Background
Air pollution, especially indoor air pollution, poses serious harm to human bodies, and 60% of human diseases are reported to be caused by air pollution. The use of interior decoration, daily chemicals and human activities produce a large amount of pollutants, such as formaldehyde, benzene series, ammonia, etc. Formaldehyde is one of volatile organic compounds, and has strong stimulating effects on eye mucosa, nose and upper respiratory tract, and can cause allergic asthma and bronchitis, and in addition, formaldehyde has toxicity on the nervous system, liver, kidney and digestive system of human body. Eliminating formaldehyde pollution, purifying indoor air and being very important to human health.
The existing indoor air purification mainly adopts filtration and adsorption. The filtration mainly removes suspended matters in the air, such as dust, smoke and the like. Volatile Organic Compounds (VOC) in the air can be removed only by adsorption, but the adsorption only transfers the organic compounds in the air to the adsorbent and does not eliminate the organic compounds, and the adsorption performance is reduced along with the increase of the adsorption quantity, and finally the volatile organic compounds tend to be saturated and lose the air purification capacity. The photocatalysis can eliminate pollutants in the air, particularly can effectively degrade volatile organic compounds in the air, is a new air purification method developed in recent years, and the reaction is carried out at normal temperature and normal pressure, so that the organic compounds can be degraded into water and carbon dioxide, and secondary pollution can not be generated.
The activated carbon has the characteristics of large specific surface area, high adsorption rate, moderate pore size distribution and the like, and has remarkable advantages in the aspects of adsorbing and separating formaldehyde pollutants. According to different adsorption modes, activated carbon adsorption is divided into physical adsorption and chemical adsorption. In the physical adsorption process, the gradient distribution of the pore diameters determines the adsorption capacity and the adsorption rate, the macropores and the mesopores play a role in conveying formaldehyde molecules, the micropores have huge specific surface area and can provide enough stay places for pollutants, and the surfaces of the activated carbon adsorb the formaldehyde molecules by utilizing Van der Waals force generated under the action of asymmetric dipole moment. The chemical adsorption is that functional groups such as carboxyl, phenolic hydroxyl and the like of the activated carbon and formaldehyde adsorbate molecules are subjected to chemical reaction, so that the adsorption is stable and irreversible. As known from the physical adsorption and chemical adsorption processes of activated carbon, the pore size distribution and surface functional groups of activated carbon are very important for the adsorbate adsorption process.
CN114315236A discloses a method for preparing porous block aerogel for adsorbing and degrading VOCs gas by 3D printing technology. Uniformly mixing isopropanol, polydimethylsiloxane and hydroxypropyl methyl cellulose, adding silicon dioxide aerogel powder and titanium dioxide photocatalytic powder, and preparing 3D printing slurry by ball milling and mixing; then preparing the material into a macroscopic porous 3D printing aerogel sample with a specific structure by using a direct-writing 3D printer; then aging at normal temperature, and drying at proper temperature to remove organic solvent and further crosslink and solidify the binder to provide certain mechanical strength; and finally, carrying out heat treatment on the mixture in an electric furnace to obtain the 3D printing silica aerogel for absorbing and degrading the VOCs. The adsorption performance of the 3D printing silica aerogel on VOCs represented by formaldehyde and toluene is higher than that of commercial activated carbon by more than 20%, the absorption rate can reach 100%, and the degradation rate can reach more than 25%.
CN113181767A discloses a capsule type slow-release formaldehyde scavenger and a preparation process thereof, belonging to the technical field of formaldehyde scavenging, comprising a slow-release carrier pill core and a coating capsule, which are prepared from the following raw materials in parts by mass: 40-70 parts of active carbon base material, 30-60 parts of titanium dioxide base material, 5-10 parts of forming material, 2-20 parts of slow release material, 1-5 parts of plasticizer and 0.5-1.5 parts of anti-sticking agent, wherein the capsule coated with the thin coat is a polytetrafluoroethylene breathable waterproof thin coat, and the preparation process comprises the steps of matrix preparation, material mixing, granulation, slow release liquid preparation and coating. Through mixing titanium dioxide oxide in the active carbon matrix, fuse the back with active carbon and forming material and slow release material, the slow release capsule can carry out lasting absorption purification to formaldehyde under photocatalysis, and the surface film can completely cut off outside steam and soak, improves slowly-releasing efficiency, is showing extension coating standing time, satisfies the continuous purification ability to formaldehyde.
