CN116585909A - Iron-based photo-thermal conversion film and preparation method and application thereof - Google Patents

Iron-based photo-thermal conversion film and preparation method and application thereof Download PDF

Info

Publication number
CN116585909A
CN116585909A CN202310864575.7A CN202310864575A CN116585909A CN 116585909 A CN116585909 A CN 116585909A CN 202310864575 A CN202310864575 A CN 202310864575A CN 116585909 A CN116585909 A CN 116585909A
Authority
CN
China
Prior art keywords
iron
conversion film
photothermal conversion
photothermal
nanowire
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN202310864575.7A
Other languages
Chinese (zh)
Other versions
CN116585909B (en
Inventor
韩凯
周川玲
黄李茗铭
宁俊淇
马鑫
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Central South University
Original Assignee
Central South University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Central South University filed Critical Central South University
Priority to CN202310864575.7A priority Critical patent/CN116585909B/en
Publication of CN116585909A publication Critical patent/CN116585909A/en
Application granted granted Critical
Publication of CN116585909B publication Critical patent/CN116585909B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D71/00Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
    • B01D71/06Organic material
    • B01D71/30Polyalkenyl halides
    • B01D71/32Polyalkenyl halides containing fluorine atoms
    • B01D71/36Polytetrafluoroethene
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D69/00Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
    • B01D69/02Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor characterised by their properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D71/00Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
    • B01D71/02Inorganic material
    • B01D71/022Metals
    • B01D71/0223Group 8, 9 or 10 metals
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D71/00Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
    • B01D71/02Inorganic material
    • B01D71/04Glass
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • C02F1/14Treatment of water, waste water, or sewage by heating by distillation or evaporation using solar energy
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/36Hydrophilic membranes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/43Specific optical properties
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/003Wastewater from hospitals, laboratories and the like, heavily contaminated by pathogenic microorganisms
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/08Seawater, e.g. for desalination

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Inorganic Chemistry (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Sustainable Development (AREA)
  • Sustainable Energy (AREA)
  • Compounds Of Iron (AREA)

Abstract

The invention discloses an iron-based photo-thermal conversion film, a preparation method and application thereof, and belongs to the technical field of photo-thermal conversion. The iron-based photothermal conversion film provided by the invention comprises: a substrate, which is a hydrophilic film; a photothermal conversion material supported on the substrate surface, the photothermal conversion material comprising an iron-based nanowire; the preparation method of the iron-based nanowire comprises the following steps: D1. carrying out solvothermal reaction on a mixture of nitrilotriacetic acid and ferrous salt; D2. and (3) carrying out heat treatment on the solid reaction product obtained in the step D1. The iron-based light-heat conversion film provided by the invention has the advantages of low cost, environmental friendliness, high absorbance and high light-heat conversion efficiency due to the selection of the materials of all the components. The invention also provides a preparation method and application of the iron-based light-heat conversion film.

