CN113649052B - Graphite-phase carbon nitride-based photocatalytic composite material and preparation and application thereof - Google Patents
Graphite-phase carbon nitride-based photocatalytic composite material and preparation and application thereof Download PDFInfo
- Publication number
- CN113649052B CN113649052B CN202111007738.7A CN202111007738A CN113649052B CN 113649052 B CN113649052 B CN 113649052B CN 202111007738 A CN202111007738 A CN 202111007738A CN 113649052 B CN113649052 B CN 113649052B
- Authority
- CN
- China
- Prior art keywords
- composite material
- powder
- graphite
- carbon nitride
- phase carbon
- 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.)
- Active
Links
- 230000001699 photocatalysis Effects 0.000 title claims abstract description 55
- 239000002131 composite material Substances 0.000 title claims abstract description 45
- JMANVNJQNLATNU-UHFFFAOYSA-N oxalonitrile Chemical compound N#CC#N JMANVNJQNLATNU-UHFFFAOYSA-N 0.000 title claims abstract description 35
- 238000002360 preparation method Methods 0.000 title claims abstract description 12
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 claims abstract description 78
- ZMXDDKWLCZADIW-UHFFFAOYSA-N N,N-Dimethylformamide Chemical compound CN(C)C=O ZMXDDKWLCZADIW-UHFFFAOYSA-N 0.000 claims abstract description 58
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 52
- CWQXQMHSOZUFJS-UHFFFAOYSA-N molybdenum disulfide Chemical compound S=[Mo]=S CWQXQMHSOZUFJS-UHFFFAOYSA-N 0.000 claims abstract description 45
- 229910052982 molybdenum disulfide Inorganic materials 0.000 claims abstract description 45
- 150000003839 salts Chemical class 0.000 claims abstract description 38
- 239000007788 liquid Substances 0.000 claims abstract description 36
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical compound [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 claims abstract description 32
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 claims abstract description 32
- 238000006243 chemical reaction Methods 0.000 claims abstract description 32
- 239000006185 dispersion Substances 0.000 claims abstract description 32
- 239000000843 powder Substances 0.000 claims abstract description 31
- 238000000034 method Methods 0.000 claims abstract description 27
- YUKQRDCYNOVPGJ-UHFFFAOYSA-N thioacetamide Chemical compound CC(N)=S YUKQRDCYNOVPGJ-UHFFFAOYSA-N 0.000 claims abstract description 24
- DLFVBJFMPXGRIB-UHFFFAOYSA-N thioacetamide Natural products CC(N)=O DLFVBJFMPXGRIB-UHFFFAOYSA-N 0.000 claims abstract description 24
- 238000010298 pulverizing process Methods 0.000 claims abstract description 23
- 239000001267 polyvinylpyrrolidone Substances 0.000 claims abstract description 22
- 235000013855 polyvinylpyrrolidone Nutrition 0.000 claims abstract description 22
- 229920000036 polyvinylpyrrolidone Polymers 0.000 claims abstract description 22
- 238000000926 separation method Methods 0.000 claims abstract description 17
- 239000001103 potassium chloride Substances 0.000 claims abstract description 16
- 235000011164 potassium chloride Nutrition 0.000 claims abstract description 16
- 239000011780 sodium chloride Substances 0.000 claims abstract description 16
- JDSHMPZPIAZGSV-UHFFFAOYSA-N melamine powder Natural products NC1=NC(N)=NC(N)=N1 JDSHMPZPIAZGSV-UHFFFAOYSA-N 0.000 claims abstract description 14
- ZQPPMHVWECSIRJ-KTKRTIGZSA-N oleic acid Chemical compound CCCCCCCC\C=C/CCCCCCCC(O)=O ZQPPMHVWECSIRJ-KTKRTIGZSA-N 0.000 claims abstract description 14
- WRIDQFICGBMAFQ-UHFFFAOYSA-N (E)-8-Octadecenoic acid Natural products CCCCCCCCCC=CCCCCCCC(O)=O WRIDQFICGBMAFQ-UHFFFAOYSA-N 0.000 claims abstract description 13
- LQJBNNIYVWPHFW-UHFFFAOYSA-N 20:1omega9c fatty acid Natural products CCCCCCCCCCC=CCCCCCCCC(O)=O LQJBNNIYVWPHFW-UHFFFAOYSA-N 0.000 claims abstract description 13
- QSBYPNXLFMSGKH-UHFFFAOYSA-N 9-Heptadecensaeure Natural products CCCCCCCC=CCCCCCCCC(O)=O QSBYPNXLFMSGKH-UHFFFAOYSA-N 0.000 claims abstract description 13
- ZQPPMHVWECSIRJ-UHFFFAOYSA-N Oleic acid Natural products CCCCCCCCC=CCCCCCCCC(O)=O ZQPPMHVWECSIRJ-UHFFFAOYSA-N 0.000 claims abstract description 13
- 239000005642 Oleic acid Substances 0.000 claims abstract description 13
- QXJSBBXBKPUZAA-UHFFFAOYSA-N isooleic acid Natural products CCCCCCCC=CCCCCCCCCC(O)=O QXJSBBXBKPUZAA-UHFFFAOYSA-N 0.000 claims abstract description 13
- 238000002156 mixing Methods 0.000 claims abstract description 13
- 239000002135 nanosheet Substances 0.000 claims abstract description 11
- 238000006068 polycondensation reaction Methods 0.000 claims abstract description 8
- 238000003756 stirring Methods 0.000 claims abstract description 7
- 238000010335 hydrothermal treatment Methods 0.000 claims abstract description 4
- 239000000047 product Substances 0.000 claims description 79
- 239000007787 solid Substances 0.000 claims description 25
- 239000002244 precipitate Substances 0.000 claims description 24
- 238000001035 drying Methods 0.000 claims description 19
- 238000000227 grinding Methods 0.000 claims description 18
- 239000006228 supernatant Substances 0.000 claims description 12
- 238000005406 washing Methods 0.000 claims description 11
- 238000001816 cooling Methods 0.000 claims description 9
- 238000010438 heat treatment Methods 0.000 claims description 5
- 238000005119 centrifugation Methods 0.000 claims description 4
- 238000001704 evaporation Methods 0.000 claims description 2
- 239000000463 material Substances 0.000 abstract description 20
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 abstract description 8
- 229910002804 graphite Inorganic materials 0.000 abstract description 8
- 239000010439 graphite Substances 0.000 abstract description 8
- 238000011160 research Methods 0.000 abstract description 2
- 239000013049 sediment Substances 0.000 abstract description 2
- 239000008367 deionised water Substances 0.000 description 48
- 229910021641 deionized water Inorganic materials 0.000 description 48
- 239000000203 mixture Substances 0.000 description 31
- 239000012071 phase Substances 0.000 description 26
- 239000011941 photocatalyst Substances 0.000 description 16
- 238000002390 rotary evaporation Methods 0.000 description 16
- 238000009210 therapy by ultrasound Methods 0.000 description 16
- 230000015556 catabolic process Effects 0.000 description 14
- 238000006731 degradation reaction Methods 0.000 description 14
- 239000010410 layer Substances 0.000 description 14
- 238000003760 magnetic stirring Methods 0.000 description 13
- -1 hydrocarbon oxygen free radical Chemical class 0.000 description 12
- 230000006872 improvement Effects 0.000 description 11
- 239000002904 solvent Substances 0.000 description 11
- 230000008569 process Effects 0.000 description 10
- 238000007146 photocatalysis Methods 0.000 description 9
- RPACBEVZENYWOL-XFULWGLBSA-M sodium;(2r)-2-[6-(4-chlorophenoxy)hexyl]oxirane-2-carboxylate Chemical compound [Na+].C=1C=C(Cl)C=CC=1OCCCCCC[C@]1(C(=O)[O-])CO1 RPACBEVZENYWOL-XFULWGLBSA-M 0.000 description 9
- 230000001276 controlling effect Effects 0.000 description 8
- 230000000694 effects Effects 0.000 description 8
- 239000011812 mixed powder Substances 0.000 description 8
- 239000004570 mortar (masonry) Substances 0.000 description 8
- 229920001343 polytetrafluoroethylene Polymers 0.000 description 8
- 239000004810 polytetrafluoroethylene Substances 0.000 description 8
- PYWVYCXTNDRMGF-UHFFFAOYSA-N rhodamine B Chemical compound [Cl-].C=12C=CC(=[N+](CC)CC)C=C2OC2=CC(N(CC)CC)=CC=C2C=1C1=CC=CC=C1C(O)=O PYWVYCXTNDRMGF-UHFFFAOYSA-N 0.000 description 8
- 229940043267 rhodamine b Drugs 0.000 description 8
- 239000004065 semiconductor Substances 0.000 description 8
- 238000007873 sieving Methods 0.000 description 8