CN113101961A discloses a load Ag/C3N4Active carbon composite material of nano particles, melamine and silver nitrate are mixed and pyrolyzed to prepare Ag/g-C3N4Nanoparticles and thenCompounding with porous active carbon material to obtain Ag/C load 3N4The active carbon composite material of nano particles takes porous active carbon as a carrier and uniformly loads Ag/g-C3N4Nanoparticles of Ag/g-C3N4The nanoparticles have excellent photochemical activity, can generate more photogenerated carriers under light irradiation, and g-C3N4The Ag doped with the matrix has excellent conductivity, and can promote the transfer of photogenerated electrons, promote the separation of the photogenerated electrons and holes and ensure that Ag/g-C3N4The nano particles show better photocatalytic activity, and have good functions of adsorbing and photodegrading formaldehyde and excellent photocatalytic antibacterial activity on bacteria and microorganisms such as escherichia coli by being combined with the porous activated carbon.
CN111514883A discloses a carbon-based catalyst for decomposing indoor formaldehyde at room temperature and a preparation method thereof, which takes molded active carbon as a carrier, uses equal volume of impregnation to load a catalytic component, and obtains a formaldehyde elimination catalyst after high-temperature calcination. The carbon-based catalyst can efficiently purify formaldehyde at room temperature, the prepared titanium dioxide-containing catalyst has the performance of removing formaldehyde by photocatalysis and catalytic oxidation, and the formaldehyde purification efficiency is improved by combining the adsorption effect of activated carbon, the oxidation effect of manganese oxide and the photocatalysis effect of titanium dioxide. And the preparation process does not use noble metals, has the characteristics of high efficiency and environmental protection, and simultaneously uses the molded active carbon to purify formaldehyde, thereby being convenient for recycling and having no secondary pollution.
In view of the above, although the prior art can effectively remove formaldehyde by combining an adsorbent with an oxidant or a photocatalyst, the above adsorbent is still not strong enough in treatment capacity and has a long removal period for low-concentration formaldehyde, and thus there is an urgent need to develop a new formaldehyde adsorbent having excellent removal capacity for formaldehyde.
Disclosure of Invention
The invention aims to solve the technical problems of overcoming the defects and shortcomings in the prior art and provides a formaldehyde adsorbent for air purification and a preparation method and application thereof. The preparation method comprises the following steps: preparing phenolic resin ethanol solution, carrying out thermal polymerization and carbonization to obtain mesoporous carbon containing manganese and copper, and then carrying out oxidation treatment to obtain oxidized mesoporous carbon; dissolving a cobalt source in deionized water, adding oxidized mesoporous carbon, uniformly stirring to obtain a mixture solution, adding 2-methylimidazole, iron salt and zinc salt into the mixture solution, stirring, filtering, washing, drying, and roasting in an inert atmosphere to obtain the methanol adsorbent. The formaldehyde adsorbent prepared by the invention has excellent adsorption and removal capacity on formaldehyde, and can oxidize the formaldehyde under the illumination condition, thereby effectively removing the formaldehyde in the air.
The invention aims to provide a preparation method of a formaldehyde adsorbent for air purification.
The invention also aims to provide a formaldehyde adsorbent for air purification and application thereof.
The above purpose of the invention is realized by the following technical scheme:
a method for preparing a formaldehyde adsorbent for air purification, the method comprising the steps of:
(1) preparation of mesoporous carbon
Dissolving phenol and formaldehyde in an alkaline solution, stirring uniformly at a certain temperature, cooling to room temperature, adjusting the solution to be neutral by hydrochloric acid, removing moisture at a certain temperature under a vacuum condition, and dissolving the obtained phenolic resin in ethanol to prepare a phenolic resin ethanol solution; dissolving the triblock copolymer, manganese salt and copper salt in a phenolic resin mixed solution, evaporating at room temperature, and performing thermal polymerization to obtain a precursor; roasting and carbonizing the precursor to obtain a mesoporous carbon material;
(2) adding the mesoporous carbon obtained in the step (1) into an oxidant solution for oxidation treatment, and then filtering and washing to obtain oxidized mesoporous carbon;
(3) dissolving a cobalt source in deionized water, adding the mesoporous carbon obtained in the step (2), uniformly stirring to obtain a mixture solution, adding 2-methylimidazole, iron salt and zinc salt into the mixture solution, stirring, filtering, washing, drying, and roasting in an inert atmosphere to obtain the methanol adsorbent.
