vapor, 10% of oxygen and nitrogen balance gas and total gas flow of 100mL/min, and the results are shown in Table 2. It can be seen that the presence of nitric oxide enhances the performance of the catalyst, since part of the nitric oxide is oxidized by the catalyst to nitrogen dioxide, which has a stronger catalytic capacity than oxygen, enhancing the oxidation of the soot particles. These results also demonstrate that example 6 of the present invention has good catalytic performance for simulating the oxidative combustion of soot particles in diesel exhaust, and can effectively convert soot particles to carbon dioxide at about 400 ℃.
TABLE 2 Performance results of catalysts under an atmosphere of 1000ppm nitric oxide, 10% steam, 10% oxygen, nitrogen balance