Description

Iron-based photo-thermal conversion film and preparation method and application thereof
Technical Field
The invention belongs to the technical field of photo-thermal conversion, and particularly relates to an iron-based photo-thermal conversion film, and a preparation method and application thereof.
Background
Under the great background of rapid development of chemical industry, medicine industry, biology industry and the like, the demand of water as a raw material, a cleaning agent and a reaction medium is increasing. Water resource purification and recovery technology has received great attention. The mature water treatment technology at the present stage has a plurality of technologies, such as biological treatment method, physical adsorption method, ion exchange resin and reverse osmosis technology, but the recovery method has the defects of larger equipment investment, larger energy consumption, high recovery cost, long recovery flow and the like.
In order to overcome the above drawbacks, researchers have proposed the use of membrane separation techniques to separate the different components of water. The membrane separation technology is an emerging technology and has the advantages of low energy consumption, simple equipment, convenient operation, high separation efficiency and the like. At present, membrane separation is used for replacing traditional methods of rectification, adsorption, filtration and the like in various systems, such as oil-water separation, gas separation, alcohol-water separation, water treatment, sea water desalination and the like. The basic principle of the membrane separation technology is that under the osmosis action of the membrane, the chemical potential difference or energy difference at two sides of the membrane is used as the mass transfer driving force of the separation process to separate and purify the mixed gas phase or liquid phase to concentrate the membrane. The membrane separation reduces the investment of equipment cost to a great extent. Meanwhile, compared with the traditional extraction, absorption-desorption and other technologies, the method has the advantages that the separation is easier because the third component is not introduced, and the pollution to the environment is reduced. Therefore, the application of the membrane separation technology in separation engineering is becoming widespread. However, the realization of membrane separation also requires a certain energy consumption, and has a great demand for energy and a severe demand for membranes, and the preparation cost of many membrane modules is high.
Based on this, it is an important task to find a more energy-saving and efficient water resource purification and recovery method for removing impurities such as dyes and metal ions in water.
Among all renewable energy sources, solar energy is considered as the most promising option to meet human energy demands. The solar energy interface evaporation water treatment is a reliable, environment-friendly and low-cost technology for realizing the photo-thermal conversion process by utilizing solar energy. The interface evaporation system is characterized by light-heat conversion, heat management, water and steam delivery, high integration of peripheral devices and fine design, and can more efficiently and rapidly absorb water from a blocky water body or even the atmosphere and generate steam through heat energy converted by solar energy by virtue of technologies such as microstructure photonics, thermal structure design, material modification processing, mechanical design and the like. Because the contact area with the water body is small, and the water evaporation process only occurs at the water-gas interface, the heat can be avoided to the greatest extent to heat the water body, the heat loss is reduced, and the energy utilization efficiency is greatly improved.
The research of the photo-thermal conversion film material becomes a trend by combining the advantages of the traditional film separation and solar energy interface evaporation.
In order to obtain a higher water evaporation rate and thus more effectively improve the working efficiency of the interfacial evaporation water treatment technology, it is required to develop a photothermal conversion film capable of achieving broadband and efficient light absorption in the solar spectrum range. The metal-based material generates an enhanced near electric field due to the interaction between the plasmon effect and the incident photons, and forms local hot spots with sub-wavelength scale, so that the metal nano structure can obtain stronger light absorption performance. Therefore, metal-based photothermal conversion materials are currently becoming a big research hotspot.
The metal materials disclosed in the related report and applicable to the interfacial evaporation water treatment technology comprise gold nanoparticles, gold-silicon dioxide composite micro-nano particles, gold-graphene composite micro-nano particles, silver nanoparticles, copper nanoparticles, MOF-Ag nano sheets and the like. However, the metal-based materials which are proved to be feasible at present generally have the defects of high price, complex preparation flow, low evaporation rate and the like.
To overcome the above problems, there are attempts to use a general transition metal material in the cross-section evaporative water treatment technique. For example, the technology discloses a manganese oxide-biochar composite material, but the preparation process of the composite material is overlong and the cost is higher; the invention also discloses a wood-based composite material with a magnetic nanoparticle coating and a preparation method thereof, and the preparation method is simple, but the water evaporation rate and the photo-thermal conversion efficiency are low.
In summary, there is still a need to develop a simple, low-cost and environmentally friendly metal-based photothermal conversion film, which has the advantages of high absorbance, high evaporation rate and Gao Guangre conversion efficiency.
Disclosure of Invention
The present invention aims to solve at least one of the technical problems in the prior art described above. Therefore, the invention provides the iron-based photo-thermal conversion film which has the advantages of low cost, environmental friendliness, high light absorbance, high evaporation rate and high photo-thermal conversion efficiency.
The invention also provides a preparation method of the iron-based light-heat conversion film.
The invention also provides a photothermal converter with the iron-based photothermal conversion film.
The invention also provides application of the photothermal converter in water treatment and solvent purification.
According to an aspect of the present invention, there is provided an iron-based photothermal conversion film comprising:
a substrate, which is a hydrophilic film;
the light-heat conversion material is arranged on the surface of the substrate and comprises iron-based nanowires;
the preparation method of the iron-based nanowire comprises the following steps:
D1. carrying out solvothermal reaction on a mixture of nitrilotriacetic acid and ferrous salt;
D2. and (3) carrying out heat treatment on the solid reaction product obtained in the step D1.
The iron-based photothermal conversion film according to a preferred embodiment of the present invention has at least the following advantageous effects:
(1) In the iron-based photothermal conversion film provided by the invention, the adopted photothermal conversion material is the iron-based nanowire, and compared with noble metal nanoparticles such as Au, ag, cu and the like, the material cost is lower. Compared with an organic light-heat conversion material which is easy to decompose, the light-heat conversion material adopted by the invention has higher stability and environmental friendliness.
(2) The invention adopts the nano linear photo-thermal conversion materials, and pore structures can be constructed by mutually stacking the nano linear photo-thermal conversion materials, so that the refraction and reflection of light in the iron-based photo-thermal conversion film can be effectively enhanced, and a space can be reserved for dissipation of generated water vapor (or other solvent vapors), thereby enhancing the evaporation rate and efficiency of the iron-based photo-thermal conversion film.
(3) The preparation condition of the iron-based nanowire is simple, and the corresponding iron-based nanowire can be obtained by heat treatment of the organic metal complex product in a specific atmosphere. Therefore, the preparation process and the preparation cost of the iron-based light-heat conversion film can be effectively reduced.
(4) The iron-based photothermal conversion film provided by the invention has the absorbance of more than or equal to 95 percent (up to 95.72 percent) within the range of 280-2500 nm, which exceeds commercial materials with mature technology in the market, and the cost is lower.
In some embodiments of the present invention, the hydrophilic membrane comprises at least one of glass fiber, organic nylon or PTFE (polytetrafluoroethylene).
In some embodiments of the invention, the hydrophilic membrane comprises glass fibers. Therefore, the hydrophilic film is formed by stacking and interweaving nano fibers and is combined with the nano linear iron-based nanowires, refraction and reflection of light in the iron-based photothermal conversion film can be further enhanced, space can be reserved for dissipation of generated water vapor, and evaporation rate and efficiency of the iron-based photothermal conversion film are enhanced.
In some embodiments of the invention, the length of the iron-based nanowire is 4-150 μm.
In some embodiments of the invention, the iron-based nanowires have a length of 10-20 μm.
In some preferred embodiments of the present invention, the diameter of the iron-based nanowire is 40-500 nm.
In some preferred embodiments of the present invention, the diameter of the iron-based nanowire is 200 to 300nm.