Preferably, in the step (1), the stirring temperature is 50-70 ℃; the temperature of the vacuum is 80-100 ℃, and the concentration of the phenolic resin ethanol solution is 20-30 wt%.
Preferably, in the step (1), the temperature of the thermal polymerization is 70-90 ℃, and the time of the thermal polymerization is 16-24 h; the roasting condition is that the temperature is raised to 750-850 ℃ at the heating rate of 4-8 ℃/min under inert gas for roasting carbonization, and the temperature is kept for 2-5 h.
Preferably, in step (1), the triblock copolymer is at least one of P123, F127; the alkaline solution is at least one of sodium hydroxide solution and potassium hydroxide solution; the inert gas is one of helium and argon; the manganese salt is at least one of manganese nitrate, manganese acetate and manganese chloride, and the copper salt is at least one of copper nitrate, copper acetate and copper chloride.
Preferably, in step (1), the molar ratio of phenol to formaldehyde is 1: 2-4; the ratio of the phenol to the triblock copolymer to the manganese salt to the copper salt is 10-14 mmol: 1 g: 0.2-0.4 mmol: 0.2 to 0.4 mmol.
Preferably, in the step (2), the oxidant is potassium permanganate or hydrogen peroxide, and the oxidation treatment condition is that the potassium permanganate or hydrogen peroxide is treated in 2mol/L potassium permanganate or hydrogen peroxide for 0.5-1.5 h.
Preferably, in the step (3), the stirring condition is that the mixture is stirred for 16-22 hours at the temperature of 20-30 ℃; the drying is drying treatment at 80-120 ℃ for 10-14 h; the calcination temperature is 450-550 ℃, and the treatment is carried out for 2-4 h; the ratio of the mesoporous carbon to the cobalt source is 1 g: 0.01-0.03 mol, wherein the molar ratio of the cobalt source to the 2-methylimidazole is 1: 4-8; the molar ratio of the cobalt source to the iron salt to the zinc salt is 1: 0.02-0.06.
Preferably, in the step (3), the inert atmosphere is one of nitrogen, argon and helium; the cobalt salt is at least one of cobalt nitrate, cobalt acetate and cobalt chloride, the ferric salt is at least one of ferric nitrate, ferric acetate and ferric chloride, and the zinc salt is at least one of zinc acetate, zinc chloride and zinc nitrate.
The formaldehyde adsorbent for air purification is prepared based on the preparation method of the formaldehyde adsorbent for air purification.
The application of the formaldehyde adsorbent for air purification is characterized in that the formaldehyde adsorbent is used for purifying formaldehyde in air.
The invention has the following beneficial effects:
(1) the modified mesoporous carbon material has excellent adsorption capacity on formaldehyde, can effectively remove the adsorbed formaldehyde due to the existence of metal, and further has excellent purification capacity on formaldehyde.
(2) The mesoporous carbon modified by manganese and copper can obviously modify the adsorption capacity of the mesoporous carbon, and has excellent catalytic oxidation capacity on formaldehyde due to the existence of manganese and copper.
(3) By oxidizing the mesoporous carbon, oxygen-containing groups on the surface of the mesoporous carbon can be increased, which is beneficial to the adsorption of cobalt, and further improves the dispersibility of the cobalt and the purification capacity of formaldehyde.
(4) Iron and zinc are added in the prepared metal framework, and the generated metal oxide formaldehyde has excellent photocatalytic degradation capability after modification and carbonization of the iron and the zinc, so that the formaldehyde purification capability is further improved.
Detailed Description
The present invention will be further described with reference to the following specific examples, which are not intended to limit the invention in any manner. The reagents, methods and apparatus employed in the present invention are conventional in the art, except as otherwise indicated.
Unless otherwise indicated, reagents and materials used in the following examples are commercially available.