- 239000003054 catalyst Substances 0.000 description 7
- 230000000630 rising effect Effects 0.000 description 7
- 230000007480 spreading Effects 0.000 description 7
- 238000003892 spreading Methods 0.000 description 7
- 239000007789 gas Substances 0.000 description 6
- 239000000126 substance Substances 0.000 description 6
- 238000012360 testing method Methods 0.000 description 6
- 239000003344 environmental pollutant Substances 0.000 description 5
- 230000031700 light absorption Effects 0.000 description 5
- 231100000719 pollutant Toxicity 0.000 description 5
- 238000005303 weighing Methods 0.000 description 5
- 239000000969 carrier Substances 0.000 description 4
- 230000000593 degrading effect Effects 0.000 description 4
- 230000004048 modification Effects 0.000 description 4
- 238000012986 modification Methods 0.000 description 4
- 238000013032 photocatalytic reaction Methods 0.000 description 4
- 239000011229 interlayer Substances 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 238000002844 melting Methods 0.000 description 3
- 230000008018 melting Effects 0.000 description 3
- 238000006116 polymerization reaction Methods 0.000 description 3
- 150000003254 radicals Chemical class 0.000 description 3
- 230000006798 recombination Effects 0.000 description 3
- 238000005215 recombination Methods 0.000 description 3
- 239000002356 single layer Substances 0.000 description 3
- 230000001502 supplementing effect Effects 0.000 description 3
- 239000004215 Carbon black (E152) Substances 0.000 description 2
- ATJFFYVFTNAWJD-UHFFFAOYSA-N Tin Chemical compound [Sn] ATJFFYVFTNAWJD-UHFFFAOYSA-N 0.000 description 2
- 238000002441 X-ray diffraction Methods 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 230000005540 biological transmission Effects 0.000 description 2
- 150000001732 carboxylic acid derivatives Chemical class 0.000 description 2
- 238000013329 compounding Methods 0.000 description 2
- 239000013078 crystal Substances 0.000 description 2
- 239000003814 drug Substances 0.000 description 2
- 229940079593 drug Drugs 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 229930195733 hydrocarbon Natural products 0.000 description 2
- 238000005286 illumination Methods 0.000 description 2
- 239000007791 liquid phase Substances 0.000 description 2
- 239000002086 nanomaterial Substances 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 238000000634 powder X-ray diffraction Methods 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 238000001878 scanning electron micrograph Methods 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 238000002336 sorption--desorption measurement Methods 0.000 description 2
- 239000004094 surface-active agent Substances 0.000 description 2
- 229910052723 transition metal Inorganic materials 0.000 description 2
- 229910052724 xenon Inorganic materials 0.000 description 2
- FHNFHKCVQCLJFQ-UHFFFAOYSA-N xenon atom Chemical compound [Xe] FHNFHKCVQCLJFQ-UHFFFAOYSA-N 0.000 description 2
- LLQPHQFNMLZJMP-UHFFFAOYSA-N Fentrazamide Chemical compound N1=NN(C=2C(=CC=CC=2)Cl)C(=O)N1C(=O)N(CC)C1CCCCC1 LLQPHQFNMLZJMP-UHFFFAOYSA-N 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- OWYWGLHRNBIFJP-UHFFFAOYSA-N Ipazine Chemical group CCN(CC)C1=NC(Cl)=NC(NC(C)C)=N1 OWYWGLHRNBIFJP-UHFFFAOYSA-N 0.000 description 1
- 229920000877 Melamine resin Polymers 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- OUUQCZGPVNCOIJ-UHFFFAOYSA-M Superoxide Chemical compound [O-][O] OUUQCZGPVNCOIJ-UHFFFAOYSA-M 0.000 description 1
- 239000011358 absorbing material Substances 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000006978 adaptation Effects 0.000 description 1
- 238000004887 air purification Methods 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000002800 charge carrier Substances 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 230000008878 coupling Effects 0.000 description 1
- 238000010168 coupling process Methods 0.000 description 1
- 238000005859 coupling reaction Methods 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 239000002019 doping agent Substances 0.000 description 1
- 239000000975 dye Substances 0.000 description 1
- 238000004299 exfoliation Methods 0.000 description 1
- 230000002349 favourable effect Effects 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 125000002887 hydroxy group Chemical group [H]O* 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 239000000138 intercalating agent Substances 0.000 description 1
- 238000009830 intercalation Methods 0.000 description 1
- 230000002687 intercalation Effects 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 230000005012 migration Effects 0.000 description 1
- 238000013508 migration Methods 0.000 description 1
- 239000011259 mixed solution Substances 0.000 description 1
- 239000002052 molecular layer Substances 0.000 description 1
- 239000002114 nanocomposite Substances 0.000 description 1
- 239000002064 nanoplatelet Substances 0.000 description 1
- 125000004433 nitrogen atom Chemical group N* 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 230000033116 oxidation-reduction process Effects 0.000 description 1
- 239000003973 paint Substances 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 239000002243 precursor Substances 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 238000001228 spectrum Methods 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 238000010301 surface-oxidation reaction Methods 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 150000003624 transition metals Chemical class 0.000 description 1
- 238000000870 ultraviolet spectroscopy Methods 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J27/00—Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
- B01J27/24—Nitrogen compounds
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8668—Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J35/00—Catalysts, in general, characterised by their form or physical properties
- B01J35/30—Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
- B01J35/39—Photocatalytic properties
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Materials Engineering (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Catalysts (AREA)
Abstract
The invention discloses a graphite phase carbon nitride-based photocatalytic composite material and preparation and application thereof, comprising the steps of dissolving polyvinylpyrrolidone into N, N-dimethylformamide containing oleic acid, and adding molybdenum disulfide powder; stirring, ultrasonic pulverizing, and centrifuging to obtain MoS 2 A nanosheet dispersion; mixing melamine powder, thioacetamide and sodium chloride/potassium chloride, and performing thermal polycondensation reaction to obtain a dark yellow product, namely the S-doped g-C prepared by molten salt 3 N 4 The method comprises the steps of carrying out a first treatment on the surface of the S doping g-C 3 N 4 Adding water, ultrasonic pulverizing, centrifuging to obtain few-layer modified g-C 3 N 4 A powder; taking few layers of modified g-C 3 N 4 Powder and MoS 2 Mixing the nanosheet dispersion liquid, preparing a mixed liquid, performing hydrothermal treatment on the mixed liquid, performing solid-liquid separation on the mixed liquid after full reaction to obtain lower-layer sediment, and obtaining MoS 2 /g‑C 3 N 4 A photocatalytic composite material. The application of the method can effectively control the harm of formaldehyde to human bodies in the aspect of formaldehyde treatment, and widens the research range of photocatalytic materials.
Description
Technical Field
The invention relates to a composite photocatalyst, in particular to a graphite-phase carbon nitride-based photocatalytic composite material and preparation and application thereof.