In some embodiments of the invention, the material of the iron-based nanowire comprises at least one of iron oxide and an iron-carbon nanocomposite. Wherein, the specific material composition of the iron-based nanowire is related to the preparation method thereof.
In some embodiments of the present invention, the iron-carbon composite material has an iron content of 30 to 90wt%.
When the sun illumination is simulated, in the iron-carbon composite material, due to the synergistic effect of the iron simple substance and carbon, the metal plasmon effect and the thermal vibration effect of the carbon material can simultaneously occur on the surface, and the metal plasmon effect and the thermal vibration effect of the carbon material can both promote the absorption of the material to light. The iron-based nanowire made of the iron-carbon composite material has extremely strong light absorption performance by combining the nanowire-shaped structure.
In some embodiments of the present invention, the method of preparing the iron-based nanowire includes the steps of:
D1. carrying out solvothermal reaction on a mixture of nitrilotriacetic acid and ferrous salt;
D2. and (3) carrying out heat treatment on the solid reaction product obtained in the step D1.
In some embodiments of the invention, in step D1, the solvent employed for the solvothermal reaction comprises water and isopropanol.
In some embodiments of the present invention, the volume concentration of the isopropanol in the solvent used in the solvothermal reaction is 10-90%.
In some embodiments of the present invention, the volume concentration of the isopropanol in the solvent is 11-15%.
In some embodiments of the invention, in step D1, the ferrous salt comprises at least one of ferrous chloride, ferrous sulfate, and hydrates thereof. Ferrous salt can be adopted to complex with nitrilotriacetic acid, so that a linear solid product is formed; the iron-based nanowires inherit the morphology of the solid product here.
In some embodiments of the present invention, in the step D1, the molar ratio of nitrilotriacetic acid to ferrous salt is 1:2-4. For example, the ratio may be 1:2.5 to 3.
In some embodiments of the present invention, in the step D1, the molar concentration of the ferrous salt is 0.05-0.2 mol/L. For example, the concentration may be specifically 0.1 to 0.15mol/L.
In some embodiments of the invention, in step D1, the method of formulating the mixture for the solvothermal reaction comprises mixing the ferrous salt, nitrilotriacetic acid, and solvent. Wherein the method of mixing comprises stirring. The mixing time is 0.5-1.5 h. For example, it may be about 1 hour.
In some embodiments of the present invention, in the step D1, the solvothermal reaction temperature is 100 to 200 ℃.
In some embodiments of the present invention, in the step D1, the solvothermal reaction temperature is 150 to 190 ℃. For example, it may be about 180 ℃.
In some embodiments of the present invention, in step D1, the duration of the solvothermal reaction is 0.5 to 36 hours.
In some embodiments of the present invention, in step D1, the duration of the solvothermal reaction is 20 to 25 hours. For example, it may be about 24 hours.
In some embodiments of the invention, step D1 further comprises washing and drying the resulting solid product after the solvothermal reaction. Specifically, the washing includes ethanol washing. Whereby the formation of iron hydroxide by hydrolysis of residual iron ions can be avoided. The cleaning times are 1-3 times. Further, the drying includes at least one of air blast drying and vacuum drying. The drying temperature is 60-100 ℃; for example, it may be about 80 ℃.
In some embodiments of the invention, in step D2, the heat-treated atmosphere comprises at least one of a shielding gas and oxygen. When oxygen is included in the atmosphere, iron oxide is included in the iron-based nanowire; if the atmosphere includes only the shielding gas, the main component of the iron-based nanowire includes the iron-carbon composite material, and at this time, nitrilotriacetic acid is carbonized as a ligand during the heat treatment to form pyrolytic carbon, which also has a reducing effect, thereby largely ensuring that iron exists in a simple substance form.
In some embodiments of the present invention, in step D2, the apparatus for heat treatment includes an atmosphere in a flowing state, or the apparatus is in a sealed state, in which the atmosphere for heat treatment is sealed. The means is not limited as long as a specific atmosphere is satisfied, and the flow rate of the atmosphere may be adjusted according to the apparatus used and the throughput.
In some embodiments of the present invention, in step D2, the temperature of the heat treatment is 500 to 800 ℃.
In some embodiments of the present invention, in the step D1, the temperature of the heat treatment is 550 to 650 ℃. For example, it may be about 600 ℃.
In some embodiments of the present invention, in step D2, the time of the heat treatment is 2 to 4 hours. For example, it may be about 3 hours.
In some embodiments of the present invention, in step D2, the heating rate of the heat treatment is 3 to 10 ℃/min. For example, it may be about 5℃per minute.
In some embodiments of the invention, the method of preparing an iron-based nanowire further comprises grinding to obtain a solid after the heat treatment.
In some embodiments of the invention, the iron-based photothermal conversion film further comprises a binder. The adhesive is coated on the surface of the substrate and is used for improving the adhesion strength between the iron-based nanowires and the substrate. Because the binder is introduced, the iron-based light-heat conversion film has good wear resistance and can also enhance the stability of the material.
In some embodiments of the invention, the binder comprises at least one of sodium carboxymethyl cellulose (CMC) and polyvinylidene fluoride (PVDF).
In some embodiments of the present invention, the iron-based photothermal conversion filmThe load capacity of the iron-based nanowire is 0.5-1.5 mg/cm 2
In some embodiments of the present invention, in the iron-based photothermal conversion film, the loading amount of the iron-based nanowires is 0.7-1.3 mg/cm 2
In some embodiments of the present invention, in the iron-based photothermal conversion film, the loading amount of the iron-based nanowires is 0.9 to 1.1mg/cm 2
In some embodiments of the invention, the mass ratio of the binder to the iron-based nanowires is 1-30:100. For example, the ratio may be 3 to 8:100. And more specifically may be about 1:20.
According to still another aspect of the present invention, there is provided a method of manufacturing the iron-based photothermal conversion film, the method comprising applying a slurry comprising the iron-based nanowires to a surface of the substrate and drying.
The preparation method according to a preferred embodiment of the present invention has at least the following advantageous effects:
the preparation method provided by the invention is simple to operate, low in energy consumption and easy for large-scale preparation.
In some embodiments of the invention, the slurry further comprises a binder and a solvent.
In some embodiments of the invention, the binder comprises at least one of sodium carboxymethyl cellulose (CMC) and polyvinylidene fluoride (PVDF). The adhesive can enable the iron-based nanowires to be tightly adhered to the surface of the substrate, and improves the mechanical stability of the iron-based photothermal conversion film.
In some embodiments of the invention, the solvent is one of water, N-methylpyrrolidone, and ethanol.
In some embodiments of the invention, the concentration of the iron-based nanowires in the slurry is 0.1-10 g/L. For example, the concentration may be specifically 0.2 to 0.3g/L.
In some embodiments of the invention, the slurry is formulated by mixing the iron-based nanowires, binder, and solvent.
In some embodiments of the invention, the slurry is prepared by mixing the iron-based nanowires, binder, and a portion of the solvent, and diluting the resulting mixture with the remaining solvent. Thereby, accurate quantification of the iron-based nanowires in the slurry (higher concentration, small mass weighing error of the iron-based nanowires) and uniform loading of the iron-based nanowires on the substrate (large volume of slurry, uniform loading) can be realized.
In some embodiments of the invention, the method of coating is at least one of suction filtration, knife coating, spray coating, and spin coating.
According to still another aspect of the present invention, there is provided a photothermal converter including the iron-based photothermal conversion film.
Since the photothermal converter employs the iron-based photothermal conversion film, all advantages of the iron-based photothermal conversion film are possessed.
In some embodiments of the invention, the structure of the photothermal converter comprises:
an iron-based photothermal conversion film;
one end of the liquid transmission channel is connected with the iron-based light-heat conversion film, and the other end of the liquid transmission channel is immersed in the liquid to be treated;
the heat insulation layer is positioned between the upper liquid level of the liquid to be treated and the iron-based light-heat conversion film, and a through hole is formed in the heat insulation layer; the liquid transport passage passes through the through hole.
Therefore, the liquid transmission channel can transmit the liquid to be treated into the iron-based light-heat conversion film for evaporation; and the heat insulation layer can avoid heat loss generated in the iron-based light-heat conversion film, and improves the evaporation capacity of liquid.
In some embodiments of the invention, the liquid transport channel material is cotton.
In some embodiments of the invention, the heat insulating layer is made of sponge foam.
In some embodiments of the invention, the insulating layer is not in contact with the iron-based photothermal conversion film. Whereby the heat insulating performance can be increased.