Example 1
A method for preparing a formaldehyde adsorbent for air purification, the method comprising the steps of:
(1) preparation of mesoporous carbon
Dissolving 12mmol of phenol and 36mmol of formaldehyde in 10mL0.6mol/L sodium hydroxide solution, uniformly stirring at 60 ℃, cooling to room temperature, adjusting the solution to be neutral by hydrochloric acid, removing moisture under the vacuum condition of 90 ℃, and dissolving the obtained phenolic resin in ethanol to prepare 35 wt% phenolic resin ethanol solution; dissolving 1g P123, 0.3mmol of manganese nitrate and 0.3mmol of copper nitrate in a phenolic resin mixed solution, evaporating at room temperature, carrying out thermal polymerization at 80 ℃, and carrying out heat treatment at the temperature for 20 hours to obtain a precursor; heating the precursor to 800 ℃ at the heating rate of 6 ℃/min under helium gas for roasting and carbonizing, and preserving heat for 4 hours to obtain a mesoporous carbon material;
(2) Adding the mesoporous carbon material obtained in the step (1) into 50mL of 2mol/L potassium permanganate solution for treatment for 1 h; then filtering and washing to obtain oxidation-treated mesoporous carbon;
(3) dissolving 0.02mol of cobalt nitrate in 10mL of deionized water, then adding 1g of mesoporous carbon obtained in the step (2), uniformly stirring to obtain a mixture solution, then adding 0.12mol of 2-methylimidazole, 0.6mmol of ferric nitrate and 0.6mmol of zinc nitrate into the mixture solution, stirring for 20h at 25 ℃, filtering, washing, drying for 12h at 100 ℃, and then roasting for 3h at 500 ℃ under nitrogen to obtain the methanol adsorbent.
Example 2
A method for preparing a formaldehyde adsorbent for air purification, the method comprising the steps of:
(1) preparation of mesoporous carbon
Dissolving 14mmol of phenol and 56mmol of formaldehyde in 10ml of 0.7mol/L potassium hydroxide solution, stirring uniformly at 70 ℃, cooling to room temperature, adjusting the solution to be neutral by hydrochloric acid, removing water under the vacuum condition of 100 ℃, dissolving the obtained phenolic resin in ethanol to prepare 30 wt% phenolic resin ethanol solution; dissolving 1g F127, 0.4mmol of manganese chloride and 0.2mmol of copper acetate in a phenolic resin mixed solution, evaporating at room temperature, carrying out thermal polymerization at 90 ℃, and carrying out heat treatment at the temperature for 16h to obtain a precursor; and heating the precursor to 850 ℃ at the heating rate of 8 ℃/min under inert gas, roasting, carbonizing, and preserving heat for 2 hours to obtain the mesoporous carbon material.
(2) Adding the mesoporous carbon obtained in the step (1) into 50mL of 2mol/L hydrogen peroxide solution for treatment for 1.5 h; then filtering and washing to obtain oxidized mesoporous carbon;
(3) dissolving 0.03mol of cobalt chloride in 10mL of deionized water, adding 1g of mesoporous carbon obtained in the step (2), uniformly stirring to obtain a mixture solution, adding 0.24mol of 2-methylimidazole, 1.8mmol of ferric chloride and 0.6mmol of zinc acetate into the mixture solution, stirring at 30 ℃ for 16h, filtering, washing, drying at 120 ℃ for 10h, and roasting at 550 ℃ under argon for 2h to obtain the methanol adsorbent.
Example 3
A method for preparing a formaldehyde adsorbent for air purification, the method comprising the steps of:
(1) preparation of mesoporous carbon
Dissolving 10mmol of phenol and 20mmol of formaldehyde in 10mL0.5mol/L sodium hydroxide solution, stirring uniformly at 50 ℃, cooling to room temperature, adjusting the solution to be neutral by hydrochloric acid, removing water under the vacuum condition of 80 ℃, and dissolving the obtained phenolic resin in ethanol to prepare 20 wt% phenolic resin ethanol solution; dissolving 1g P123, 0.2mmol of manganese acetate and 0.4mmol of copper chloride in a phenolic resin mixed solution, evaporating at room temperature, carrying out thermal polymerization at 70 ℃, and carrying out heat treatment at the temperature for 24 hours to obtain a precursor; and heating the precursor to 750 ℃ at the heating rate of 4 ℃/min under helium gas, roasting, carbonizing, and preserving heat for 5 hours to obtain the mesoporous carbon material.