Background
The VOC of the indoor paint furniture volatilizes slowly, which has bad influence on the living environment of people and seriously damages the healthy life of people. The most typical indoor air contaminant is formaldehyde. On one hand, the pollution of formaldehyde needs to be controlled by reducing the generation of the source, controlling the content of pollutants such as formaldehyde in materials in the production and processing process, developing novel pollution-free materials, prohibiting products containing high harmful substances from entering the market, and on the other hand, improving the pollutant removal efficiency. Currently, ventilation, filtration and adsorption are the main means of purifying indoor pollutants, but cannot thoroughly degrade the pollutants. Photocatalytic means is one of the most effective methods for degrading formaldehyde in a room. According to the photocatalysis mechanism, when the photocatalyst is irradiated, generated photo-generated electrons and photo-generated holes can generate hydroxyl free radicals (OH) and superoxide free radicals (O) in the surface oxidation process 2 - ) Activity OH and O 2 - Together with the oxidation, OH can obtain hydrogen in formaldehyde to generate hydrocarbon oxygen free radical (CHO), and then the hydrocarbon oxygen free radical is further oxidized into carboxylic acid, and the carboxylic acid is finally oxidized and decomposed to generate CO 2 And H 2 O. The self-purification of indoor air can be realized through the reaction, and the aim of effectively degrading formaldehyde can be achieved if a heterojunction photocatalyst with high activity is used.
The existing photocatalyst for treating formaldehyde pollution has certain effect, but most of materials used comprise heavy metal substances or equipment requirements are high, so that the photocatalyst is high in price. Therefore, the preparation of a photocatalyst which is cheaper, has low cost and simple process and achieves the best performance is the key of mass production.
Disclosure of Invention
The invention aims to provide a graphite phase carbon nitride base (g-C 3 N 4 Base) photocatalytic composite material, and its preparation and application. The g-C 3 N 4 The base composite photocatalyst can realize the effective separation of photo-generated electron hole pairs, promote the improvement of the photocatalysis efficiency, and further enhance the formaldehyde degradation performance.
The technical scheme adopted by the invention is as follows:
the preparation method of the graphite-phase carbon nitride-based photocatalytic composite material comprises the following steps:
dissolving polyvinylpyrrolidone into N, N-dimethylformamide containing oleic acid, and adding molybdenum disulfide powder; stirring, ultrasonic pulverizing, centrifuging, and washing the supernatant to obtain water-dispersed MoS 2 A nanosheet dispersion;
mixing melamine powder, thioacetamide and sodium chloride/potassium chloride, and performing thermal polycondensation reaction to obtain a dark yellow product, namely the S-doped g-C prepared by molten salt 3 N 4 ;
S doping g-C 3 N 4 Adding water, ultrasonic pulverizing, centrifuging, collecting upper dispersion, rotary evaporating, collecting lower solid, drying, and grinding to obtain few modified g-C 3 N 4 A powder;
taking few layers of modified g-C 3 N 4 Powder and MoS 2 Mixing the nanosheet dispersion liquid, preparing a mixed liquid, performing hydrothermal treatment on the mixed liquid, performing solid-liquid separation on the mixed liquid after full reaction to obtain lower-layer sediment, and obtaining MoS 2 /g-C 3 N 4 A photocatalytic composite material.
As a further improvement of the invention, the mass ratio of polyvinylpyrrolidone, oleic acid and molybdenum disulfide powder is 1:1:1.
as a further improvement of the invention, the thioacetamide is added in an amount of not more than 20% by weight of the total mass of melamine powder and thioacetamide.
As a further improvement of the invention, the mass ratio of Na salt to K salt in the sodium chloride/potassium chloride is 9:11.
As a further improvement of the present invention, the conditions of the thermal polycondensation reaction are:
heating to 550 ℃ from 120min, heating rate is 4-6 ℃/min, and reacting for 150-200 min at 550 ℃ under constant temperature.
As a further improvement of the invention, the hydrothermal condition is 130-150 ℃, and the reaction is carried out for 10-13 h and then the reaction product is naturally cooled.
As an approach to the inventionOne-step improvement, the few-layer modified g-C 3 N 4 Powder and MoS 2 The solid-liquid ratio of the nano-sheet dispersion liquid is 1g/5-20ml.
As a further improvement of the invention, the ultrasonic crushing is processed by an ultrasonic cell crusher, the temperature of the system is kept at 50 ℃ during the processing, and the ultrasonic is accumulated for 10 hours;
the rotational speed of the centrifugation is 5000rpm, and the centrifugation is carried out for 10min.
A preparation method of a graphite-phase carbon nitride-based photocatalytic composite material is provided, and the graphite-phase carbon nitride-based photocatalytic composite material is prepared by the method.
The graphite-phase carbon nitride-based photocatalytic composite material prepared by the method is applied to formaldehyde pollution treatment.
The invention has the following advantages:
the g-C 3 N 4 The base composite photocatalyst directly adjusts the main catalyst g-C through element doping 3 N 4 And adjusting g-C using a salt melt having a higher melting point 3 N 4 And (3) the polymerization process of the polymer increases the light absorption range and improves the crystallinity. And then, the two different semiconductors are combined, and generated photo-generated carriers can be separated due to the characteristic that electrons spontaneously flow to a lower potential under the irradiation of light, and holes can be transferred to the semiconductor with the lower potential, so that the effective separation of photo-generated electron-hole pairs can be realized, the improvement of the photo-catalytic efficiency is promoted, and the formaldehyde degradation performance is further enhanced. The invention discloses a graphite-phase carbon nitride-based photocatalytic composite material by utilizing element doping, molten salt adjustment, liquid phase stripping and heterojunction compounding methods. Compared with other photocatalysts applied at present, the prepared graphite-phase carbon nitride-based photocatalytic composite material has the advantages that equipment, process and medicines are low in cost, and the optimal performance is achieved at the same time. By reacting g-C 3 N 4 The modification of the light-absorbing material can expand the light-absorbing range and increase the specific surface area, and the light utilization rate is obviously improved. Meanwhile, a 2D-2D heterojunction construction mode is adopted to modify g-C 3 N 4 As a main catalyst, moS 2 As a cocatalyst, electrons can be rapidly transferred through an interface of chemical bond connection, and the method is improvedThe flow direction of electrons and holes is changed, the recombination probability of photo-generated carriers is greatly reduced, and the formaldehyde removal efficiency is effectively improved.
Drawings
FIG. 1 SEM image (2 μm) of a graphite-phase carbon nitride-based photocatalytic composite material obtained in example 2;
FIG. 2 is an XRD pattern of the graphite-phase carbon nitride-based photocatalytic composite material obtained in example 2;
FIG. 3 degradation RhB properties of the graphite-phase carbon nitride-based photocatalytic composite material obtained in example 2;
FIG. 4 formaldehyde degrading properties of the graphite phase carbon nitride based photocatalytic composite material obtained in example 2.
Detailed Description
The technical solutions in the embodiments of the present invention will be clearly and completely described below. It will be apparent that the described embodiments are only some, but not all, embodiments of the invention. All other embodiments, which can be made by those skilled in the art based on the embodiments of the invention without making any inventive effort, are intended to be within the scope of the invention.
Graphite phase carbon nitride material (g-C) 3 N 4 ) Is a typical nonmetallic semiconductor material, and has excellent thermal conductivity and thermal stability, and a proper forbidden bandwidth can enable the material to respond under the condition of visible light, so the material is attractive in various fields as a new-generation semiconductor material, and is expected to become a high-efficiency sustainable photocatalyst. However, due to the larger interlayer spacing (0.67 nm), the transfer between the photo-generated electron layers is limited, the electron quantity transferred to the surface of the material is reduced, and meanwhile, the carrier transmission capability is poor due to low conductivity, so that the photo-catalytic reaction and application of the material are restricted. Thus, g-C is required 3 N 4 Effective modification is carried out, the recombination rate of photo-generated electron-hole pairs is reduced, and the photocatalytic reaction activity is improved.
The invention aims to provide a preparation method of a graphite-phase carbon nitride-based photocatalytic composite material. The g-C 3 N 4 The base composite photocatalyst directly adjusts the main catalyst g-C through element doping 3 N 4 And adjusting g-C using a salt melt having a higher melting point 3 N 4 And (3) the polymerization process of the polymer increases the light absorption range and improves the crystallinity. And then, the two different semiconductors are combined, and generated photo-generated carriers can be separated due to the characteristic that electrons spontaneously flow to a lower potential under the irradiation of light, and holes can be transferred to the semiconductor with the lower potential, so that the effective separation of photo-generated electron-hole pairs can be realized, the improvement of the photo-catalytic efficiency is promoted, and the formaldehyde degradation performance is further enhanced.
The invention relates to a graphite phase carbon nitride based photocatalysis composite material, which uses nonmetallic element doping and salt melt to obtain original g-C 3 N 4 Modified and combined with another semiconductor material, the activity of degrading formaldehyde by photocatalysis is effectively enhanced.
Because the thermal polycondensation method has simple process, is easy to operate and suitable for mass production, and simultaneously obtains a sample with better crystallinity, the thermal polycondensation method is very suitable for the application of the sample, so the thermal polycondensation method is selected to prepare the g-C 3 N 4 A material. The element doping is an effective method for directly adjusting the energy band structure, and can be used for g-C 3 N 4 The mesoheptazine ring and the electronic structure are engineered. The relatively low-cost nonmetallic element S is selected as the doping agent, and the doping of the nonmetallic element S can replace g-C preferentially 3 N 4 And nitrogen atoms at the edge of the middle heptazine unit expand the visible light absorption range and enhance the oxidation-reduction capability in the photocatalytic reaction. And adjusting g-C using NaCl/KCl mixed salt melt with higher melting point 3 N 4 Ensuring active polyheptanoimide as g-C 3 N 4 The main component and the crystallinity are improved.
The few-layer nano material is used in the field of photocatalysis, and because of the greatly improved specific surface area, more edge active sites can be obtained, the utilization efficiency of visible light is enhanced, and the photocatalysis effect is improved. Transition metal sulfides (TMDC) are widely used as typical 2D layered materials in storage, catalysis, sensing and other electrochemical devices due to their attractive chemical and electrochemical properties, molybdenum disulfide (MoS 2 ) Is typical of transition metal sulfidesRepresentative of the type. Nanoscale MoS 2 Has a variable energy band layered structure, so that the material has photocatalytic activity under visible light, and is used as a nano material, and is single-layer MoS 2 The specific surface area is large, more photoelectron active sites can be provided, the catalytic activity of the photocatalyst is enhanced to adsorb more reactant molecules, and the photocatalyst becomes a very advantageous photocatalyst. In addition, a single layer MoS 2 The forbidden band width is about 1.90eV, the energy band difference is equal to the sum of light and g-C 3 N 4 Is very suitable as g-C 3 N 4 Is a catalyst promoter. It is combined with g-C 3 N 4 The MoS is formed by chemical bond connection easily in the process of compounding at high temperature and high pressure 2 /g-C 3 N 4 The binary nanocomposite can effectively enhance visible light absorption. After binding at g-C 3 N 4 The photoelectrons excited by the upper part are firstly transferred to MoS 2 On the monolayer, the catalyst migrates to the surface of the material to react with pollutants, and the process prevents the combination of photo-generated electrons and holes on the catalyst, so that the photocatalytic capability is stronger, and the photocatalytic efficiency of organic pollutants and air purification is effectively improved.
To realize MoS 2 Application of thin layer in large-scale photocatalysis field, high-quality and high-efficiency preparation of few-layer MoS 2 Particularly critical. Liquid phase exfoliation has been common for layered materials, but the application of ultrasonic operations with the direct addition of materials to the corresponding solvents often does not provide the desired results. In general, whether the polarity of the solvent matches that of the material directly affects the degree of dispersion and stability. In addition, the addition of surfactants and intercalating agents also greatly increases the nanoplatelet yield and significantly increases the dispersion stability. By comparison with MoS 2 DMF with equivalent surface energy is used as a solvent, and the quality and the concentration of dispersion liquid of the prepared nano-sheet are improved in a mode of combining a micromolecular intercalation agent and a macromolecular surfactant.
The graphite phase carbon nitride-based photocatalytic composite material is characterized by comprising the following steps of:
(1) 0.25g polyvinylpyrrolidone (PVP) was dissolved in 50ml N, N-Dimethylformamide (DMF) containing 0.25g oleic acid0.25g of molybdenum disulfide (MoS 2 ) And (3) powder. The mixture is stirred for 20min by magnetic force and is subjected to ultrasonic treatment for 20min to be uniformly mixed, and then the mixture is transferred to an ultrasonic cell grinder for ultrasonic pulse stripping, so that the system temperature is kept at 50 ℃ for accumulated ultrasonic treatment for 10h. Centrifuging the mixture at 5000rpm for 10min after pulverizing, and collecting supernatant 2 A nanosheet dispersion. The dispersion was washed twice with DMF to remove excess PVP and oleic acid, and deionized water (H) was used by rotary evaporation 2 O) replacing the original solvent DMF twice to obtain water-dispersed MoS 2 A nanosheet dispersion.
(2) Firstly, weighing 3-5g of melamine powder, washing with deionized water and filtering to remove the influences of soluble impurities and easily-decomposed substances in the precursor on a sample. Oven dried at 80deg.C and triturated, then 0-2g Thioacetamide (TAA) was added to give a total of 5g with melamine. Meanwhile, 10g of sodium chloride/potassium chloride (NaCI/KCI) is added as mixed molten salt (the mass ratio of Na salt to K salt is controlled to be 9:11), the mixed molten salt is mixed and ground for 30min by using a mortar, poured into a 50ml crucible with a cover, the mixed powder is tiled in the crucible, then placed into a muffle furnace for 120min to be heated to 550 ℃ (the heating rate is 4-6 ℃/min), and reacted for 150-200 min at constant temperature, and cooled along with the furnace, so that a dark yellow product is obtained. Subsequently, the milled product was dispersed in deionized water to dissolve the salt, and then filtered, and the salt was washed off three times repeatedly. Drying in oven at 50deg.C, grinding, sieving to obtain dark yellow powder which is S-doped g-C prepared from molten salt 3 N 4 。
(3) 1g of the modified g-C as described above was weighed out 3 N 4 Placed in a beaker containing 500ml deionized water and stirred magnetically for 20min to mix well. Then, an ultrasonic cell grinder is adopted to carry out ultrasonic pulse stripping, so that the system temperature is kept at 50 ℃ and accumulated ultrasonic is carried out for 10 hours. Centrifuging the mixture at 5000rpm for 10min after pulverizing, and collecting supernatant as few-layer g-C 3 N 4 Removing water from the dispersion by rotary evaporation, collecting lower layer solid, drying and grinding to obtain few modified g-C 3 N 4 And (3) powder.
Weighing 0.5g of treated few-layer modified g-C 3 N 4 Powder and 2.5-10mI the MoS described above 2 The nano dispersion is placed in a 100ml polytetrafluoroethylene lining reaction kettle, 45-52.5ml deionized water is added, and then magnetic stirring is carried out for 30min. Carrying out hydrothermal treatment on the mixed solution, putting the reaction kettle into a constant temperature oven with the temperature of 130-150 ℃, reacting for 10-13 h, and naturally cooling. Subsequently, the mixed liquid in the reaction vessel was subjected to solid-liquid separation using a centrifuge to obtain a lower precipitate. Washing the solid precipitate with deionized water for several times, and drying in oven at 50deg.C for 12 hr to obtain MoS 2 /g-C 3 N 4 A photocatalytic composite material.
The graphite-phase carbon nitride-based photocatalytic composite material prepared by the method can be used as a high-efficiency photocatalyst to be applied to formaldehyde pollution treatment.
The graphite phase carbon nitride based photocatalysis composite material is prepared by doping thioacetamide into modified g-C 3 N 4 And regulating the polymerization process through a sodium chloride/potassium chloride mixed molten salt body, and simultaneously stripping the mixed molten salt body into a two-dimensional structure to be compounded with a few layers of molybdenum disulfide, so as to prepare a heterojunction interface favorable for promoting charge carrier separation. The photocatalyst obtained by the invention not only expands the light absorption range and improves the crystallinity, but also realizes the effective separation of photo-generated electron hole pairs, promotes the improvement of the photocatalysis efficiency and further enhances the formaldehyde degradation performance. The equipment, the process and the medicines adopted in the preparation are relatively low in cost, and the optimal performance is achieved at the same time. The application of the catalyst in formaldehyde treatment can effectively control the harm of formaldehyde to human bodies and widen the research range of photocatalytic materials.
Example 1
0.25g polyvinylpyrrolidone (PVP) was dissolved in 50ml N, N-Dimethylformamide (DMF) containing 0.25g oleic acid, and 0.25g molybdenum disulfide (MoS) 2 ) And (3) powder. After magnetic stirring for 20min and ultrasonic treatment for 20min, the mixture is transferred to an ultrasonic cell grinder, and the system temperature is kept at 50 ℃ for accumulated ultrasonic treatment for 10h. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10min, and the resulting supernatant was washed twice with DMF and was then subjected to rotary evaporation with deionized water (H 2 O) the original solvent DMF was replaced twice and the dispersion was recorded as product I.
4g of melamine powder are weighed out, washed with deionized water and filtered, dried in an oven at 80℃and triturated, and 1g of Thioacetamide (TAA) is added. Simultaneously adding 10g of sodium chloride/potassium chloride (NaCI/KCI) as mixed molten salt (controlling the mass ratio of Na salt to K salt to be 9:11), mixing and grinding for 30min by using a mortar, pouring into a 50ml crucible with a cover, spreading the mixed powder in the crucible, then placing into a muffle furnace for 120min to rise to 550 ℃ (the temperature rising rate is 5 ℃/min), reacting for 180min at constant temperature, and cooling along with the furnace to obtain a dark yellow product. Subsequently, the milled product was dispersed in deionized water to dissolve the salt, and then filtered and repeated three times. Drying in a 50 ℃ oven, grinding and sieving to obtain dark yellow powder which is marked as a product II.
1g of product II was weighed into a beaker with 500ml of deionized water added, magnetically stirred for 20min, and then sonicated for 10h with an ultrasonic cell disruptor to maintain the system temperature at 50 ℃. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10 minutes, the upper dispersion was collected by rotary evaporation, and the lower solid was dried and pulverized, and the obtained sample was designated as product III.
Weighing 0.5g of product III and 5ml of product I, placing the mixture in a 100ml polytetrafluoroethylene lining reaction kettle, supplementing 50ml of deionized water, and magnetically stirring the mixture for 30min. The reaction kettle is put into a constant temperature oven at 140 ℃ to react for 12 hours and then is naturally cooled. Subsequently, the mixed liquid in the reaction vessel was subjected to solid-liquid separation using a centrifuge to obtain a lower precipitate. Washing the solid precipitate with deionized water for several times, and drying the solid precipitate for 12 hours in a 50 ℃ oven, wherein the obtained product is the target product.
Example 2
0.25g polyvinylpyrrolidone (PVP) was dissolved in 50ml N, N-Dimethylformamide (DMF) containing 0.25g oleic acid, and 0.25g molybdenum disulfide (MoS) 2 ) And (3) powder. After magnetic stirring for 20min and ultrasonic treatment for 20min, the mixture is transferred to an ultrasonic cell grinder, and the system temperature is kept at 50 ℃ for accumulated ultrasonic treatment for 10h. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10min, and the resulting supernatant was washed twice with DMF and was then subjected to rotary evaporation with deionized water (H 2 O) the original solvent DMF was replaced twice and the dispersion was recorded as product I.
3.5g of melamine powder are weighed out, washed with deionized water and filtered, dried in an oven at 80℃and triturated, and 1.5g of Thioacetamide (TAA) is added. Simultaneously adding 10g of sodium chloride/potassium chloride (NaCI/KCI) as mixed molten salt (controlling the mass ratio of Na salt to K salt to be 9:11), mixing and grinding for 30min by using a mortar, pouring into a 50ml crucible with a cover, spreading the mixed powder in the crucible, then placing into a muffle furnace for 120min to rise to 550 ℃ (the temperature rising rate is 5 ℃/min), reacting for 180min at constant temperature, and cooling along with the furnace to obtain a dark yellow product. Subsequently, the milled product was dispersed in deionized water to dissolve the salt, and then filtered and repeated three times. Drying in a 50 ℃ oven, grinding and sieving to obtain dark yellow powder which is marked as a product II.
1g of product II was weighed into a beaker with 500ml of deionized water added, magnetically stirred for 20min, and then sonicated for 10h with an ultrasonic cell disruptor to maintain the system temperature at 50 ℃. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10 minutes, the upper dispersion was collected by rotary evaporation, and the lower solid was dried and pulverized, and the obtained sample was designated as product III.
Weighing 0.5g of product III and 5ml of product I, placing the mixture in a 100ml polytetrafluoroethylene lining reaction kettle, supplementing 50ml of deionized water, and magnetically stirring the mixture for 30min. The reaction kettle is put into a constant temperature oven at 140 ℃ to react for 12 hours and then is naturally cooled. Subsequently, the mixed liquid in the reaction vessel was subjected to solid-liquid separation using a centrifuge to obtain a lower precipitate. Washing the solid precipitate with deionized water for several times, and drying the solid precipitate for 12 hours in a 50 ℃ oven, wherein the obtained product is the target product.
Example 3
0.25g polyvinylpyrrolidone (PVP) was dissolved in 50ml N, N-Dimethylformamide (DMF) containing 0.25g oleic acid, and 0.25g molybdenum disulfide (MoS) 2 ) And (3) powder. After magnetic stirring for 20min and ultrasonic treatment for 20min, the mixture is transferred to an ultrasonic cell grinder, and the system temperature is kept at 50 ℃ for accumulated ultrasonic treatment for 10h. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10min, and the resulting supernatant was washed twice with DMF and was then subjected to rotary evaporation with deionized water (H 2 O) the original solvent DMF was replaced twice and the dispersion was recorded as product I.
3g of melamine powder are weighed out, washed with deionized water and filtered, dried in an oven at 80℃and triturated, and 2g of Thioacetamide (TAA) are added. Simultaneously adding 10g of sodium chloride/potassium chloride (NaCI/KCI) as mixed molten salt (controlling the mass ratio of Na salt to K salt to be 9:11), mixing and grinding for 30min by using a mortar, pouring into a 50ml crucible with a cover, spreading the mixed powder in the crucible, then placing into a muffle furnace for 120min to rise to 550 ℃ (the temperature rising rate is 5 ℃/min), reacting for 180min at constant temperature, and cooling along with the furnace to obtain a dark yellow product. Subsequently, the milled product was dispersed in deionized water to dissolve the salt, and then filtered and repeated three times. Drying in a 50 ℃ oven, grinding and sieving to obtain dark yellow powder which is marked as a product II.
1g of product II was weighed into a beaker with 500ml of deionized water added, magnetically stirred for 20min, and then sonicated for 10h with an ultrasonic cell disruptor to maintain the system temperature at 50 ℃. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10 minutes, the upper dispersion was collected by rotary evaporation, and the lower solid was dried and pulverized, and the obtained sample was designated as product III.
Weighing 0.5g of product III and 5ml of product I, placing the mixture in a 100ml polytetrafluoroethylene lining reaction kettle, supplementing 50ml of deionized water, and magnetically stirring the mixture for 30min. The reaction kettle is put into a constant temperature oven at 140 ℃ to react for 12 hours and then is naturally cooled. Subsequently, the mixed liquid in the reaction vessel was subjected to solid-liquid separation using a centrifuge to obtain a lower precipitate. Washing the solid precipitate with deionized water for several times, and drying the solid precipitate for 12 hours in a 50 ℃ oven, wherein the obtained product is the target product.
Example 4
0.25g polyvinylpyrrolidone (PVP) was dissolved in 50ml N, N-Dimethylformamide (DMF) containing 0.25g oleic acid, and 0.25g molybdenum disulfide (MoS) 2 ) And (3) powder. After magnetic stirring for 20min and ultrasonic treatment for 20min, the mixture is transferred to an ultrasonic cell grinder, and the system temperature is kept at 50 ℃ for accumulated ultrasonic treatment for 10h. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10min, and the resulting supernatant was washed twice with DMF and was then subjected to rotary evaporation with deionized water (H 2 O) the original solvent DMF was replaced twice and the dispersion was recorded as product I.
3.5g of melamine powder are weighed out, washed with deionized water and filtered, dried in an oven at 80℃and triturated, and 1.5g of Thioacetamide (TAA) is added. Simultaneously adding 10g of sodium chloride/potassium chloride (NaCI/KCI) as mixed molten salt (controlling the mass ratio of Na salt to K salt to be 9:11), mixing and grinding for 30min by using a mortar, pouring into a 50ml crucible with a cover, spreading the mixed powder in the crucible, then placing into a muffle furnace for 120min to rise to 550 ℃ (the temperature rising rate is 5 ℃/min), reacting for 180min at constant temperature, and cooling along with the furnace to obtain a dark yellow product. Subsequently, the milled product was dispersed in deionized water to dissolve the salt, and then filtered and repeated three times. Drying in a 50 ℃ oven, grinding and sieving to obtain dark yellow powder which is marked as a product II.
1g of product II was weighed into a beaker with 500ml of deionized water added, magnetically stirred for 20min, and then sonicated for 10h with an ultrasonic cell disruptor to maintain the system temperature at 50 ℃. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10 minutes, the upper dispersion was collected by rotary evaporation, and the lower solid was dried and pulverized, and the obtained sample was designated as product III.
0.5g of product III and 2.5ml of product I are weighed and placed in a 100ml polytetrafluoroethylene lining reaction kettle, and after 52.5ml of deionized water is supplemented, magnetic stirring is carried out for 30min. The reaction kettle is put into a constant temperature oven at 140 ℃ to react for 12 hours and then is naturally cooled. Subsequently, the mixed liquid in the reaction vessel was subjected to solid-liquid separation using a centrifuge to obtain a lower precipitate. Washing the solid precipitate with deionized water for several times, and drying the solid precipitate for 12 hours in a 50 ℃ oven, wherein the obtained product is the target product.
Example 5
0.25g polyvinylpyrrolidone (PVP) was dissolved in 50ml N, N-Dimethylformamide (DMF) containing 0.25g oleic acid, and 0.25g molybdenum disulfide (MoS) 2 ) And (3) powder. After magnetic stirring for 20min and ultrasonic treatment for 20min, the mixture is transferred to an ultrasonic cell grinder, and the system temperature is kept at 50 ℃ for accumulated ultrasonic treatment for 10h. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10min, and the resulting supernatant was washed twice with DMF and was then subjected to rotary evaporation with deionized water (H 2 O) the original solvent DMF was replaced twice and the dispersion was recorded as product I.
3.5g of melamine powder are weighed out, washed with deionized water and filtered, dried in an oven at 80℃and triturated, and 1.5g of Thioacetamide (TAA) is added. Simultaneously adding 10g of sodium chloride/potassium chloride (NaCI/KCI) as mixed molten salt (controlling the mass ratio of Na salt to K salt to be 9:11), mixing and grinding for 30min by using a mortar, pouring into a 50ml crucible with a cover, spreading the mixed powder in the crucible, then placing into a muffle furnace for 120min to rise to 550 ℃ (the temperature rising rate is 5 ℃/min), reacting for 180min at constant temperature, and cooling along with the furnace to obtain a dark yellow product. Subsequently, the milled product was dispersed in deionized water to dissolve the salt, and then filtered and repeated three times. Drying in a 50 ℃ oven, grinding and sieving to obtain dark yellow powder which is marked as a product II.
1g of product II was weighed into a beaker with 500ml of deionized water added, magnetically stirred for 20min, and then sonicated for 10h with an ultrasonic cell disruptor to maintain the system temperature at 50 ℃. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10 minutes, the upper dispersion was collected by rotary evaporation, and the lower solid was dried and pulverized, and the obtained sample was designated as product III.
0.5g of product III and 10ml of product I are weighed and placed in a 100ml polytetrafluoroethylene lining reaction kettle, 45ml of deionized water is added, and magnetic stirring is carried out for 30min. The reaction kettle is put into a constant temperature oven at 140 ℃ to react for 12 hours and then is naturally cooled. Subsequently, the mixed liquid in the reaction vessel was subjected to solid-liquid separation using a centrifuge to obtain a lower precipitate. Washing the solid precipitate with deionized water for several times, and drying the solid precipitate for 12 hours in a 50 ℃ oven, wherein the obtained product is the target product.
Example 6
0.25g polyvinylpyrrolidone (PVP) was dissolved in 50ml N, N-Dimethylformamide (DMF) containing 0.25g oleic acid, and 0.25g molybdenum disulfide (MoS) 2 ) And (3) powder. After magnetic stirring for 20min and ultrasonic treatment for 20min, the mixture is transferred to an ultrasonic cell grinder, and the system temperature is kept at 50 ℃ for accumulated ultrasonic treatment for 10h. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10min, and the resulting supernatant was washed twice with DMF and was then subjected to rotary evaporation with deionized water (H 2 O) the original solvent DMF was replaced twice and the dispersion was recorded as product I.
3.5g of melamine powder are weighed out, washed with deionized water and filtered, dried in an oven at 80℃and triturated, and 1.5g of Thioacetamide (TAA) is added. Simultaneously adding 10g of sodium chloride/potassium chloride (NaCI/KCI) as mixed molten salt (controlling the mass ratio of Na salt to K salt to be 9:11), mixing and grinding for 30min by using a mortar, pouring into a 50ml crucible with a cover, spreading the mixed powder in the crucible, then placing into a muffle furnace for 120min to rise to 550 ℃ (the rising rate of 3 ℃/min), reacting for 200min at constant temperature, and cooling along with the furnace to obtain a dark yellow product. Subsequently, the milled product was dispersed in deionized water to dissolve the salt, and then filtered and repeated three times. Drying in a 50 ℃ oven, grinding and sieving to obtain dark yellow powder which is marked as a product II.
1g of product II was weighed into a beaker with 500ml of deionized water added, magnetically stirred for 20min, and then sonicated for 10h with an ultrasonic cell disruptor to maintain the system temperature at 50 ℃. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10 minutes, the upper dispersion was collected by rotary evaporation, and the lower solid was dried and pulverized, and the obtained sample was designated as product III.
0.5g of product III and 10ml of product I are weighed and placed in a 100ml polytetrafluoroethylene lining reaction kettle, 45ml of deionized water is added, and magnetic stirring is carried out for 30min. The reaction kettle is put into a constant temperature oven at 130 ℃ for reaction for 13 hours and then naturally cooled. Subsequently, the mixed liquid in the reaction vessel was subjected to solid-liquid separation using a centrifuge to obtain a lower precipitate. Washing the solid precipitate with deionized water for several times, and drying the solid precipitate for 12 hours in a 50 ℃ oven, wherein the obtained product is the target product.
Example 7
0.25g polyvinylpyrrolidone (PVP) was dissolved in 50ml N, N-Dimethylformamide (DMF) containing 0.25g oleic acid, and 0.25g molybdenum disulfide (MoS) 2 ) And (3) powder. After magnetic stirring for 20min and ultrasonic treatment for 20min, the mixture is transferred to an ultrasonic cell grinder, and the system temperature is kept at 50 ℃ for accumulated ultrasonic treatment for 10h. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10min, and the resulting supernatant was washed twice with DMF and was then subjected to rotary evaporation with deionized water (H 2 O) the original solvent DMF was replaced twice and the dispersion was recorded as product I.
3.5g of melamine powder are weighed out, washed with deionized water and filtered, dried in an oven at 80℃and triturated, and 1.5g of Thioacetamide (TAA) is added. Simultaneously adding 10g of sodium chloride/potassium chloride (NaCI/KCI) as mixed molten salt (controlling the mass ratio of Na salt to K salt to be 9:11), mixing and grinding for 30min by using a mortar, pouring into a 50ml crucible with a cover, spreading the mixed powder in the crucible, then placing into a muffle furnace for 120min to rise to 550 ℃ (the rising rate of 6 ℃/min), reacting for 150min at constant temperature, and cooling along with the furnace to obtain a dark yellow product. Subsequently, the milled product was dispersed in deionized water to dissolve the salt, and then filtered and repeated three times. Drying in a 50 ℃ oven, grinding and sieving to obtain dark yellow powder which is marked as a product II.
1g of product II was weighed into a beaker with 500ml of deionized water added, magnetically stirred for 20min, and then sonicated for 10h with an ultrasonic cell disruptor to maintain the system temperature at 50 ℃. After the completion of the pulverization, the mixture was centrifuged at 5000rpm for 10 minutes, the upper dispersion was collected by rotary evaporation, and the lower solid was dried and pulverized, and the obtained sample was designated as product III.
0.5g of product III and 10ml of product I are weighed and placed in a 100ml polytetrafluoroethylene lining reaction kettle, 45ml of deionized water is added, and magnetic stirring is carried out for 30min. The reaction kettle is put into a constant temperature oven at 150 ℃ to react for 11 hours and then is naturally cooled. Subsequently, the mixed liquid in the reaction vessel was subjected to solid-liquid separation using a centrifuge to obtain a lower precipitate. Washing the solid precipitate with deionized water for several times, and drying the solid precipitate for 12 hours in a 50 ℃ oven, wherein the obtained product is the target product.
To characterize the morphology of the graphite-phase carbon nitride-based photocatalytic composite material, a field emission Scanning Electron Microscope (SEM) test was performed on the target product of example 2, and the results are shown in fig. 1. FIG. 1 SEM image (2 μm) of a graphite-phase carbon nitride-based photocatalytic composite material obtained in example 2
From the figure, the sample morphology appears to be aggregated and holes appear, which illustrates a few MoS layers 2 With lamellar g-C 3 N 4 Bonding occurs gradually. The morphology still keeps g-C 3 N 4 Typical layered structures.
To verify the crystal structure characteristics of the graphite-phase carbon nitride-based photocatalytic composite material, an X-ray powder diffraction (XRD) test was performed on the target product in example 2, and the results are shown in fig. 2. FIG. 2 XRD pattern of graphite-phase carbon nitride-based photocatalytic composite material obtained in example 2
As can be seen from the graph, the graphite phase carbon nitride-based photocatalytic composite material has peaks and pure g-C at about 27.5 degrees and 13.3 degrees 3 N 4 Similar Bragg diffraction peaks, which indicate that the crystal structure is not due to MoS 2 The addition of the nanolayer is destroyed. In contrast, by comparing the (002) diffraction peak at 27.5 °, it was found that the half-width of the composite material was slightly narrowed and the peak position was shifted to the left, and that the crystallinity was improved instead means MoS 2 With g-C 3 N 4 The sheet faces are fairly tightly bonded and the expansion of the interlayer spacing occurs due to the few MoS layers 2 Enter into g-C 3 N 4 Interlayer, indicating successful recombination of the two semiconductors. In addition, it can be observed that the composite material shows an original few-layer MoS at 39.5 °, 44.5 ° and 58.3 ° 2 Weak diffraction peaks of (103), (104) and (110) planes, confirm MoS 2 Is a successful introduction of (a).
Degradation of organic dyes is the most important index reflecting photocatalytic performance, so the performance of the target product can be evaluated by testing the degradation effect of rhodamine B (RhB). The specific test process is as follows:
0.1g of the prepared photocatalytic sample was added to 50ml of 20mg/l rhodamine B (RhB) solution, stirred for 30 minutes under dark conditions using magnetic stirring to reach adsorption-desorption equilibrium, then illuminated with a 300W xenon lamp under stirring, 1ml of the supernatant was sampled every interval of time, and the concentration change of rhodamine B was measured under an ultraviolet-visible spectrophotometer. The maximum absorption intensity was measured at 553nm and plotted to obtain a degradation curve, the results of which are shown in FIG. 3. FIG. 3 degradation RhB Properties of the graphite-phase carbon nitride-based photocatalytic composite Material obtained in example 2
From the graph, the degradation rate of the composite material is obviously improved, and approximately half of RhB can be removed within 10min, and the degradation efficiency reaches 82.9% after 1h, so that the separation of electron-hole pairs is further accelerated due to the formation of heterojunction.
The performance of the target product was evaluated by testing the degradation effect of formaldehyde. The specific test process is as follows:
uniformly placing 0.1g of prepared photocatalytic sample into a culture dish, placing the culture dish into the bottom of a 500ml cylinder gas reactor, sealing the upper part by using light-transmitting quartz glass, covering the upper part by using tinfoil paper to prevent light transmission, simultaneously connecting a side wall interface of the gas reactor with an infrared sound spectrum gas detector (Innova 1512), and starting to monitor formaldehyde and CO in the gas reactor in real time 2 、H 2 Concentration of gaseous components such as O. Before the reaction starts, 100ppm of formaldehyde gas is injected from the side wall interface, after the formaldehyde in the reactor is stable and reaches adsorption-desorption balance, the tinfoil paper is taken off, the 300W xenon lamp is adopted for illumination, the photocatalytic reaction starts, and the detection interval of the gas detector is set to be 10 minutes. The results are shown in FIG. 4. FIG. 4 Formaldehyde degradation Properties of the graphite-phase carbon nitride-based photocatalytic composite Material obtained in example 2
From the graph, the degradation efficiency of the composite material reaches 77.6% after 2h illumination, which shows that electron migration generated by coupling of heterojunction interfaces is very effective for separating carriers, thereby generating more active h + Takes part in the oxidation reaction.
The foregoing is merely a preferred embodiment of the present invention and it should be noted that modifications and adaptations to those skilled in the art may be made without departing from the principles of the present invention, which are intended to be comprehended within the scope of the present invention.
Finally, it should be noted that: the above embodiments are only for illustrating the technical aspects of the present invention and not for limiting the same, and although the present invention has been described in detail with reference to the above embodiments, it should be understood by those of ordinary skill in the art that: modifications and equivalents may be made to the specific embodiments of the invention without departing from the spirit and scope of the invention, which is intended to be covered by the claims.
Claims (6)
1. The preparation method of the graphite-phase carbon nitride-based photocatalytic composite material is characterized by comprising the following steps of:
dissolving polyvinylpyrrolidone into N, N-dimethylformamide containing oleic acid, and adding molybdenum disulfide powder; stirring, ultrasonic pulverizing, centrifuging, and washing the supernatant to obtain water-dispersed MoS 2 A nanosheet dispersion;
mixing melamine powder, thioacetamide and sodium chloride/potassium chloride, and performing thermal polycondensation reaction to obtain a dark yellow product, namely the S-doped g-C prepared by molten salt 3 N 4 ;
S doping g-C 3 N 4 Adding water, ultrasonic pulverizing, centrifuging, collecting upper dispersion, rotary evaporating, collecting lower solid, drying, and grinding to obtain few modified g-C 3 N 4 A powder;
taking few layers of modified g-C 3 N 4 Powder and MoS 2 Mixing the nano-sheet dispersion liquid, preparing a mixed liquid, performing hydrothermal treatment on the mixed liquid, performing solid-liquid separation on the mixed liquid after full reaction to obtain a lower layer precipitate, and obtaining the graphite-phase carbon nitride-based photocatalytic composite material MoS 2 /g-C 3 N 4 ;
Wherein, the mass ratio of polyvinylpyrrolidone, oleic acid and molybdenum disulfide powder is 1:1:1, a step of;
the mass ratio of sodium chloride to potassium chloride in the sodium chloride/potassium chloride is 9:11;
the conditions of the thermal polycondensation reaction are as follows:
heating to 550 ℃ within 120min, heating at a speed of 4-6 ℃/min, and reacting at a constant temperature of 550 ℃ for 150-200 min;
the hydrothermal condition is 130-150 ℃, and the reaction is carried out for 10-13 hours and then natural cooling is carried out.
2. The method for preparing a graphite-phase carbon nitride-based photocatalytic composite material according to claim 1, wherein the addition amount of the thioacetamide is not more than 20wt% of the total mass of the melamine powder and the thioacetamide.
3. The method for preparing the graphite-phase carbon nitride-based photocatalytic composite material according to claim 1, wherein,
the less-layer modified g-C 3 N 4 Powder and MoS 2 The solid-to-liquid ratio of the nano-sheet dispersion liquid is 1g/5-20ml.
4. The method for preparing a graphite-phase carbon nitride-based photocatalytic composite material according to claim 1, wherein the ultrasonic cell pulverizer is adopted for both ultrasonic pulverization, the system temperature is kept at 50 ℃ during the treatment, and the accumulated ultrasonic waves are 10h;
the rotational speed of the centrifugation is 5000rpm for both times, and the centrifugation is 10min.
5. A graphite-phase carbon nitride-based photocatalytic composite material, characterized by being produced by the method according to any one of claims 1 to 4.
6. Use of the graphite-phase carbon nitride-based photocatalytic composite material prepared by the method according to any one of claims 1 to 4 for treating formaldehyde pollution.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202111007738.7A CN113649052B (en) | 2021-08-30 | 2021-08-30 | Graphite-phase carbon nitride-based photocatalytic composite material and preparation and application thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202111007738.7A CN113649052B (en) | 2021-08-30 | 2021-08-30 | Graphite-phase carbon nitride-based photocatalytic composite material and preparation and application thereof |
Publications (2)
Publication Number | Publication Date |
---|---|
CN113649052A CN113649052A (en) | 2021-11-16 |
CN113649052B true CN113649052B (en) | 2024-04-02 |
Family
ID=78493287
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202111007738.7A Active CN113649052B (en) | 2021-08-30 | 2021-08-30 | Graphite-phase carbon nitride-based photocatalytic composite material and preparation and application thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN113649052B (en) |
Families Citing this family (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN114367300A (en) * | 2022-01-27 | 2022-04-19 | 西藏民族大学 | Preparation method of S-graphite phase carbon nitride and graphene oxide photocatalyst |
CN114768869A (en) * | 2022-05-21 | 2022-07-22 | 深圳市绿蔓科技有限公司 | Preparation method and application of aza-condensed ring g-C3N4 composite material |
CN115108587A (en) * | 2022-06-24 | 2022-09-27 | 上海交通大学医学院附属仁济医院 | Molybdenum disulfide-doped two-dimensional carbon nitrogen compound matrix and preparation method and application thereof |
CN115178286A (en) * | 2022-07-10 | 2022-10-14 | 湖南大学 | Sulfur-doped carbon nitride modified molybdenum oxide composite photocatalytic material with adjustable defect density and preparation method thereof |
CN116332438B (en) * | 2023-05-23 | 2023-07-21 | 湖南环宏环保科技有限公司 | Treatment method of landfill leachate membrane concentrate |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106824250A (en) * | 2017-03-16 | 2017-06-13 | 江苏理工学院 | A kind of carbonitride visible light catalyst for the zinc that adulterates and its production and use |
CN108671955A (en) * | 2018-05-24 | 2018-10-19 | 西京学院 | A kind of photodissociation aquatic products complex hydroformylation catalyst and preparation method thereof |
CN109364977A (en) * | 2018-12-06 | 2019-02-22 | 辽宁大学 | Sulfur doping graphite phase carbon nitride nanosheet photocatalyst and the preparation method and application thereof |
CN112295584A (en) * | 2020-10-23 | 2021-02-02 | 南昌航空大学 | Preparation method and application of molybdenum disulfide/boron-doped graphite-phase carbon nitride composite visible-light-driven photocatalyst |
Family Cites Families (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20170044170A (en) * | 2014-08-21 | 2017-04-24 | 더 유니버시티 오브 리버풀 | Two-dimensional carbon nitride material and method of preparation |
-
2021
- 2021-08-30 CN CN202111007738.7A patent/CN113649052B/en active Active
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106824250A (en) * | 2017-03-16 | 2017-06-13 | 江苏理工学院 | A kind of carbonitride visible light catalyst for the zinc that adulterates and its production and use |
CN108671955A (en) * | 2018-05-24 | 2018-10-19 | 西京学院 | A kind of photodissociation aquatic products complex hydroformylation catalyst and preparation method thereof |
CN109364977A (en) * | 2018-12-06 | 2019-02-22 | 辽宁大学 | Sulfur doping graphite phase carbon nitride nanosheet photocatalyst and the preparation method and application thereof |
CN112295584A (en) * | 2020-10-23 | 2021-02-02 | 南昌航空大学 | Preparation method and application of molybdenum disulfide/boron-doped graphite-phase carbon nitride composite visible-light-driven photocatalyst |
Non-Patent Citations (3)
Title |
---|
Molten salt-mediated formation of g-C3N4-MoS2 for visible-light-driven photocatalytic hydrogen evolution;Li, N,et al.;《APPLIED SURFACE SCIENCE》;第218-224页 * |
Synthesis of MoS2/g-C3N4 nanosheets as 2D heterojunction photocatalysts with enhanced visible light activity;Li, J,et al.;《APPLIED SURFACE SCIENCE》;第694-702页 * |
构建MoS2/Fe-g-C3N4异质结催化剂以促进其可见光催化产氢性能;田少鹏等;《精细化工》;第2431-2437页 * |
Also Published As
Publication number | Publication date |
---|---|
CN113649052A (en) | 2021-11-16 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN113649052B (en) | Graphite-phase carbon nitride-based photocatalytic composite material and preparation and application thereof | |
Wang et al. | A critical review on graphitic carbon nitride (g-C3N4)-based materials: Preparation, modification and environmental application | |
CN111450819B (en) | Biochar modified bismuth vanadate catalyst, preparation method and application thereof | |
Wang et al. | g-C3N4/B doped g-C3N4 quantum dots heterojunction photocatalysts for hydrogen evolution under visible light | |
Yu et al. | Novel rugby-ball-like Zn3 (PO4) 2@ C3N4 photocatalyst with highly enhanced visible-light photocatalytic performance | |
Li et al. | Visible-light-driven CQDs@ MIL-125 (Ti) nanocomposite photocatalyst with enhanced photocatalytic activity for the degradation of tetracycline | |
Tang et al. | Enhanced photocatalytic degradation of tetracycline antibiotics by reduced graphene oxide–CdS/ZnS heterostructure photocatalysts | |
Liu et al. | Facile synthesis and enhanced visible-light photocatalytic activity of graphitic carbon nitride decorated with ultrafine Fe 2 O 3 nanoparticles | |
Liang et al. | High performance visible-light driven photocatalysts of Bi2MoO6-g-C3N4 with controllable solvothermal fabrication | |
Li et al. | Facile synthesis of ZnO/g-C3N4 composites with honeycomb-like structure by H2 bubble templates and their enhanced visible light photocatalytic performance | |
Zhang et al. | Calcination of reduced graphene oxide decorated TiO2 composites for recovery and reuse in photocatalytic applications | |
Jiang et al. | Construction of amorphous Ta2O5/g-C3N4 nanosheet hybrids with superior visible-light photoactivities for organic dye degradation and mechanism insight | |
Zhao et al. | PVP-capped CdS nanopopcorns with type-II homojunctions for highly efficient visible-light-driven organic pollutant degradation and hydrogen evolution | |
Li et al. | Facial synthesis of dandelion-like g-C3N4/Ag with high performance of photocatalytic hydrogen production | |
Rahman et al. | Detailed photocatalytic study of alkaline titanates and its application for the degradation of methylene blue (MB) under solar irradiation | |
Li et al. | Folded nano-porous graphene-like carbon nitride with significantly improved visible-light photocatalytic activity for dye degradation | |
Shi et al. | The bifunctional composites of AC restrain the stack of g-C3N4 with the excellent adsorption-photocatalytic performance for the removal of RhB | |
Zhou et al. | Enhanced visible light photocatalytic degradation of rhodamine B by Z-scheme CuWO 4/gC 3 N 4 heterojunction | |
CN110624594A (en) | Magnetic Fe3O4/ZnO/g-C3N4Composite photocatalyst and preparation method thereof | |
Wang et al. | Green synthesis g-C3N4 quantum dots loading h-BN for efficient and stable photocatalytic performance | |
Yang et al. | Ascorbic acid-assisted hydrothermal route to create mesopores in polymeric carbon nitride for increased photocatalytic hydrogen generation | |
Liu et al. | One-step microwave synthesis of covalently bonded OC3N4/C60 with enhanced photocatalytic properties | |
Zheng et al. | Binary solvent controllable synthesis of BiOCl towards enhanced photocatalytic activity | |
He et al. | Tunable nanostructure of TiO 2/reduced graphene oxide composite for high photocatalysis | |
Yadav et al. | Preparation of controlled lotus like structured ZnO decorated reduced graphene oxide nanocomposites to obtain enhanced photocatalytic properties |
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 |