In some embodiments of the invention, the geometric center of the iron-based photothermal conversion film falls within a contact range of the iron-based photothermal conversion film and the liquid transport channel.
According to the photothermal converter provided by the invention, the direct contact between the liquid to be treated (such as water or an organic solvent) and the iron-based photothermal conversion film (light absorption layer) is reduced by utilizing the local heating principle, and compared with the traditional integral heating mode, the photothermal converter can effectively reduce heat loss and realize higher photothermal conversion water evaporation efficiency.
According to a further aspect of the invention, there is provided the use of the photothermal converter in water treatment and solvent purification.
In some embodiments of the invention, the use in water treatment includes use in interfacial evaporation water treatment.
In some embodiments of the invention, the application in water treatment is in a range of applications including at least one of seawater, industrial wastewater, domestic wastewater and medical wastewater.
In some embodiments of the invention, the application in water treatment is in a range including at least one of heavy metal ion wastewater, organic dye wastewater, and high concentration brine. In the application process, the impurity removal rate is higher, and the application prospect is wide.
In some embodiments of the invention, the use in water treatment comprises illuminating the photothermal converter with a source of sunlight. Specifically, the iron-based photothermal conversion film is irradiated.
The term "about" as used herein, unless otherwise specified, means that the tolerance is within + -2%, for example, about 100 is actually 100 + -2%. Times.100.
Unless otherwise specified, the term "between … …" in the present invention includes the present number, for example "between 2 and 3" includes the end values of 2 and 3.
Additional features and advantages of the invention will be set forth in the description which follows, and in part will be obvious from the description, or may be learned by practice of the invention.
Drawings
The invention is further described with reference to the accompanying drawings and examples, in which:
fig. 1 is a schematic diagram of a photothermal converter according to embodiment 9 to 16 of the present invention.
Fig. 2 is an SEM image of the iron-based nanowires obtained in example 1 of the present invention.
Fig. 3 is an SEM image of the iron-based nanowires obtained in example 9 of the present invention.
FIG. 4 shows the evaporation rate of pure water by the photothermal transducers according to examples 9 to 13 of the present invention.
FIG. 5 shows XRD patterns of the iron-based nanowire powders obtained in examples 1 and 6 to 7 of the present invention.
Fig. 6 is an XRD pattern of the iron-based nanowire obtained in example 8 of the present invention.
Fig. 7 is an absorption spectrum of the photothermal conversion films obtained in example 1, example 8 and comparative examples 2 to 3 of the present invention in a wet state.
FIG. 8 shows the light-to-heat conversion film in the light-to-heat converters of example 9, example 16 and comparative examples 4 to 5 of the present invention at 1 solar light intensity of 1kW/m 2 And (5) a surface temperature change chart in the evaporation process for 1h under illumination.
FIG. 9 shows the photothermal converters of examples 9, 16 and comparative examples 4 to 5 of the present invention at 1kW/m 2 And the water loss curve is used for the water body weight loss curve when the solar interface evaporation water treatment is performed under illumination.
FIG. 10 is a graph showing the water treatment at 1kW/m for the photothermal converter according to example 9 of the present invention 2 And (3) purifying performance diagram of the organic dye wastewater containing methylene blue under illumination.
FIG. 11 is a graph showing the result of example 9 of the present invention, in which the photothermal conversion is carried out at 1kW/m in the treatment of industrial wastewater containing actual heavy metals 2 And (5) removing performance diagram of heavy metal ions under illumination.
Reference numerals:
the liquid to be treated 100, the liquid transmission channel 200, the heat insulation layer 300, the iron-based light-heat conversion film 400 and the light source 500.
Detailed Description
The conception and the technical effects produced by the present invention will be clearly and completely described in conjunction with the embodiments below to fully understand the objects, features and effects of the present invention. It is apparent that the described embodiments are only some embodiments of the present invention, but not all embodiments, and that other embodiments obtained by those skilled in the art without inventive effort are within the scope of the present invention based on the embodiments of the present invention.
Examples of embodiments are illustrated in the accompanying drawings, wherein like or similar reference numerals refer to like or similar elements throughout or elements having like or similar functionality. In the description of the present invention, unless explicitly defined otherwise, terms such as arrangement, installation, connection, etc. should be construed broadly and the specific meaning of the terms in the present invention can be reasonably determined by a person skilled in the art in combination with the specific contents of the technical scheme.
Example 1
The embodiment prepares the iron-based light-heat conversion film, which comprises the following specific processes:
A1. weighing 0.6000g nitrilotriacetic acid (CAS: 139-13-9), 1.2493g ferrous chloride tetrahydrate, weighing 52.5mL deionized water and 7.5mL isopropyl alcohol, adding into a polytetrafluoroethylene hydrothermal kettle liner, magnetically stirring at 400rpm for 1h, adding a stainless steel water heating kettle, and reacting in a 180 ℃ oven for 24h;
A2. after the hydrothermal kettle is naturally cooled to room temperature, transferring the reaction product into a beaker, performing ultrasonic dispersion for 0.5h, rinsing with 500mL of ethanol, performing suction filtration, and repeating the steps for two other times; finally, the obtained product is dried in a baking oven at 70 ℃;
A3. carrying out heat treatment on the obtained product by using a tubular furnace filled with argon, controlling the speed of the argon to be 200mL/min, the heating rate to be 5 ℃/min, the heat preservation temperature and time to be 600 ℃/2h, and taking out the product after the temperature is reduced to room temperature to obtain a nano linear iron-carbon composite material (marked as Fe/C);
A4. 60mg of the iron-carbon composite material and 3mg of polyvinylidene fluoride (PVDF) are added into 30mL of N-methyl pyrrolidone, and stirred for 1h at room temperature to prepare primary slurry;
A5. dispersing the primary slurry by using 300mL of ethanol to obtain secondary slurry; and loading the secondary slurry on the surface of the glass fiber membrane in a vacuum filtration mode, and drying in an oven to obtain the iron-based light-heat conversion membrane.
The loading capacity of the iron-based nanowires in the iron-based photothermal conversion film can be adjusted by adjusting the ratio between the area of the glass fiber film and the dosage of the secondary sizing agent, and the loading capacity in the example is 1.0mg/cm 2
Examples 2 to 5 respectively prepare an iron-based photothermal conversion film, and the specific process differs from that of example 1 in that:
in the obtained iron-based photothermal conversion film, the loading amounts of the iron-based nanowires are different, and the specific is that:
example 2 has a loading of 0.6mg/cm 2 The loading of example 3 was 0.8mg/cm 2 The loading of example 4 was 1.2mg/cm 2 The loading of example 5 was 1.4mg/cm 2
Examples 6 to 7 respectively prepare an iron-based photothermal conversion film, and the specific process differs from that of example 1 in that:
in the step A3, the heat preservation temperatures are different, specifically:
the soak temperature for example 6 was 500℃and for example 7 was 700 ℃.
Example 8
The difference between the specific process and the specific process of the embodiment 1 is that:
in the step A3, the obtained product is subjected to heat treatment at 500 ℃ for 2 hours by a muffle furnace (without argon protection and air atmosphere) to obtain nano-linear ferric oxide (marked as Fe) 2 O 3 )。
Example 9
The embodiment provides a photothermal converter, as shown in fig. 1, and specific components and connection relationships are as follows:
an iron-based photothermal conversion film 400, the iron-based photothermal conversion film 400 used in this example is derived from example 1 (also referred to as a photothermal absorption layer); when in use, the iron-based photothermal conversion film 400 faces the light source 500;
a liquid transfer channel 200, wherein the material of the liquid transfer channel 200 is cotton, one end of the liquid transfer channel is in contact with the iron-based photothermal conversion film 400, and the other end of the liquid transfer channel is immersed in the liquid 100 to be treated in the beaker;
the heat insulating layer 300 is made of melamine foam, and is placed on the beaker and parallel to the iron-based photothermal conversion film 400, and is positioned between the upper liquid surface of the liquid 100 to be treated and the iron-based photothermal conversion film 400, and is penetrated by the liquid transmission channel 200.
Embodiments 10 to 16 respectively provide a photothermal converter, which is different from embodiment 9 specifically:
the iron-based photothermal conversion films 400 used in examples 10 to 16 were from examples 2 to 8.
Comparative example 1
This comparative example shows a photothermal conversion film, which differs from example 9 specifically in that:
the iron-based photothermal conversion film 400 in example 9 was replaced with a blank glass fiber film, which was the same as the glass fiber film used in step A5 of example 1.