(2) Adding the mesoporous carbon obtained in the step (1) into 50mL of 2mol/L potassium permanganate solution, and treating for 0.5-1.5 h; then filtering and washing to obtain oxidized mesoporous carbon;
(3) dissolving 0.01mol of cobalt acetate in 10mL of deionized water, then adding 1g of mesoporous carbon obtained in the step (2), uniformly stirring to obtain a mixture solution, then adding 0.04mol of 2-methylimidazole, 0.2mmol of iron acetate and 0.6mmol of zinc chloride into the mixture solution, stirring at 20 ℃ for 22h, filtering, washing, drying at 80 ℃ for 14h, and then roasting at 450 ℃ for 4h under the atmosphere of helium gas to obtain the methanol adsorbent.
Comparative example 1
A method for preparing a formaldehyde adsorbent for air purification, the method comprising the steps of:
(1) preparation of mesoporous carbon
Dissolving 12mmol of phenol and 36mmol of formaldehyde in 10mL0.6mol/L sodium hydroxide solution, uniformly stirring at 60 ℃, cooling to room temperature, adjusting the solution to be neutral by hydrochloric acid, removing moisture under the vacuum condition of 90 ℃, and dissolving the obtained phenolic resin in ethanol to prepare 35 wt% phenolic resin ethanol solution; dissolving 1g P123 and 0.6mmol of manganese nitrate in the phenolic resin mixed solution, evaporating at room temperature, carrying out thermal polymerization at 80 ℃, and carrying out thermal treatment at the temperature for 20h to obtain a precursor; heating the precursor to 800 ℃ at the heating rate of 6 ℃/min under helium gas for roasting and carbonizing, and preserving heat for 4 hours to obtain a mesoporous carbon material;
(2) Adding the mesoporous carbon material obtained in the step (1) into 50mL of 2mol/L potassium permanganate solution for treatment for 1 h; then filtering and washing to obtain oxidized mesoporous carbon;
(3) dissolving 0.02mol of cobalt nitrate in 10mL of deionized water, then adding 1g of mesoporous carbon obtained in the step (2), uniformly stirring to obtain a mixture solution, then adding 0.12mol of 2-methylimidazole, 0.6mmol of ferric nitrate and 0.6mmol of zinc nitrate into the mixture solution, stirring for 20h at 25 ℃, filtering, washing, drying for 12h at 100 ℃, and then roasting for 3h at 500 ℃ under nitrogen to obtain the methanol adsorbent.
Comparative example 2
A method for preparing a formaldehyde adsorbent for air purification, the method comprising the steps of:
(1) preparation of mesoporous carbon
Dissolving 12mmol of phenol and 36mmol of formaldehyde in 10mL0.6mol/L sodium hydroxide solution, uniformly stirring at 60 ℃, cooling to room temperature, adjusting the solution to be neutral by hydrochloric acid, removing moisture under the vacuum condition of 90 ℃, and dissolving the obtained phenolic resin in ethanol to prepare 35 wt% phenolic resin ethanol solution; dissolving 1g P123 and 0.6mmol of copper nitrate in the phenolic resin mixed solution, evaporating at room temperature, carrying out thermal polymerization at 80 ℃, and carrying out thermal treatment at the temperature for 20h to obtain a precursor; heating the precursor to 800 ℃ at the heating rate of 6 ℃/min under helium gas for roasting and carbonizing, and preserving heat for 4 hours to obtain a mesoporous carbon material;
(2) Adding the mesoporous carbon material obtained in the step (1) into 50mL of 2mol/L potassium permanganate solution for treatment for 1 h; then filtering and washing to obtain oxidation-treated mesoporous carbon;
(3) dissolving 0.02mol of cobalt nitrate in 10mL of deionized water, then adding 1g of mesoporous carbon obtained in the step (2), uniformly stirring to obtain a mixture solution, then adding 0.12mol of 2-methylimidazole, 0.6mmol of ferric nitrate and 0.6mmol of zinc nitrate into the mixture solution, stirring for 20h at 25 ℃, filtering, washing, drying for 12h at 100 ℃, and then roasting for 3h at 500 ℃ under nitrogen to obtain the methanol adsorbent.
Comparative example 3
A method for preparing a formaldehyde adsorbent for air purification, the method comprising the steps of:
(1) preparation of mesoporous carbon
Dissolving 12mmol of phenol and 36mmol of formaldehyde in 10mL of 0.6mol/L sodium hydroxide solution, stirring uniformly at 60 ℃, cooling to room temperature, adjusting the solution to be neutral by hydrochloric acid, removing moisture under a vacuum condition of 90 ℃, and dissolving the obtained phenolic resin in ethanol to prepare 35 wt% of phenolic resin ethanol solution; dissolving 1g P123, 0.3mmol of manganese nitrate and 0.3mmol of copper nitrate in a phenolic resin mixed solution, evaporating at room temperature, carrying out thermal polymerization at 80 ℃, and carrying out heat treatment at the temperature for 20 hours to obtain a precursor; heating the precursor to 800 ℃ at the heating rate of 6 ℃/min under helium gas for roasting and carbonizing, and preserving heat for 4 hours to obtain a mesoporous carbon material;
(2) Adding the mesoporous carbon material obtained in the step (1) into 50mL of 2mol/L potassium permanganate solution for treatment for 1 h; then filtering and washing to obtain oxidation-treated mesoporous carbon;
(3) dissolving 0.02mol of cobalt nitrate in 10mL of deionized water, then adding 1g of mesoporous carbon obtained in the step (2), uniformly stirring to obtain a mixture solution, then adding 0.12mol of 2-methylimidazole and 1.2mmol of ferric nitrate into the mixture solution, stirring for 20h at 25 ℃, filtering, washing, drying for 12h at 100 ℃, and then roasting for 3h at 500 ℃ under nitrogen to obtain the methanol adsorbent.
Comparative example 4
A method for preparing a formaldehyde adsorbent for air purification, the method comprising the steps of:
(1) preparation of mesoporous carbon
Dissolving 12mmol of phenol and 36mmol of formaldehyde in 10mL of 0.6mol/L sodium hydroxide solution, stirring uniformly at 60 ℃, cooling to room temperature, adjusting the solution to be neutral by hydrochloric acid, removing moisture under a vacuum condition of 90 ℃, and dissolving the obtained phenolic resin in ethanol to prepare 35 wt% of phenolic resin ethanol solution; dissolving 1g P123, 0.3mmol of manganese nitrate and 0.3mmol of copper nitrate in a phenolic resin mixed solution, evaporating at room temperature, carrying out thermal polymerization at 80 ℃, and carrying out heat treatment at the temperature for 20 hours to obtain a precursor; and heating the precursor to 800 ℃ at the heating rate of 6 ℃/min under helium gas, roasting, carbonizing, and preserving heat for 4 hours to obtain the mesoporous carbon material.
(2) Adding the mesoporous carbon material obtained in the step (1) into 50mL of 2mol/L potassium permanganate solution for treatment for 1 h; then filtering and washing to obtain oxidation-treated mesoporous carbon;
(3) dissolving 0.02mol of cobalt nitrate in 10mL of deionized water, then adding 1g of mesoporous carbon obtained in the step (2), uniformly stirring to obtain a mixture solution, then adding 0.12mol of 2-methylimidazole and 1.2mmol of zinc nitrate into the mixture solution, stirring for 20h at 25 ℃, filtering, washing, drying for 12h at 100 ℃, and then roasting for 3h at 500 ℃ under nitrogen to obtain the methanol adsorbent.
Comparative example 5
A method for preparing a formaldehyde adsorbent for air purification, the method comprising the steps of:
(1) preparation of mesoporous carbon
Dissolving 12mmol of phenol and 36mmol of formaldehyde in 10mL of 0.6mol/L sodium hydroxide solution, uniformly stirring at 60 ℃, cooling to room temperature, adjusting the solution to be neutral by hydrochloric acid, removing water under the vacuum condition of 90 ℃, and dissolving the obtained phenolic resin in ethanol to prepare 35 wt% of phenolic resin ethanol solution; dissolving 1g P123, 0.3mmol of manganese nitrate and 0.3mmol of copper nitrate in a phenolic resin mixed solution, evaporating at room temperature, carrying out thermal polymerization at 80 ℃, and carrying out heat treatment at the temperature for 20 hours to obtain a precursor; heating the precursor to 800 ℃ at the heating rate of 6 ℃/min under helium gas for roasting and carbonizing, and preserving heat for 4 hours to obtain a mesoporous carbon material;
(2) Dissolving 0.02mol of cobalt nitrate in 10mL of deionized water, then adding 1g of mesoporous carbon obtained in the step (1), uniformly stirring to obtain a mixture solution, then adding 0.12mol of 2-methylimidazole, 0.6mmol of ferric nitrate and 0.6mmol of zinc nitrate into the mixture solution, stirring for 20h at 25 ℃, filtering, washing, drying for 12h at 100 ℃, and then roasting for 3h at 500 ℃ under nitrogen to obtain the methanol adsorbent.