Comparative example 2 was temporarily free of other solvents such as ethanol, n-propanol, etc.
This comparative example provides a photothermal conversion film, the specific procedure differs from that of example 1 in that:
(1) The method does not comprise the steps A1 to A3;
(2) In step A4, fe/C was replaced with commercial carbon black of equal mass Super-P (designated Super-P).
Comparative example 3
This comparative example produced a photothermal conversion film, the specific procedure being different from example 1 in that:
the following steps are added between the step A3 and the step A4:
and (3) etching the Fe/C nanowire obtained in the step (A3) for 24 hours by adopting 2mol/L hydrochloric acid, and marking as Fe/C-Etch.
And in the subsequent step, fe/C-Etch is used for replacing Fe/C with equal quality.
Comparative example 4
There is provided a photothermal converter, specifically differing from embodiment 9 in that:
the iron-based photothermal conversion film 400 was replaced with the photothermal conversion film obtained in comparative example 2.
Comparative example 5
There is provided a photothermal converter, specifically differing from embodiment 9 in that:
the iron-based photothermal conversion film 400 was replaced with the photothermal conversion film obtained in comparative example 3.
Test examples
This test example first aspect tests the morphology of the iron-based nanowires obtained in example 1 and example 9 by Scanning Electron Microscopy (SEM). The result shows that the iron-carbon nanowire obtained in the embodiment 1 has a longer length of 4-20 mu m and is in clustered tight arrangement; fe obtained in example 9 2 O 3 The length is below 10 mu m; the diameter of the iron-based nanowires obtained in example 1 and example 9 ranges from 200 to 500nm. Therefore, the linear structure of the iron-based nanowire obtained in example 9 is significantly reduced and the aspect ratio is reduced as compared with the iron-based nanowire obtained in example 1. The specific results are shown in fig. 2-3.
The second aspect of this test example tested the evaporation rate of water (pure water as the liquid to be treated) in the photothermal transducers obtained in examples 9 to 13. The results show that in the iron-based photothermal conversion film obtained according to the methods of examples 1 to 5, when the loading amount of the iron-based nanowires was 1.0mg/cm 2 The evaporation rate of pure water was 2.6kg/m at the highest 2 h, the reason is that the membrane pore canal can be blocked by excessive membrane load, so that the transmission of water and gas is influenced, and the evaporation rate is further influenced. The specific test results are shown in fig. 4.
The third aspect of this test example tests the composition of the iron-based nanowires obtained in example 1 and examples 6 to 8. The results of XRD testing showed that: at a sintering temperature of 600 ℃, the crystallinity of the iron-carbon composite is best. The test results are shown in fig. 5; HR-TEM testing showed that the iron-carbon composite showed characteristic lattice fringes of elemental iron, thereby further confirming that iron exists as crystalline elemental iron in the iron-carbon composite. EDS tests show that a significant amount of carbon is also included in the iron-carbon composite. From this, it was confirmed that when the atmosphere obtained in step A3 is an inert gas, the obtained iron-based nanowire is a nanowire-shaped composite material composed of elemental iron and elemental carbon. The XRD pattern of the iron-based nanowires obtained in example 8 was well matched with the standard pattern of iron oxide. The test results are shown in fig. 6.
In the fourth aspect of this test example, absorption spectra of the four photothermal conversion films obtained in example 1, example 8 and comparative examples 2 to 3 under wet conditions were measured. The test results showed that the light-heat conversion films prepared in example 1, example 8 and comparative examples 2 to 3 had absorbance values of 95.72%, 73.95%, 91.44% and 94.15%, respectively, in the spectral range of 280 to 2500 nm. The results show that the photothermal conversion film prepared by taking the nano linear iron-carbon composite material as the light absorption material in the embodiment 1 of the invention has the light absorption capacity of more than 95% under the synergistic effect of the metal plasmon effect and the thermal vibration effect of the carbon material, and is superior to the embodiment 8 which takes the semiconductor non-radiative relaxation effect as the photothermal conversion mechanism and the comparative examples 2 and 3 which take the thermal vibration effect of the pure carbon material as the photothermal conversion mechanism. In example 1 provided by the invention, elemental iron and carbon act synergistically to increase absorbance. The specific test results are shown in fig. 7.
The fifth aspect of the test example tested the photothermal converters obtained in example 9, example 16 and comparative examples 4 to 5 for a temperature change of the photothermal conversion film within 1 hour when the solar interface was used for evaporating pure water; the specific process is as follows: adjusting xenon lamp of the analog light source to ensure that the illumination intensity reaching the surface of the photo-thermal conversion film is 1kW/m 2 The temperature of the film surface was then tested using an infrared gun at 0min, 2min, 10min, 30min and 60min of light, respectively. The four photothermal conversion films were all capable of rapidly increasing temperature within 2min from the start of evaporation, and when 60min was reached, the Fe/C film of example 1 had a maximum film surface temperature of 48.2 ℃ during evaporation, example 8 (Fe 2 O 3 ) In comparative example 4 (Super-P) and comparative example 5 (Fe/C-Etch), the photothermal conversion films were 41.3 ℃, 46.3 ℃ and 44.5 ℃ respectively, which are lower than the Fe/C film, which also explains the reason that the pure water evaporation rate of the Fe/C material is the fastest. Because the Fe/C-Etch film etches away most of Fe metal simple substance, the surface temperature of the film is lower than that of the Fe/C film during evaporation, and the plasmon effect of metal Fe is demonstrated from the side surface, so that the photo-thermal conversion process can be rapidly realized, the evaporation interface obtains higher evaporation temperature, and the evaporation rate is improved. The test results are shown in fig. 8.
Referring to the test means of the fifth aspect of the test example, the weight of the water to be treated at different time points was counted and fitted with 1kW/m 2 Loss of water under illuminationHeavy change curve. The results showed that the pure water evaporation rates (obtained by conversion of the slope of the evaporation curve) of the photothermal transducers prepared in example 9, example 16 and comparative examples 4 to 5 were 0.39 kg/m, respectively 2 h (control), 2.60. 2.60 kg/m 2 h、1.69 kg/m 2 h、2.24kg/m 2 h and 2.15. 2.15 kg/m 2 h, performing H; the photo-thermal conversion water evaporation efficiencies were calculated to be 25.02% (control), 95.65%, 64.2%, 84.59% and 79.68%, respectively; compared with pure water evaporation, when the photothermal converter comprising the iron-based photothermal conversion film provided by the invention is used for solar energy interfacial evaporation water treatment, the evaporation rate of water is respectively improved to 6.7, 4.3, 5.7 and 5.5 times of that of pure water evaporation in example 9, example 16 and comparative examples 4-5; this demonstrates that the combined action of iron and carbon in example 1 can make the light-heat conversion performance of the iron-based light-heat conversion film more prominent. The specific test results are shown in fig. 9.
The purification performance of the photothermal converter obtained in example 9 on methylene blue-containing organic dye wastewater was also tested in this example, specifically, the liquid to be treated was defined as methylene blue-containing organic dye wastewater (concentration: 40 mg/L), and the iron-based photothermal conversion film was subjected to 1kW/m 2 Xenon lamp illumination. The results showed that the absorbance of the obtained liquid after the treatment of the organic dye wastewater containing methylene blue was almost 0, showing an extremely excellent organic dye removal effect. The specific test results are shown in fig. 10.
The performance of the photothermal conversion film obtained in example 9 in treating industrial wastewater containing heavy metal ions was also tested in this example, and in the test process, the iron-based photothermal conversion film received 1kW/m 2 Xenon lamp illumination. The results show that in the treated wastewater, al 3+ 、Ca 2 + 、Co 3+ 、Mg 2+ 、Mn 2+ And Na (Na) + The removal rates of (a) reach 99.97%, 99.61%, 99.70%, 98.37%, 99.99% and 86.07%, respectively, and excellent heavy metal ion removal performance is exhibited. The specific test results are shown in fig. 11.
In conclusion, the iron-based light-heat conversion film provided by the invention has the advantages that due to the special design of the material and the structure of the light-heat conversion material, the light absorption performance and the evaporation performance to solvents such as water are obviously improved, and when the material of the iron-based nanowire is an iron-carbon composite material, the performance is better. Furthermore, the photothermal converter provided by the invention has wide application prospects in water treatment and solvent purification due to the adoption of the iron-based photothermal conversion film.
The embodiments of the present invention have been described in detail with reference to the accompanying drawings, but the present invention is not limited to the above embodiments, and various changes can be made within the knowledge of one of ordinary skill in the art without departing from the spirit of the present invention. Furthermore, embodiments of the invention and features of the embodiments may be combined with each other without conflict.