Comparative example 6
A method for preparing a formaldehyde adsorbent for air purification, the method comprising the steps of:
(1) preparation of mesoporous carbon
Dissolving 12mmol of phenol and 36mmol of formaldehyde in 10mL of 0.6mol/L sodium hydroxide solution, stirring uniformly at 60 ℃, cooling to room temperature, adjusting the solution to be neutral by hydrochloric acid, removing moisture under a vacuum condition of 90 ℃, and dissolving the obtained phenolic resin in ethanol to prepare 35 wt% of phenolic resin ethanol solution; dissolving 1g P123, 0.3mmol of manganese nitrate and 0.3mmol of copper nitrate in a phenolic resin mixed solution, evaporating at room temperature, carrying out thermal polymerization at 80 ℃, and carrying out heat treatment at the temperature for 20 hours to obtain a precursor; heating the precursor to 800 ℃ at the heating rate of 6 ℃/min under helium gas for roasting and carbonizing, and preserving heat for 4 hours to obtain a mesoporous carbon material;
(2) Adding the mesoporous carbon material obtained in the step (1) into 50mL of 2mol/L potassium permanganate solution for treatment for 1 h; then filtering and washing to obtain oxidation-treated mesoporous carbon;
(3) dissolving 0.02mol of cobalt nitrate in 10mL of deionized water, uniformly stirring to obtain a mixture solution, adding 0.12mol of 2-methylimidazole, 0.6mmol of ferric nitrate and 0.6mmol of zinc nitrate into the mixture solution, stirring at 25 ℃ for 20 hours, then adding 1g of mesoporous carbon obtained in the step (2), continuing stirring for 0.5min, filtering, washing, drying at 100 ℃ for 12 hours, and then roasting at 500 ℃ under nitrogen for 3 hours to obtain the methanol adsorbent.
The formaldehyde adsorbents for air purification of examples 1 to 3 and comparative examples 1 to 6 were subjected to the adsorption and degradation experiments of formaldehyde, and the specific test results are shown in table 1.
Adsorption test of formaldehyde: and (3) putting 20g of sample into a closed container, wherein the volume of the container is 1000L, introducing 100ppm of formaldehyde as VOCs to be detected, extracting gas in the closed environment through a sampling needle, detecting the initial concentration of toluene in the container by using an acetylacetone method, and checking the removal rate at 60 min.
Degradation test of formaldehyde: putting 20g of sample into a closed container, wherein the volume of the container is 1000L, introducing 100ppm of formaldehyde as VOCs to be detected, extracting gas in the closed environment through a sampling needle, detecting the initial concentration of toluene in the container by using an acetylacetone method, then introducing 100ppm of formaldehyde gas into the closed environment for multiple times until the concentration of the VOCs in the closed environment is equal to the determined initial concentration and is still unchanged after 60min, opening 300W xenon lamp light for degradation performance test, and determining the formaldehyde degradation rate at 30 min.
TABLE 1
As can be seen from Table 1, the formaldehyde adsorbent for air purification prepared in the present application has advantageous adsorption and removal ability to formaldehyde, and it can be confirmed by comparing examples 1 to 3 with comparative examples 1 to 6 that the components of the present invention have a mutual coordination effect and it is the mutual coordination effect between the components that promotes the improvement of the adsorption ability and the degradation ability of the formaldehyde adsorbent.
The above embodiments are preferred embodiments of the present invention, but the present invention is not limited to the above embodiments, and any other changes, modifications, substitutions, combinations, and simplifications which do not depart from the spirit and principle of the present invention should be construed as equivalents thereof, and all such modifications are intended to be included in the scope of the present invention.