Claims (10)

1. An iron-based photothermal conversion film, characterized in that the iron-based photothermal conversion film comprises:
a substrate, which is a hydrophilic film;
a photothermal conversion material supported on the substrate surface, the photothermal conversion material comprising an iron-based nanowire;
the preparation method of the iron-based nanowire comprises the following steps:
D1. carrying out solvothermal reaction on a mixture of nitrilotriacetic acid and ferrous salt;
D2. and (3) carrying out heat treatment on the solid reaction product obtained in the step D1.
2. The iron-based photothermal conversion film according to claim 1, wherein the material of the iron-based nanowires comprises at least one of iron oxide and an iron-carbon composite.
3. The iron-based photothermal conversion film according to claim 1, wherein the length of the iron-based nanowire is 4-150 μm; and/or the diameter of the iron-based nanowire is 40-500 nm.
4. The iron-based photothermal conversion film according to claim 1, wherein in step D2, the heat-treated atmosphere comprises at least one of a shielding gas and oxygen; and/or, in the step D2, the temperature of the heat treatment is 500-800 ℃.
5. The iron-based photothermal conversion film according to claim 1, wherein in step D1, the solvent used for the solvothermal reaction comprises water and isopropyl alcohol; and/or, in the solvent, the volume concentration of the isopropanol is 11-15%.
6. The iron-based photothermal conversion film according to claim 1, wherein in step D1, the solvothermal reaction temperature is 100 to 200 ℃.
7. The method for preparing the iron-based photothermal conversion film according to any one of claims 1 to 6, comprising coating a slurry containing the iron-based nanowires on the surface of the substrate and drying.
8. The method of preparing according to claim 7, wherein the slurry further comprises a binder and a solvent; and/or the coating method is at least one of suction filtration, knife coating, spray coating and spin coating.
9. A photothermal converter comprising the iron-based photothermal conversion film according to any one of claims 1 to 6.
10. Use of the photothermal converter according to claim 9 in water treatment and solvent purification.
CN202310864575.7A 2023-07-14 2023-07-14 Iron-based photo-thermal conversion film and preparation method and application thereof Active CN116585909B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202310864575.7A CN116585909B (en) 2023-07-14 2023-07-14 Iron-based photo-thermal conversion film and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202310864575.7A CN116585909B (en) 2023-07-14 2023-07-14 Iron-based photo-thermal conversion film and preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN116585909A true CN116585909A (en) 2023-08-15
CN116585909B CN116585909B (en) 2023-09-29

Family

ID=87604818

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202310864575.7A Active CN116585909B (en) 2023-07-14 2023-07-14 Iron-based photo-thermal conversion film and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN116585909B (en)

Citations (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH11212256A (en) * 1998-01-21 1999-08-06 Konica Corp Image forming material and production of image forming material
CN103361625A (en) * 2012-03-31 2013-10-23 姜辛 Carbon nanofiber membrane photo-thermal converting material and preparation method thereof
US20150353385A1 (en) * 2014-06-09 2015-12-10 King Abdullah University Of Science And Technology Hydrophobic photothermal membranes, devices including the hydrophobic photothermal membranes, and methods for solar desalination
CN107118395A (en) * 2017-06-15 2017-09-01 湖北大学 A kind of carbon-based photothermal conversion film and its preparation method and application and a kind of photothermal conversion device
CN109342420A (en) * 2018-12-07 2019-02-15 上海工程技术大学 Fe3O4The application of@C one-dimensional nano line
CN109715317A (en) * 2016-09-27 2019-05-03 尤尼吉可株式会社 Metal nanometer line
CN110886032A (en) * 2019-11-20 2020-03-17 济南大学 Preparation method of iron-based nanofiber
CN112028052A (en) * 2020-09-18 2020-12-04 西北大学 Preparation method and application of biomass carbon-based Fe monatomic-N doped porous carbon material
CN113790538A (en) * 2021-08-27 2021-12-14 中南大学 Photo-thermal conversion film and preparation method and application thereof
CN114751484A (en) * 2022-05-12 2022-07-15 东北电力大学 Alga removing method of ferroferric oxide photo-thermal nano material
US20220298018A1 (en) * 2021-03-22 2022-09-22 Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences Iron-Carbon Composite Material, Preparation Method Thereof and Use Therefor
US20220390147A1 (en) * 2021-06-03 2022-12-08 National Taiwan University Of Science And Technology High Performance Photothermal Conversion Materials, Membrane, Layer Structure and Applications Thereof
CN115745050A (en) * 2022-11-24 2023-03-07 中山大学 Photo-thermal evaporation and photocatalysis synergistic sewage treatment material and preparation method thereof
CN116119761A (en) * 2022-12-28 2023-05-16 河南科技大学 Iron diselenide/carbon black photo-thermal material, preparation method thereof and seawater evaporation device
CN116143217A (en) * 2023-01-03 2023-05-23 重庆邮电大学 Preparation method of multifunctional light-heat conversion film with semiconductor-metal nanowire structure
CN116285173A (en) * 2023-02-09 2023-06-23 山东大学 Nanoscale Co 2 Preparation and application of C/PTFE (polytetrafluoroethylene) composite photo-thermal material

Patent Citations (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH11212256A (en) * 1998-01-21 1999-08-06 Konica Corp Image forming material and production of image forming material
CN103361625A (en) * 2012-03-31 2013-10-23 姜辛 Carbon nanofiber membrane photo-thermal converting material and preparation method thereof
US20150353385A1 (en) * 2014-06-09 2015-12-10 King Abdullah University Of Science And Technology Hydrophobic photothermal membranes, devices including the hydrophobic photothermal membranes, and methods for solar desalination
CN109715317A (en) * 2016-09-27 2019-05-03 尤尼吉可株式会社 Metal nanometer line
CN107118395A (en) * 2017-06-15 2017-09-01 湖北大学 A kind of carbon-based photothermal conversion film and its preparation method and application and a kind of photothermal conversion device
CN109342420A (en) * 2018-12-07 2019-02-15 上海工程技术大学 Fe3O4The application of@C one-dimensional nano line
CN110886032A (en) * 2019-11-20 2020-03-17 济南大学 Preparation method of iron-based nanofiber
CN112028052A (en) * 2020-09-18 2020-12-04 西北大学 Preparation method and application of biomass carbon-based Fe monatomic-N doped porous carbon material
US20220298018A1 (en) * 2021-03-22 2022-09-22 Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences Iron-Carbon Composite Material, Preparation Method Thereof and Use Therefor
US20220390147A1 (en) * 2021-06-03 2022-12-08 National Taiwan University Of Science And Technology High Performance Photothermal Conversion Materials, Membrane, Layer Structure and Applications Thereof
CN113790538A (en) * 2021-08-27 2021-12-14 中南大学 Photo-thermal conversion film and preparation method and application thereof
CN114751484A (en) * 2022-05-12 2022-07-15 东北电力大学 Alga removing method of ferroferric oxide photo-thermal nano material
CN115745050A (en) * 2022-11-24 2023-03-07 中山大学 Photo-thermal evaporation and photocatalysis synergistic sewage treatment material and preparation method thereof
CN116119761A (en) * 2022-12-28 2023-05-16 河南科技大学 Iron diselenide/carbon black photo-thermal material, preparation method thereof and seawater evaporation device
CN116143217A (en) * 2023-01-03 2023-05-23 重庆邮电大学 Preparation method of multifunctional light-heat conversion film with semiconductor-metal nanowire structure
CN116285173A (en) * 2023-02-09 2023-06-23 山东大学 Nanoscale Co 2 Preparation and application of C/PTFE (polytetrafluoroethylene) composite photo-thermal material

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
HUANHUAN LI等: "In situ synthesis of hierarchical mesoporous Fe3O4@C nanowires derived from coordination polymers for high-performance lithium-ion batteries", 《RSC ADVANCES》, no. 4, pages 51960 - 51965 *
XUEBO LIU等: "A two-dimensional G-CoP/N, P-co-doped carbon nanowire electrode for the simultaneous determination of hydroquinone and catechol in domestic wastewater", 《ANALYTICA CHIMICA ACTA》, no. 1210, pages 339871 *
毛停停等: "面向水处理与有机溶剂回收的太阳能界面蒸发系统与材料", 《化工进展》, vol. 42, no. 1, pages 178 - 193 *

Also Published As

Publication number Publication date
CN116585909B (en) 2023-09-29

Similar Documents

Publication Publication Date Title
CN108325555B (en) Nitrogen self-doped graphitized carbon nitride nanosheet photocatalyst and preparation method and application thereof
CN110152710B (en) High-stability TiO2nanobelt-RGO-porous carbon nitride composite photocatalyst and preparation method thereof
CN108355669B (en) Magnetic nano onion carbon loaded Bi2WO6Photocatalyst and preparation method and application thereof
CN111453804A (en) Preparation method of iron-doped graphite-like phase carbon nitride/graphene multifunctional nano composite material
CN113617351A (en) Graphite-like phase carbon nitride/graphene oxide composite aerogel and method
CN108339544B (en) Photocatalyst/super-hydrophobic membrane composite material modified by fullerene carboxyl derivative
CN110756223A (en) Adsorption catalysis composite material and application thereof in pollutant treatment
CN111389439A (en) Preparation method of BN quantum dot combined photocatalytic composite fiber
CN113506904B (en) Proton exchange membrane and preparation method and application thereof
CN116585909B (en) Iron-based photo-thermal conversion film and preparation method and application thereof
Wang et al. Fabrication of nitrogen-deficient gC 3 N 4 nanosheets via an acetaldehyde-assisted hydrothermal route and their high photocatalytic performance for H 2 O 2 production and Cr (vi) reduction
CN107349951B (en) CuO/g-C3N4Preparation method of capillary-like nano-composite
CN117205740A (en) Carbon dioxide-containing waste gas treatment system and treatment method
CN108745405B (en) Carbon nitride/nitrogen doped hollow mesoporous carbon/bismuth trioxide ternary Z-shaped photocatalyst and preparation method thereof
CN113790538B (en) Photo-thermal conversion film and preparation method and application thereof
CN116196944A (en) Preparation method and application of biomass nitrogen-doped carbon quantum dot coupled ultrathin BiOBr nano-sheet composite photocatalyst
CN114014316B (en) Composite photo-thermal material based on titanium carbide and preparation method thereof
CN112973757B (en) Bismuth vanadate quantum dot/RGO/graphite phase carbon nitride ternary composite photocatalyst and preparation method thereof
CN113145099B (en) Bismuth-loaded bismuth titanate/calcium titanate composite photocatalyst, and preparation method and application thereof
CN107876073A (en) Core shell structure g C3N4The preparation method of/MCNTs/BiOI composites
CN110624532B (en) TiO 22-BiVO4-graphene ternary composite photocatalytic material and preparation method thereof
CN113559856A (en) Preparation method of barium titanate/silver iodate heterojunction photocatalyst
CN112844375A (en) MnO for removing nitrogen oxide2/Bi2WO6Heterojunction photocatalyst and preparation method thereof
CN113135558A (en) Photothermal material based on porous carbon spheres and preparation method thereof
CN110918104A (en) Ternary heterojunction graphene-bismuth oxide/bismuth oxyhalide visible light photocatalyst and preparation method thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant