CN115400699A - Preparation Method and Application of Reduced Graphene Oxide/Phosphated Polyvinyl Alcohol Composite Airgel - Google Patents
Preparation Method and Application of Reduced Graphene Oxide/Phosphated Polyvinyl Alcohol Composite Airgel Download PDFInfo
- Publication number
- CN115400699A CN115400699A CN202211071700.0A CN202211071700A CN115400699A CN 115400699 A CN115400699 A CN 115400699A CN 202211071700 A CN202211071700 A CN 202211071700A CN 115400699 A CN115400699 A CN 115400699A
- Authority
- CN
- China
- Prior art keywords
- polyvinyl alcohol
- graphene oxide
- reduced graphene
- reaction
- phosphated
- 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
Links
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 title claims abstract description 131
- 239000004372 Polyvinyl alcohol Substances 0.000 title claims abstract description 129
- 229920002451 polyvinyl alcohol Polymers 0.000 title claims abstract description 129
- 229910021389 graphene Inorganic materials 0.000 title claims abstract description 122
- 239000002131 composite material Substances 0.000 title claims abstract description 102
- 238000002360 preparation method Methods 0.000 title claims abstract description 33
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 87
- 238000001704 evaporation Methods 0.000 claims abstract description 68
- 230000008020 evaporation Effects 0.000 claims abstract description 68
- 238000006243 chemical reaction Methods 0.000 claims abstract description 56
- 238000000034 method Methods 0.000 claims abstract description 31
- 239000004964 aerogel Substances 0.000 claims abstract description 8
- 239000013535 sea water Substances 0.000 claims abstract description 7
- 229910001385 heavy metal Inorganic materials 0.000 claims abstract description 6
- 239000002351 wastewater Substances 0.000 claims abstract description 6
- ZMXDDKWLCZADIW-UHFFFAOYSA-N N,N-Dimethylformamide Chemical compound CN(C)C=O ZMXDDKWLCZADIW-UHFFFAOYSA-N 0.000 claims description 36
- 239000008367 deionised water Substances 0.000 claims description 20
- 229910021641 deionized water Inorganic materials 0.000 claims description 20
- 239000000243 solution Substances 0.000 claims description 19
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims description 16
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 16
- VWDWKYIASSYTQR-UHFFFAOYSA-N sodium nitrate Chemical compound [Na+].[O-][N+]([O-])=O VWDWKYIASSYTQR-UHFFFAOYSA-N 0.000 claims description 16
- DLYUQMMRRRQYAE-UHFFFAOYSA-N tetraphosphorus decaoxide Chemical compound O1P(O2)(=O)OP3(=O)OP1(=O)OP2(=O)O3 DLYUQMMRRRQYAE-UHFFFAOYSA-N 0.000 claims description 15
- 230000035484 reaction time Effects 0.000 claims description 14
- 239000000203 mixture Substances 0.000 claims description 13
- 150000003839 salts Chemical group 0.000 claims description 11
- 238000012546 transfer Methods 0.000 claims description 9
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 8
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 claims description 8
- 239000004202 carbamide Substances 0.000 claims description 8
- 239000000017 hydrogel Substances 0.000 claims description 8
- 235000010344 sodium nitrate Nutrition 0.000 claims description 8
- 239000004317 sodium nitrate Substances 0.000 claims description 8
- 238000001027 hydrothermal synthesis Methods 0.000 claims description 7
- 238000005406 washing Methods 0.000 claims description 7
- 238000002156 mixing Methods 0.000 claims description 6
- 239000012286 potassium permanganate Substances 0.000 claims description 6
- 239000011165 3D composite Substances 0.000 claims description 5
- 238000004108 freeze drying Methods 0.000 claims description 5
- 239000011259 mixed solution Substances 0.000 claims description 4
- 229910052757 nitrogen Inorganic materials 0.000 claims description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 claims 4
- ATHHXGZTWNVVOU-UHFFFAOYSA-N N-methylformamide Chemical compound CNC=O ATHHXGZTWNVVOU-UHFFFAOYSA-N 0.000 claims 2
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical compound [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 claims 2
- 229910000147 aluminium phosphate Inorganic materials 0.000 claims 2
- 239000001103 potassium chloride Substances 0.000 claims 1
- 235000011164 potassium chloride Nutrition 0.000 claims 1
- 238000003756 stirring Methods 0.000 claims 1
- 239000012267 brine Substances 0.000 abstract description 9
- HPALAKNZSZLMCH-UHFFFAOYSA-M sodium;chloride;hydrate Chemical compound O.[Na+].[Cl-] HPALAKNZSZLMCH-UHFFFAOYSA-M 0.000 abstract description 9
- 230000003287 optical effect Effects 0.000 abstract description 4
- 238000006068 polycondensation reaction Methods 0.000 abstract description 4
- YWEUIGNSBFLMFL-UHFFFAOYSA-N diphosphonate Chemical compound O=P(=O)OP(=O)=O YWEUIGNSBFLMFL-UHFFFAOYSA-N 0.000 description 11
- 230000000052 comparative effect Effects 0.000 description 10
- 239000002121 nanofiber Substances 0.000 description 8
- 238000005516 engineering process Methods 0.000 description 7
- 239000000463 material Substances 0.000 description 5
- IMROMDMJAWUWLK-UHFFFAOYSA-N Ethenol Chemical compound OC=C IMROMDMJAWUWLK-UHFFFAOYSA-N 0.000 description 3
- 238000001157 Fourier transform infrared spectrum Methods 0.000 description 3
- 239000001913 cellulose Substances 0.000 description 3
- 229920002678 cellulose Polymers 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 239000006185 dispersion Substances 0.000 description 3
- 230000003993 interaction Effects 0.000 description 3
- 238000003760 magnetic stirring Methods 0.000 description 3
- GGAUUQHSCNMCAU-ZXZARUISSA-N (2s,3r)-butane-1,2,3,4-tetracarboxylic acid Chemical compound OC(=O)C[C@H](C(O)=O)[C@H](C(O)=O)CC(O)=O GGAUUQHSCNMCAU-ZXZARUISSA-N 0.000 description 2
- KWSLGOVYXMQPPX-UHFFFAOYSA-N 5-[3-(trifluoromethyl)phenyl]-2h-tetrazole Chemical compound FC(F)(F)C1=CC=CC(C2=NNN=N2)=C1 KWSLGOVYXMQPPX-UHFFFAOYSA-N 0.000 description 2
- 238000005033 Fourier transform infrared spectroscopy Methods 0.000 description 2
- 238000001237 Raman spectrum Methods 0.000 description 2
- 238000002835 absorbance Methods 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 238000002425 crystallisation Methods 0.000 description 2
- 230000008025 crystallization Effects 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 239000003292 glue Substances 0.000 description 2
- 230000031700 light absorption Effects 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 229910001379 sodium hypophosphite Inorganic materials 0.000 description 2
- 238000012360 testing method Methods 0.000 description 2
- YJLUBHOZZTYQIP-UHFFFAOYSA-N 2-[5-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]-1,3,4-oxadiazol-2-yl]-1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C1=NN=C(O1)CC(=O)N1CC2=C(CC1)NN=N2 YJLUBHOZZTYQIP-UHFFFAOYSA-N 0.000 description 1
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 description 1
- MKYBYDHXWVHEJW-UHFFFAOYSA-N N-[1-oxo-1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)propan-2-yl]-2-[[3-(trifluoromethoxy)phenyl]methylamino]pyrimidine-5-carboxamide Chemical compound O=C(C(C)NC(=O)C=1C=NC(=NC=1)NCC1=CC(=CC=C1)OC(F)(F)F)N1CC2=C(CC1)NN=N2 MKYBYDHXWVHEJW-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 238000002441 X-ray diffraction Methods 0.000 description 1
- 238000000026 X-ray photoelectron spectrum Methods 0.000 description 1
- 239000011358 absorbing material Substances 0.000 description 1
- 238000000862 absorption spectrum Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 238000005452 bending Methods 0.000 description 1
- 239000010866 blackwater Substances 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 238000012512 characterization method Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 238000006482 condensation reaction Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 238000004132 cross linking Methods 0.000 description 1
- 239000003431 cross linking reagent Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 238000009510 drug design Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000007710 freezing Methods 0.000 description 1
- 230000008014 freezing Effects 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 125000000524 functional group Chemical group 0.000 description 1
- 229910052748 manganese Inorganic materials 0.000 description 1
- 239000011572 manganese Substances 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 230000011514 reflex Effects 0.000 description 1
- 238000001223 reverse osmosis Methods 0.000 description 1
- 238000001878 scanning electron micrograph Methods 0.000 description 1
- 238000001228 spectrum Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
Images
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
- B01J13/00—Colloid chemistry, e.g. the production of colloidal materials or their solutions, not otherwise provided for; Making microcapsules or microballoons
- B01J13/0091—Preparation of aerogels, e.g. xerogels
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
- C02F1/043—Details
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
- C02F1/14—Treatment of water, waste water, or sewage by heating by distillation or evaporation using solar energy
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Dispersion Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Sustainable Development (AREA)
- Sustainable Energy (AREA)
- Carbon And Carbon Compounds (AREA)
Abstract
Description
技术领域technical field
本发明涉及光热水蒸发材料技术领域,尤其涉及一种还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的制备方法及其应用。The invention relates to the technical field of photothermal water evaporation materials, in particular to a preparation method and application of a reduced graphene oxide/phosphated polyvinyl alcohol composite airgel.
背景技术Background technique
随着人类社会经济的发展,能源短缺和水资源污染的问题日益凸显。为了减少对环境造成的污染,对清洁能源的利用是人类发展的必由之路。传统水净化技术,如反渗透、膜蒸馏技术等,具有能耗高、基础设施集中且大型化的特点,而在自然蒸发的启发下,提出了太阳光驱动的界面蒸发技术。太阳能作为一种清洁可持续的能源,可以将吸收的光能转化热量,用于加热水/空气界面的水分子。因此,太阳能驱动的界面蒸发技术被认为是一种缓解淡水资源和减少碳足迹的有前景的替代方案之一。With the development of human society and economy, the problems of energy shortage and water pollution have become increasingly prominent. In order to reduce pollution to the environment, the use of clean energy is the only way for human development. Traditional water purification technologies, such as reverse osmosis and membrane distillation technologies, have the characteristics of high energy consumption, centralized and large-scale infrastructure. Inspired by natural evaporation, a solar-driven interface evaporation technology is proposed. As a clean and sustainable energy source, solar energy can convert the absorbed light energy into heat, which can be used to heat water molecules at the water/air interface. Therefore, solar-driven interfacial evaporation technology is considered as one of the promising alternatives to alleviate freshwater resources and reduce carbon footprint.
在太阳能驱动的界面蒸发技术中,光热吸收材料是重点,其中氧化石墨烯(GO)因其优异的太阳光吸收率、高化学稳定性和较轻的密度,为太阳光蒸发器的合理设计和利用提供了巨大的机会,并被广泛应用于界面蒸发。现有技术中,申请号为202210251817.0,公开日为2022年4月29日,名称为“一种纤维素纳米纤维气凝胶光热界面水蒸发材料及其制备方法”的发明专利通过将一定量含有纤维素纳米纤维、聚乙烯醇、氧化石墨烯、交联剂和催化剂的分散液倒入模具中冷冻,之后冷冻干燥成气凝胶,对气凝胶在高温下进行交联,再进行还原,制备了化学交联型纤维素纳米纤维/聚乙烯醇/还原氧化石墨烯气凝胶光热界面水蒸发材料。上述技术方案中虽然可以制备出纳米纤维气凝胶,但是制备过程复杂,制备流程长,成本较高,对环境不友好;此外,上述技术方案中通过引入纤维素纳米纤维和交联剂将聚乙烯醇和氧化石墨烯进行交联的方式,难以对气凝胶内部的结构进行调控,水传输速率较慢,影响了复合气凝胶在界面蒸发应用中的蒸发效率。In solar-driven interfacial evaporation technology, photothermal absorbing materials are the focus, among which graphene oxide (GO) is the rational design of solar evaporator due to its excellent solar light absorption rate, high chemical stability and light density. and utilization offer great opportunities and are widely used in interfacial evaporation. In the existing technology, the application number is 202210251817.0, and the publication date is April 29, 2022. The invention patent named "a cellulose nanofiber airgel photothermal interface water evaporation material and its preparation method" has passed a certain amount of The dispersion containing cellulose nanofibers, polyvinyl alcohol, graphene oxide, cross-linking agent and catalyst is poured into a mold and frozen, then freeze-dried into an airgel, and the airgel is cross-linked at high temperature, and then reduced , A chemically crosslinked cellulose nanofiber/polyvinyl alcohol/reduced graphene oxide airgel photothermal interface water evaporation material was prepared. Although the nanofiber airgel can be prepared in the above technical solution, the preparation process is complicated, the preparation process is long, the cost is high, and it is not friendly to the environment; in addition, in the above technical solution, the poly The cross-linking method of vinyl alcohol and graphene oxide makes it difficult to control the internal structure of the airgel, and the water transfer rate is slow, which affects the evaporation efficiency of the composite airgel in the interface evaporation application.
有鉴于此,有必要设计一种改进的超吸水性高性能的三维还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的制备方法及其应用,以解决上述问题。In view of this, it is necessary to design an improved superabsorbent high-performance three-dimensional reduced graphene oxide/phosphated polyvinyl alcohol composite airgel preparation method and its application to solve the above problems.
发明内容Contents of the invention
本发明的目的在于提供一种还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的制备方法及其应用。The object of the present invention is to provide a preparation method and application of reduced graphene oxide/phosphated polyvinyl alcohol composite airgel.
为实现上述发明目的,本发明提供了一种还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的制备方法,包括如下步骤:In order to achieve the above-mentioned purpose of the invention, the invention provides a method for preparing a reduced graphene oxide/phosphated polyvinyl alcohol composite aerogel, comprising the steps of:
S1、将预定量的聚乙烯醇、N,N-二甲基甲酰胺及五氧化二磷加入到反应容器中,混合均匀后,将所述反应容器在油浴中进行反应;待反应结束后,将产物洗涤,烘干后制得磷酸酯化聚乙烯醇;S1. Add a predetermined amount of polyvinyl alcohol, N,N-dimethylformamide and phosphorus pentoxide into the reaction container, and after mixing evenly, react the reaction container in an oil bath; after the reaction is completed , the product is washed and dried to obtain phosphated polyvinyl alcohol;
S2、采用改进Hummers法制备氧化石墨烯;S2, using improved Hummers method to prepare graphene oxide;
S3、将步骤S2制得的氧化石墨烯分散在去离子水中,并加入预定量的尿素,混合均匀后得到氧化石墨烯溶液;再将步骤S1中制得的所述磷酸酯化聚乙烯醇加入到所述氧化石墨烯溶液中,混合均匀后,将上述混合溶液转移至高压反应釜中进行水热反应,形成圆柱状三维复合水凝胶;最后,将所述圆柱状三维复合水凝胶取出,经洗涤和冷冻干燥处理后,即制得还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶。S3. Disperse the graphene oxide prepared in step S2 in deionized water, add a predetermined amount of urea, and mix uniformly to obtain a graphene oxide solution; then add the phosphated polyvinyl alcohol prepared in step S1 into the graphene oxide solution, and after mixing evenly, transfer the mixed solution to an autoclave for hydrothermal reaction to form a cylindrical three-dimensional composite hydrogel; finally, take out the cylindrical three-dimensional composite hydrogel , after washing and freeze-drying, the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel is prepared.
优选的,在步骤S1中,所述聚乙烯醇、所述N,N-二甲基甲酰胺及所述五氧化二磷三者的质量比为(1~3):(10~100):(1~3)。Preferably, in step S1, the mass ratio of the polyvinyl alcohol, the N,N-dimethylformamide and the phosphorus pentoxide is (1-3): (10-100): (1~3).
优选的,在步骤S1中,所述反应的反应温度为100~200℃,反应时间为1~5h。Preferably, in step S1, the reaction temperature of the reaction is 100-200° C., and the reaction time is 1-5 h.
优选的,在步骤S3中,所述氧化石墨烯、所述尿素及所述磷酸酯化聚乙烯醇的质量比为(1~3):(10~100):(1~3)。Preferably, in step S3, the mass ratio of the graphene oxide, the urea and the phosphated polyvinyl alcohol is (1-3):(10-100):(1-3).
优选的,在步骤S3中,所述水热反应的反应温度为100~200℃,反应时间为1~5h;优选的,所述还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的高度为0.5~3cm。Preferably, in step S3, the reaction temperature of the hydrothermal reaction is 100-200°C, and the reaction time is 1-5h; preferably, the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel The height is 0.5-3cm.
优选的,在步骤S2中,所述氧化石墨烯的具体制备过程如下:在磁力搅拌条件下,使石墨粉与硫酸进行混合,再依次加入硝酸钠和高锰酸钾,再将盛装上述混合物的容器转移至油浴中进行油浴反应,反应过程中加入去离子水进行升温反应,再加入去离子水和双氧水进行反应,反应结束后对产物进行洗涤和干燥,即可制得氧化石墨烯。Preferably, in step S2, the specific preparation process of the graphene oxide is as follows: under the condition of magnetic stirring, graphite powder is mixed with sulfuric acid, then sodium nitrate and potassium permanganate are added in sequence, and the above-mentioned mixture is filled with The container is transferred to an oil bath for oil bath reaction. During the reaction process, deionized water is added for temperature rise reaction, and then deionized water and hydrogen peroxide are added for reaction. After the reaction, the product is washed and dried to obtain graphene oxide.
优选的,所述石墨粉、所述硫酸、所述硝酸钠、所述高锰酸钾及所述双氧水的质量比为(1~3):(10~50):(1~3):(1~10):(10~50)。Preferably, the mass ratio of the graphite powder, the sulfuric acid, the sodium nitrate, the potassium permanganate and the hydrogen peroxide is (1~3):(10~50):(1~3):( 1~10): (10~50).
优选的,所述油浴反应的反应温度为10~100℃,反应时间为100~200min;所述洗涤过程采用盐酸和去离子水进行,洗涤次数为3~5次。Preferably, the reaction temperature of the oil bath reaction is 10-100° C., and the reaction time is 100-200 min; the washing process is carried out with hydrochloric acid and deionized water, and the washing times are 3-5 times.
特别地,本发明还提供了所述还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的应用,采用如下方式进行:将还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶放置在待处理的水体中,在模拟太阳光下,使环境的温度和湿度为恒定值,通过电子分析天平监测到的所述水体和所述还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的质量之和的变化,计算太阳光驱动的光热蒸发速率。In particular, the present invention also provides the application of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel, which is carried out in the following manner: the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel is placed In the water body to be treated, under simulated sunlight, the temperature and humidity of the environment are kept at a constant value, and the water body and the reduced graphene oxide/phosphated polyvinyl alcohol composite aircondensation monitored by an electronic analytical balance The change of the sum of the masses of the glue is used to calculate the photothermal evaporation rate driven by sunlight.
优选的,所述水体为盐水、实际海水、黑臭水体或重金属染料废水。Preferably, the water body is brine, actual sea water, black and odorous water body or heavy metal dye wastewater.
本发明的有益效果是:The beneficial effects of the present invention are:
1、本发明提供的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的制备方法,通过先制备超亲水的磷酸酯化聚乙烯醇,再将其与氧化石墨烯复合,最终制得机械性能强、超亲水性、低热传导率且光热转化效率高的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶。通过上述方式,有效解决了现有技术中利用纳米纤维制备光热界面水蒸发材料过程中存在的制备过程复杂、制备流程长及成本高等问题,并制得了能够广泛应用于盐水、实际海水、黑臭水体或重金属染料废水中的水分子蒸发的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶。1. The preparation method of the reduced graphene oxide/phosphorylated polyvinyl alcohol composite airgel provided by the present invention is to prepare superhydrophilic phosphated polyvinyl alcohol first, and then compound it with graphene oxide to finally produce A reduced graphene oxide/phosphated polyvinyl alcohol composite airgel with strong mechanical properties, superhydrophilicity, low thermal conductivity and high photothermal conversion efficiency was obtained. Through the above method, the problems of complex preparation process, long preparation process and high cost in the process of using nanofibers to prepare photothermal interfacial water evaporation materials in the prior art are effectively solved, and the preparation can be widely used in salt water, actual sea water, black water, etc. Reduced graphene oxide/phosphorylated polyvinyl alcohol composite aerogels evaporated from water molecules in odorous water or heavy metal dye wastewater.
2、本发明制备的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶,通过引入超亲水的磷酸酯化聚乙烯醇,不仅可赋予复合气凝胶超亲水性,使其在用于水体蒸发时,能够更快速地将水体输送至蒸发界面,可确保在较集中的光强下实现水体的高效蒸发;还可利用磷酸酯化聚乙烯醇与氧化石墨烯之间形成的网络结构与水之间的相互作用,使水分子活化,减少水蒸发所需的能量,从而提升水蒸发速率;复合气凝胶的低热传导率可使光热转化过程中的热量集中在蒸发界面,减少了与环境的热量交换,更利于蒸发过程的进行;由于复合气凝胶本身具有的三维结构,其在蒸发过程中的蒸发致冷效应使得复合气凝胶侧边的温度低于环境温度,从而可以从环境中吸取额外的能量用于使水体中的水分子蒸发;另外,复合气凝胶的超亲水性及快速水传输可构造盐结晶与盐释放之间的动态平衡,避免海水蒸发过程中,盐分堵塞气凝胶的内部孔道,确保蒸发过程的持续进行。2. The reduced graphene oxide/phosphorylated polyvinyl alcohol composite airgel prepared by the present invention can not only endow the composite airgel with superhydrophilicity by introducing superhydrophilic phosphated polyvinyl alcohol, but also make it When used for water evaporation, it can transport water to the evaporation interface more quickly, ensuring efficient evaporation of water under concentrated light intensity; it can also use the network formed between phosphated polyvinyl alcohol and graphene oxide The interaction between the structure and water activates the water molecules, reduces the energy required for water evaporation, thereby increasing the evaporation rate of water; the low thermal conductivity of the composite airgel can concentrate the heat in the process of photothermal conversion on the evaporation interface, The heat exchange with the environment is reduced, which is more conducive to the evaporation process; due to the three-dimensional structure of the composite airgel itself, its evaporative cooling effect during the evaporation process makes the temperature on the side of the composite airgel lower than the ambient temperature, In this way, additional energy can be absorbed from the environment to evaporate water molecules in the water body; in addition, the superhydrophilicity and fast water transport of the composite airgel can construct a dynamic balance between salt crystallization and salt release, avoiding seawater evaporation During the evaporation process, the salt plugs the internal pores of the airgel to ensure the continuous evaporation process.
3、本发明提出的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的制备方法,利用磷酸酯化聚乙烯醇与氧化石墨烯之间的缩聚反应,可充分利用氧化石墨烯自身优异的光学性能和三维环境增强效应与磷酸酯化聚乙烯醇的超亲水性和低蒸发焓进行结合,赋予复合气凝胶高蒸发速率和能量利用效率,同时,磷酸酯化聚乙烯醇与氧化石墨烯之间的反应,有效增强了复合气凝胶的机械强度,提高了在水净化技术的实际应用性能。3. The method for preparing the reduced graphene oxide/phosphorylated polyvinyl alcohol composite airgel proposed by the present invention utilizes the polycondensation reaction between phosphated polyvinyl alcohol and graphene oxide, which can make full use of the excellent properties of graphene oxide itself. The optical properties and three-dimensional environmental enhancement effect of phosphated polyvinyl alcohol are combined with the superhydrophilicity and low evaporation enthalpy, which endows the composite airgel with high evaporation rate and energy utilization efficiency. At the same time, phosphated polyvinyl alcohol and oxidation The reaction between graphene effectively enhances the mechanical strength of the composite airgel and improves the practical application performance in water purification technology.
附图说明Description of drawings
图1为本发明的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的制备方法的制备原理图;Fig. 1 is the preparation schematic diagram of the preparation method of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel of the present invention;
图2为本发明的实施例1制得的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的SEM图;Fig. 2 is the SEM picture of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel that
图3为本发明的实施例1制得的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的XRD图;Fig. 3 is the XRD figure of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel that
图4为本发明的实施例1制得的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的FTIR图;Fig. 4 is the FTIR figure of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel that the embodiment of the
图5为本发明的实施例1制得的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的XPS图;Fig. 5 is the XPS figure of the reduced graphene oxide/phosphorylated polyvinyl alcohol composite airgel prepared in Example 1 of the present invention;
图6为本发明的实施例1制得的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的吸光强度图;Fig. 6 is the absorbance intensity diagram of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel prepared in Example 1 of the present invention;
图7为本发明的实施例1制得的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的Raman光谱;Fig. 7 is the Raman spectrum of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel prepared in Example 1 of the present invention;
图8为本发明的实施例1制得的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的DSC图;Fig. 8 is the DSC figure of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel prepared in Example 1 of the present invention;
图9为本发明制得的不同厚度的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的纯水的蒸发速率的对比图。Fig. 9 is a comparison chart of the evaporation rate of pure water of reduced graphene oxide/phosphated polyvinyl alcohol composite airgel with different thicknesses prepared in the present invention.
具体实施方式Detailed ways
为了使本发明的目的、技术方案和优点更加清楚,下面结合附图和具体实施例对本发明进行详细描述。In order to make the object, technical solution and advantages of the present invention clearer, the present invention will be described in detail below in conjunction with the accompanying drawings and specific embodiments.
在此,还需要说明的是,为了避免因不必要的细节而模糊了本发明,在附图中仅仅示出了与本发明的方案密切相关的结构和/或处理步骤,而省略了与本发明关系不大的其他细节。Here, it should also be noted that, in order to avoid obscuring the present invention due to unnecessary details, only the structures and/or processing steps closely related to the solution of the present invention are shown in the drawings, and the steps related to the present invention are omitted. Invent other details that don't really matter.
另外,还需要说明的是,术语“包括”、“包含”或者其任何其他变体意在涵盖非排他性的包含,从而使得包括一系列要素的过程、方法、物品或者设备不仅包括那些要素,而且还包括没有明确列出的其他要素,或者是还包括为这种过程、方法、物品或者设备所固有的要素。Additionally, it should be noted that the term "comprises", "comprises" or any other variation thereof is intended to cover a non-exclusive inclusion such that a process, method, article or apparatus comprising a set of elements includes not only those elements, but also Other elements not expressly listed, or inherent to the process, method, article, or apparatus are also included.
请参阅图1所示,本发明提出的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的制备方法,包括如下步骤:Please refer to shown in Figure 1, the preparation method of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel proposed by the present invention comprises the following steps:
S1、制备磷酸酯化聚乙烯醇:将预定量的聚乙烯醇、N,N-二甲基甲酰胺及五氧化二磷加入到反应容器中,混合均匀后,将反应容器转移至油浴环境中进行反应;待反应结束后,用去离子水洗涤产物,烘干后制得磷酸酯化聚乙烯醇;S1. Preparation of phosphated polyvinyl alcohol: Add a predetermined amount of polyvinyl alcohol, N,N-dimethylformamide and phosphorus pentoxide into the reaction vessel, mix well, and transfer the reaction vessel to an oil bath environment The reaction is carried out in; after the reaction is finished, the product is washed with deionized water and dried to obtain phosphated polyvinyl alcohol;
S2、制备氧化石墨烯:采用改进Hummers法制备氧化石墨烯,具体的制备过程如下:在磁力搅拌条件下,使石墨粉与硫酸进行混合,再依次加入硝酸钠和高锰酸钾,再将盛装上述混合物的容器转移至油浴中进行油浴反应,反应过程中加入去离子水进行升温反应,再加入去离子水和双氧水进行反应,反应结束后将溶液用盐酸和去离子水洗涤3~5次,再经干燥,即可制得氧化石墨烯;S2, preparation of graphene oxide: the improved Hummers method is used to prepare graphene oxide, the specific preparation process is as follows: under the condition of magnetic stirring, graphite powder is mixed with sulfuric acid, then sodium nitrate and potassium permanganate are added successively, and then the The container of the above mixture is transferred to an oil bath for oil bath reaction. During the reaction, deionized water is added for temperature rise reaction, and then deionized water and hydrogen peroxide are added for reaction. After the reaction, the solution is washed with hydrochloric acid and deionized water for 3 to 5 times, and then dried to obtain graphene oxide;
S3、制备还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶;S3. Prepare reduced graphene oxide/phosphated polyvinyl alcohol composite airgel;
将步骤S2得到的氧化石墨烯加入到去离子水中,混合均匀后加入预定量的尿素,混合均匀后得到氧化石墨烯溶液;再将步骤S1制得的磷酸酯化聚乙烯醇加入到氧化石墨烯溶液中,混合均匀后,将上述混合溶液转移至高压反应釜中进行水热反应,在100~200℃下反应1~5h,该过程中磷酸酯化聚乙烯醇与氧化石墨烯发生缩聚反应,形成圆柱状三维复合水凝胶;最后,用去离子水洗涤复合水凝胶3~5次后,经冷冻干燥处理即制得还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶。Add the graphene oxide obtained in step S2 into deionized water, mix uniformly, add a predetermined amount of urea, and mix uniformly to obtain a graphene oxide solution; then add the phosphated polyvinyl alcohol obtained in step S1 to the graphene oxide In the solution, after mixing evenly, transfer the above mixed solution to a high-pressure reactor for hydrothermal reaction, and react at 100-200°C for 1-5h. During this process, polycondensation reaction between phosphated polyvinyl alcohol and graphene oxide occurs, A cylindrical three-dimensional composite hydrogel is formed; finally, after the composite hydrogel is washed with deionized water for 3 to 5 times, the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel is obtained through freeze-drying treatment.
优选的,在步骤S1中,聚乙烯醇、N,N-二甲基甲酰胺及五氧化二磷三者的质量比为(1~3):(10~100):(1~3)。Preferably, in step S1, the mass ratio of polyvinyl alcohol, N,N-dimethylformamide and phosphorus pentoxide is (1-3):(10-100):(1-3).
优选的,在步骤S1中,反应温度为100~200℃,反应时间为1~5h。Preferably, in step S1, the reaction temperature is 100-200° C., and the reaction time is 1-5 h.
优选的,在步骤S2中,石墨粉、硫酸、高锰酸钾、硝酸钠及双氧水的质量比为(1~3):(10~50):(1~3):(1~10):(10~50)。Preferably, in step S2, the mass ratio of graphite powder, sulfuric acid, potassium permanganate, sodium nitrate and hydrogen peroxide is (1~3):(10~50):(1~3):(1~10): (10-50).
优选的,在步骤S2中,油浴反应的反应温度为10~100℃,反应时间为100~200min。Preferably, in step S2, the reaction temperature of the oil bath reaction is 10-100° C., and the reaction time is 100-200 min.
优选的,在步骤S3中,氧化石墨烯、尿素及磷酸酯化聚乙烯醇的质量比为(1~3):(10~100):(1~3)。Preferably, in step S3, the mass ratio of graphene oxide, urea and phosphated polyvinyl alcohol is (1-3):(10-100):(1-3).
优选的,在步骤S3中,反应温度为100~200℃,反应时间为1~5h。Preferably, in step S3, the reaction temperature is 100-200° C., and the reaction time is 1-5 h.
优选的,在步骤S3中,制得的复合气凝胶的高度为0.5~3cm,复合气凝胶的高度由水热反应过程中溶液的加入体积决定。Preferably, in step S3, the prepared composite airgel has a height of 0.5-3 cm, and the height of the composite airgel is determined by the added volume of the solution during the hydrothermal reaction.
优选的,在步骤S3中,冷冻干燥处理的时间为48h。Preferably, in step S3, the freeze-drying time is 48 hours.
特别地,本发明还提供了氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的应用方法,包括如下步骤:将直径为2cm高度为0.5~3cm的复合气凝胶放置在待处理的水体中,使环境的温度和湿度为恒定值时,采用模拟太阳光照射,通过电子分析天平监测到的水体和还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的质量之和的变化,计算太阳光驱动的光热蒸发速率;上述过程中太阳光强度为50~300mW cm-2,风速为1.5~2.5m s-1,上述水体为盐水、实际海水、黑臭水体或重金属染料废水。In particular, the present invention also provides an application method of graphene oxide/phosphated polyvinyl alcohol composite airgel, comprising the following steps: placing a composite airgel with a diameter of 2 cm and a height of 0.5 to 3 cm in the water body to be treated In the process, when the temperature and humidity of the environment are kept at a constant value, using simulated sunlight irradiation, the change of the sum of the mass of the water body and the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel monitored by the electronic analytical balance, Calculate the solar-driven photothermal evaporation rate; the solar intensity in the above process is 50-300mW cm -2 , the wind speed is 1.5-2.5ms -1 , and the above-mentioned water body is salt water, actual sea water, black and odorous water or heavy metal dye wastewater.
下面结合具体的实施例对本发明提出的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的制备方法及其应用作进一步说明:The preparation method and application of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel proposed by the present invention will be further described below in conjunction with specific examples:
实施例1Example 1
本实施例制备了一种还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶,包括如下制备步骤:In this embodiment, a reduced graphene oxide/phosphated polyvinyl alcohol composite airgel is prepared, which includes the following preparation steps:
S1、制备磷酸酯化聚乙烯醇:将聚乙烯醇和N,N-二甲基甲酰胺加入到五口烧瓶中,再加入五氧化二磷混合均匀后,其中,聚乙烯醇、N,N-二甲基甲酰胺及五氧化二磷的质量比为1.25:50:1;将五口烧瓶转移至130℃油浴环境中反应4h;待反应结束后,用去离子水洗涤产物,烘干后制得磷酸酯化聚乙烯醇;S1. Preparation of phosphated polyvinyl alcohol: Add polyvinyl alcohol and N, N-dimethylformamide to a five-necked flask, and then add phosphorus pentoxide and mix evenly. Among them, polyvinyl alcohol, N, N- The mass ratio of dimethylformamide to phosphorus pentoxide is 1.25:50:1; transfer the five-neck flask to an oil bath environment at 130°C for 4 hours; after the reaction is complete, wash the product with deionized water, and dry it Prepare phosphated polyvinyl alcohol;
S2、制备氧化石墨烯:采用改进Hummers法制备氧化石墨烯,具体的制备过程如下:在磁力搅拌条件下,将石墨粉和硫酸加入到五口烧瓶中混合均匀,再依次加入硝酸钠和高锰酸钾,再将盛装上述混合物的五口烧瓶转移至35℃的油浴锅中反应2h,加入去离子水后进行升温反应,再加入去离子水和双氧水进行反应,反应结束后将溶液用盐酸和去离子水洗涤3~5次,再经干燥,即可制得氧化石墨烯;其中,石墨粉、硫酸、硝酸钠、高锰酸钾及双氧水的质量比为1:46:1:6:20;S2. Preparation of graphene oxide: graphene oxide was prepared by the improved Hummers method. The specific preparation process was as follows: under magnetic stirring conditions, graphite powder and sulfuric acid were added to a five-necked flask and mixed evenly, and then sodium nitrate and high manganese were added in turn. Potassium acid, and then transfer the five-necked flask containing the above mixture to an oil bath at 35°C for reaction for 2 hours, add deionized water, then heat up the reaction, then add deionized water and hydrogen peroxide to react, after the reaction, the solution is washed with hydrochloric acid Wash with deionized water for 3 to 5 times, and then dry to obtain graphene oxide; wherein, the mass ratio of graphite powder, sulfuric acid, sodium nitrate, potassium permanganate and hydrogen peroxide is 1:46:1:6: 20;
S3、制备还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶;S3. Prepare reduced graphene oxide/phosphated polyvinyl alcohol composite airgel;
将步骤S2得到的氧化石墨烯加入到去离子水中,混合均匀后加入预定量的尿素,混合均匀后得到氧化石墨烯溶液;再将步骤S1制得的磷酸酯化聚乙烯醇加入到氧化石墨烯溶液中,混合均匀后,将上述混合溶液转移至高压反应釜中进行水热反应,在160℃下反应3h,即可制得圆柱状三维还原氧化石墨烯/磷酸酯化聚乙烯醇复合水凝胶;用去离子水洗涤复合水凝胶3遍后,经冷冻干燥处理48h即制得还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶,其中,氧化石墨烯、尿素及磷酸酯化聚乙烯醇的质量比为1:30:1。Add the graphene oxide obtained in step S2 into deionized water, mix uniformly, add a predetermined amount of urea, and mix uniformly to obtain a graphene oxide solution; then add the phosphated polyvinyl alcohol obtained in step S1 to the graphene oxide solution, after mixing evenly, transfer the above mixed solution to an autoclave for hydrothermal reaction, and react at 160°C for 3 hours to prepare a cylindrical three-dimensional reduced graphene oxide/phosphated polyvinyl alcohol composite hydrogel glue; after washing the composite hydrogel with deionized water for 3 times, the reduced graphene oxide/phosphorylated polyvinyl alcohol composite airgel was prepared by freeze-drying for 48 hours, in which graphene oxide, urea and phosphated polyvinyl alcohol The mass ratio of polyvinyl alcohol is 1:30:1.
对制得的复合气凝胶进行表征,表征所得图谱如图2至8所示,其中图2为还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的SEM图,从图中可以看出还原氧化石墨烯/磷酸酯化聚乙烯醇混合气凝胶具有自组装的三维互联结构,包括随机分布的内部间隙和微米通道。图3为还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的XRD图,还原氧化石墨烯气凝胶在25.1°处出现了特征衍射峰,磷酸酯化聚乙烯醇在22.0°附近出现了宽特征峰,还原氧化石墨烯/磷酸酯化聚乙烯醇混合气凝胶在25.0°附近出现宽峰,这是磷酸酯化聚乙烯醇和还原氧化石墨烯特征峰的叠加。图4为还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的FTIR图,氧化石墨烯的FTIR光谱显示在3412cm-1存在着-OH的拉伸振动峰,在1733cm-1为C=O拉伸振动,在1617cm-1和1050cm-1分别为C=C弯曲振动和C-O拉伸振动。在还原氧化石墨烯FTIR光谱中,1733cm-1处的C=O的峰几乎消失,-OH的峰仍然存在但变弱。磷酸酯化聚乙烯醇在1210、1080和935cm-1处的峰值分别为P=O、P-O-C和P-OH,证明聚乙烯醇已被磷酸酯化。在还原氧化石墨烯/磷酸酯化聚乙烯醇混合气凝胶FTIR光谱中均存在C=C、P=O、P-O-C、P-OH等官能团,证明材料成功制备。图5为还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的XPS图,在XPS光谱中,P存在,表明还原氧化石墨烯/磷酸酯化聚乙烯醇混合气凝胶复合成功。图6为还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的吸收光谱图,吸光度在94%以上。图7为还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的Raman光谱图,可以分为自由水和中间水,中间水更容易从聚合物网络中蒸发变成蒸汽,因此中间水的存在可以降低蒸发所需的能量。图8为还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的DSC图,还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的蒸发焓为1512J g-1,远低于纯水的蒸发焓(2422J g-1)。The obtained composite airgel is characterized, and the obtained spectra of the characterization are shown in Figures 2 to 8, wherein Figure 2 is the SEM image of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel, as can be seen from the figure The reduced graphene oxide/phosphated polyvinyl alcohol hybrid airgel has a self-assembled three-dimensional interconnected structure, including randomly distributed internal gaps and micron channels. Figure 3 is the XRD pattern of the reduced graphene oxide/phosphorylated polyvinyl alcohol composite airgel. The reduced graphene oxide airgel has a characteristic diffraction peak at 25.1°, and the phosphated polyvinyl alcohol appears near 22.0°. A broad characteristic peak was found, and the reduced graphene oxide/phosphated polyvinyl alcohol hybrid airgel showed a broad peak around 25.0°, which was the superposition of the characteristic peaks of phosphorylated polyvinyl alcohol and reduced graphene oxide. Figure 4 is the FTIR figure of the reduced graphene oxide/phosphorylated polyvinyl alcohol composite airgel. The FTIR spectrum of graphene oxide shows that there is a stretching vibration peak of -OH at 3412cm- 1 , and C= at 1733cm -1 O stretching vibration, C=C bending vibration and CO stretching vibration at 1617cm -1 and 1050cm -1 respectively. In the FTIR spectrum of reduced graphene oxide, the peak of C=O at 1733 cm -1 almost disappeared, and the peak of -OH still existed but became weaker. The peaks of phosphated polyvinyl alcohol at 1210, 1080 and 935 cm -1 are P=O, POC and P-OH respectively, which proves that polyvinyl alcohol has been phosphorylated. Functional groups such as C=C, P=O, POC, and P-OH exist in the FTIR spectrum of the reduced graphene oxide/phosphated polyvinyl alcohol hybrid airgel, which proves that the material was successfully prepared. Figure 5 is the XPS image of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel. In the XPS spectrum, P exists, indicating that the reduced graphene oxide/phosphated polyvinyl alcohol hybrid airgel is successfully composited. Fig. 6 is an absorption spectrum diagram of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel, and the absorbance is above 94%. Figure 7 is the Raman spectrum of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel, which can be divided into free water and intermediate water. The intermediate water is more likely to evaporate from the polymer network into steam, so the intermediate water Presence can reduce the energy required for evaporation. Figure 8 is the DSC chart of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel. The evaporation enthalpy of the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel is 1512J g -1 , much lower than that of pure Enthalpy of evaporation of water (2422J g -1 ).
特别地,本发明还探究了上述还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的光热蒸发性能,具体操作步骤如下:分别将高度为0.5cm、1cm、2cm、3cm,直径为2cm的复合气凝胶置于纯水中,在强度为100mW cm-2的模拟太阳光下,纯水的蒸发情况如图9所示,蒸发速率分别为2.49、3.27、4.10、4.89kg m-2h-1,结果表明,高度为3cm的光热蒸发速率最高。In particular, the present invention also explores the photothermal evaporation performance of the above-mentioned reduced graphene oxide/phosphated polyvinyl alcohol composite airgel. The specific operation steps are as follows: The 2cm composite airgel is placed in pure water. Under the simulated sunlight with an intensity of 100mW cm -2 , the evaporation of pure water is shown in Figure 9, and the evaporation rates are 2.49, 3.27, 4.10, and 4.89kg m - 2 h -1 , the results show that the photothermal evaporation rate is the highest at the height of 3cm.
同时,本发明还探究了高度为3cm、直径为2cm的复合气凝胶在不同测试条件下的光热转化性,具体地,在强度为50、100、200及300mW cm-2的模拟太阳光下,纯水的蒸发速率分别为2.74、4.89、7.10、9.21kg m-2h-1;在风速为1.5,2.0和2.5m s-1时,纯水的蒸发速率分别为12.84、15.07、16.22kg m-2h-1;在浓度为3.5wt%和15wt%的盐水中,强度为100mW cm-2的模拟太阳光下,盐水中的蒸发速率分别为4.69、4.38kg m-2h-1;当风速为1.5,2.0和2.5ms-1时,纯水的蒸发速率分别为12.84、15.07、16.22kg m-2h-1,在3.5wt%的盐水的蒸发速率分别为12.59、14.04、15.41kg m-2h-1。At the same time, the present invention also explores the photothermal conversion of composite airgel with a height of 3 cm and a diameter of 2 cm under different test conditions, specifically, simulated sunlight with an intensity of 50, 100, 200 and 300 mW cm -2 The evaporation rates of pure water are 2.74, 4.89, 7.10, 9.21kg m -2 h -1 respectively; when the wind speed is 1.5, 2.0 and 2.5ms -1 , the evaporation rates of pure water are 12.84, 15.07, 16.22kg m -2 h -1 ; in the brine with a concentration of 3.5wt% and 15wt%, under simulated sunlight with an intensity of 100mW cm -2 , the evaporation rates in brine are 4.69, 4.38kg m -2 h -1 respectively; When the wind speed is 1.5, 2.0 and 2.5ms -1 , the evaporation rates of pure water are 12.84, 15.07, 16.22kg m -2 h -1 respectively, and the evaporation rates of 3.5wt% brine are 12.59, 14.04, 15.41kg m -2 h -1 .
结果表明,本发明制得的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶在应用于盐水蒸发时,具有较高的蒸发效率和良好的抗盐特性;这是因为复合气凝胶中磷酸酯化聚乙烯醇的引入可赋予复合气凝胶超亲水性,利于将盐水输送至蒸发界面再借助于氧化石墨烯的光学性能将光能转化为热能,进而使盐水中的水分进行蒸发,输送和蒸发的过程中盐水中的盐分结晶与盐分溶解达到动态平衡,因而不会堵塞气凝胶的孔道结构和阻碍盐水输送至蒸发界面,同时,该过程中还可利用磷酸酯化聚乙烯醇与氧化石墨烯之间形成的网络结构与水之间的相互作用,使水分子活化,减少水蒸发所需的能量,从而提高水分子的蒸发速率。The results show that the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel prepared by the present invention has higher evaporation efficiency and good salt resistance characteristics when applied to salt water evaporation; this is because the composite airgel The introduction of phosphated polyvinyl alcohol can endow the composite airgel with superhydrophilicity, which is beneficial to transport the brine to the evaporation interface and then convert the light energy into heat energy with the help of the optical properties of graphene oxide, and then make the water in the brine evaporate. During the process of evaporation, transportation and evaporation, the salt crystallization and salt dissolution in the brine reach a dynamic balance, so the pore structure of the airgel will not be blocked and the brine will not be transported to the evaporation interface. The interaction between the network structure formed between vinyl alcohol and graphene oxide and water activates water molecules and reduces the energy required for water evaporation, thereby increasing the evaporation rate of water molecules.
实施例2至3Examples 2 to 3
实施例2至3与实施例1的区别仅在于:在步骤S1中,聚乙烯醇、N,N-二甲基甲酰胺、五氧化二磷的质量比不同,其他步骤与实施例1基本相同,在此不再赘述。实施例2至3中聚乙烯醇、N,N-二甲基甲酰胺、五氧化二磷的质量比的设置如表1所示,结果表明,复合气凝胶的蒸发速率受磷酸酯化聚乙烯醇制备过程中聚乙烯醇、N,N-二甲基甲酰胺、五氧化二磷的质量比的影响,当聚乙烯醇、N,N-二甲基甲酰胺、五氧化二磷的质量比为1.25:50:1时,复合气凝胶的蒸发速率最高。The difference between
表1实施例1至3中制备磷酸酯化聚乙烯醇时聚乙烯醇、N,N-二甲基甲酰胺、五氧化二磷的质量比的设置及制得的复合气凝胶的蒸发速率The setting of the mass ratio of polyvinyl alcohol, N, N-dimethylformamide, phosphorus pentoxide and the evaporation rate of the composite airgel obtained when preparing phosphated polyvinyl alcohol in Table 1
实施例4至5Examples 4 to 5
实施例4至5与实施例1的区别仅在于:在步骤S1中,反应温度不同,其他步骤与实施例1基本相同,在此不再赘述。实施例4至5中反应温度的设置如表2所示,结果表明,结果表明,在反应温度为100℃和200℃时,制得的复合气凝胶的蒸发速率降低。The difference between Embodiments 4 to 5 and
表2实施例1与实施例4至5中制备磷酸酯化聚乙烯醇时反应温度的设置及制得的复合气凝胶的蒸发速率The setting of reaction temperature and the evaporation rate of the composite airgel when preparing phosphated polyvinyl alcohol in Table 2
实施例6至7Examples 6 to 7
实施例6至7与实施例1的区别仅在于:在步骤S1中,反应时间不同,其他步骤与实施例1基本相同,在此不再赘述。实施例6至7中反应时间的设置如表3所示,结果表明,复合气凝胶的性能受制备磷酸酯化聚乙烯醇时的反应时间的影响,且在一定的反应时间下,制得的复合气凝胶的蒸发速率最高。The difference between Embodiments 6 to 7 and
表3实施例1与实施例6至7中制备磷酸酯化聚乙烯醇时反应时间的设置及制得的复合气凝胶的蒸发速率Table 3 Example 1 and Examples 6 to 7 when preparing phosphated polyvinyl alcohol, the setting of reaction time and the evaporation rate of the composite airgel made
对比例1Comparative example 1
对比例1与实施例1的区别仅在于:制备复合气凝胶的过程中,直接利用聚乙烯醇代替实施例1中的磷酸酯化聚乙烯醇制备复合气凝胶,对比例1在模具中冷冻,实施例是在高温反应釜中进行自缩聚反应。为比较对比例1制得的聚乙烯醇/氧化石墨烯气凝胶与实施例1制得的复合气凝胶的光热转化效率,将二者在同一条件下进行光热水蒸发试验,结果表明:聚乙烯醇/氧化石墨烯气凝胶的蒸发速率低于复合气凝胶的蒸发速率,这是因为聚乙烯醇/氧化石墨烯气凝胶中水分传输较慢,且气凝胶网络中水分子蒸发所需的能量比复合气凝胶的高。The difference between Comparative Example 1 and Example 1 is that in the process of preparing the composite airgel, polyvinyl alcohol is directly used to replace the phosphated polyvinyl alcohol in Example 1 to prepare the composite airgel, and Comparative Example 1 is in the mold Freezing, the embodiment is to carry out self-condensation reaction in high temperature reactor. In order to compare the light-to-heat conversion efficiency of the polyvinyl alcohol/graphene oxide airgel prepared in Comparative Example 1 and the composite airgel prepared in Example 1, the two were subjected to a photothermal water evaporation test under the same conditions, and the results It shows that the evaporation rate of polyvinyl alcohol/graphene oxide airgel is lower than that of composite airgel, because the moisture transport in polyvinyl alcohol/graphene oxide airgel is slow and the airgel network The energy required for water molecules to evaporate is higher than for composite aerogels.
对比例2Comparative example 2
对比例2与对比例1的区别在于:在步骤S3中,将聚乙烯醇加入氧化石墨烯溶液中后,还继续加入了纳米纤维分散液、丁烷四羧酸和次亚磷酸钠,其中,聚乙烯醇与纳米纤维分散液中的纳米纤维的质量比为3:10,丁烷四羧酸和次亚磷酸钠的质量与聚乙烯醇相同;后续步骤均与对比例1一致,在此不再赘述。The difference between comparative example 2 and comparative example 1 is: in step S3, after polyvinyl alcohol is added in the graphene oxide solution, also continue to add nanofiber dispersion liquid, butane tetracarboxylic acid and sodium hypophosphite, wherein, The mass ratio of polyvinyl alcohol and the nanofibers in the nanofiber dispersion liquid is 3:10, and the quality of butane tetracarboxylic acid and sodium hypophosphite is identical with polyvinyl alcohol; Subsequent steps are all consistent with comparative example 1, not here Let me repeat.
将对比例2制得的复合气凝胶与实施例1制得的复合气凝胶在同一条件下进行水蒸发,本对比例制得的复合气凝胶的蒸发速率为2.28kg m-2h-1,该数值明显低于实施例1的蒸发速率4.89kg m-2h-1,结果表明本发明提出的方法制得的复合气凝胶能够实现优异吸光性、超亲水性、低蒸发焓和环境增强的有效结合,显示出更为优异的光热转化性。The composite airgel obtained in Comparative Example 2 and the composite airgel obtained in Example 1 were evaporated under the same conditions, and the evaporation rate of the composite airgel obtained in this comparative example was 2.28 kg m -2 h -1 , which is significantly lower than the evaporation rate of Example 1, 4.89kg m -2 h -1 , and the results show that the composite airgel prepared by the method proposed in the present invention can achieve excellent light absorption, superhydrophilicity, and low evaporation The effective combination of enthalpy and environmental enhancement shows more excellent light-to-heat conversion.
综上所述,本发明提出的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶的制备方法,利用磷酸酯化聚乙烯醇和氧化石墨烯之间的缩聚反应制得复合气凝胶,可充分利用磷酸酯化聚乙烯醇的超亲水性及氧化石墨烯自身优异的光学性能和较高的比表面积,制得机械性能强、超亲水性、低热传导率且光热转化效率高的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶;磷酸酯化聚乙烯醇的引入,不仅可赋予复合气凝胶超亲水性,使其在用于水体蒸发时,更易将水体输送至蒸发界面,还可利用磷酸酯化聚乙烯醇与氧化石墨烯之间形成的网络结构与水之间的相互作用,使水分子活化,减少水蒸发所需的能量,同时结合氧化石墨烯的光热转化性能,有效提升水蒸发速率。应用本发明提出的方法制得的还原氧化石墨烯/磷酸酯化聚乙烯醇复合气凝胶,能够应用于盐水、实际海水、黑臭水体或重金属染料废水中的水分子蒸发并获得清洁的水资源。In summary, the method for preparing the reduced graphene oxide/phosphated polyvinyl alcohol composite airgel proposed by the present invention utilizes the polycondensation reaction between the phosphorylated polyvinyl alcohol and graphene oxide to prepare the composite airgel, It can make full use of the superhydrophilicity of phosphated polyvinyl alcohol and the excellent optical properties and high specific surface area of graphene oxide itself to obtain strong mechanical properties, superhydrophilicity, low thermal conductivity and high photothermal conversion efficiency. The reduced graphene oxide/phosphorylated polyvinyl alcohol composite airgel; the introduction of phosphated polyvinyl alcohol can not only endow the composite airgel with superhydrophilicity, but also make it easier for the water body to evaporate when it is used for water evaporation. Transported to the evaporation interface, the interaction between the network structure formed between phosphated polyvinyl alcohol and graphene oxide and water can also be used to activate water molecules, reduce the energy required for water evaporation, and combine graphene oxide Excellent light-to-heat conversion performance, effectively improving the water evaporation rate. The reduced graphene oxide/phosphated polyvinyl alcohol composite airgel prepared by the method proposed in the present invention can be applied to the evaporation of water molecules in salt water, actual seawater, black and odorous water or heavy metal dye wastewater to obtain clean water resource.
以上实施例仅用以说明本发明的技术方案而非限制,尽管参照较佳实施例对本发明进行了详细说明,本领域的普通技术人员应当理解,可以对本发明的技术方案进行修改或者等同替换,而不脱离本发明技术方案的精神和范围。The above embodiments are only used to illustrate the technical solutions of the present invention without limitation. Although the present invention has been described in detail with reference to preferred embodiments, those of ordinary skill in the art should understand that the technical solutions of the present invention can be modified or equivalently replaced. Without departing from the spirit and scope of the technical solution of the present invention.
Claims (10)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211071700.0A CN115400699B (en) | 2022-09-02 | 2022-09-02 | Preparation method and application of reduced graphene oxide/phosphate polyvinyl alcohol composite aerogel |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211071700.0A CN115400699B (en) | 2022-09-02 | 2022-09-02 | Preparation method and application of reduced graphene oxide/phosphate polyvinyl alcohol composite aerogel |
Publications (2)
Publication Number | Publication Date |
---|---|
CN115400699A true CN115400699A (en) | 2022-11-29 |
CN115400699B CN115400699B (en) | 2023-06-16 |
Family
ID=84162798
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202211071700.0A Active CN115400699B (en) | 2022-09-02 | 2022-09-02 | Preparation method and application of reduced graphene oxide/phosphate polyvinyl alcohol composite aerogel |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN115400699B (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN115710034A (en) * | 2023-01-09 | 2023-02-24 | 北京科技大学 | Composite aerogel based on graphdiyne elementary structure and preparation method thereof |
CN116004188A (en) * | 2022-12-17 | 2023-04-25 | 安徽大学 | High polymer composite graphene aerogel and composite phase change material prepared from same |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109280540A (en) * | 2018-09-20 | 2019-01-29 | 赵建平 | It is a kind of using graphene aerogel as energy storage material of matrix and preparation method thereof |
CN109554164A (en) * | 2017-09-26 | 2019-04-02 | 西南科技大学 | A kind of composite phase-change material and preparation method thereof |
CN112387258A (en) * | 2020-11-12 | 2021-02-23 | 济南大学 | Adsorbent for ultra-fast removing heavy metal ions in acidic wastewater |
CN114405421A (en) * | 2022-03-15 | 2022-04-29 | 北京化工大学 | Cellulose nanofiber aerogel photothermal interface water evaporation material and preparation method thereof |
-
2022
- 2022-09-02 CN CN202211071700.0A patent/CN115400699B/en active Active
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109554164A (en) * | 2017-09-26 | 2019-04-02 | 西南科技大学 | A kind of composite phase-change material and preparation method thereof |
CN109280540A (en) * | 2018-09-20 | 2019-01-29 | 赵建平 | It is a kind of using graphene aerogel as energy storage material of matrix and preparation method thereof |
CN112387258A (en) * | 2020-11-12 | 2021-02-23 | 济南大学 | Adsorbent for ultra-fast removing heavy metal ions in acidic wastewater |
CN114405421A (en) * | 2022-03-15 | 2022-04-29 | 北京化工大学 | Cellulose nanofiber aerogel photothermal interface water evaporation material and preparation method thereof |
Non-Patent Citations (2)
Title |
---|
安承超: "氧化石墨烯和石墨烯有机凝胶的制备与性能" * |
宋鸽: "磷酸化聚乙烯醇水凝胶网膜的制备及其性能研究" * |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116004188A (en) * | 2022-12-17 | 2023-04-25 | 安徽大学 | High polymer composite graphene aerogel and composite phase change material prepared from same |
CN115710034A (en) * | 2023-01-09 | 2023-02-24 | 北京科技大学 | Composite aerogel based on graphdiyne elementary structure and preparation method thereof |
CN115710034B (en) * | 2023-01-09 | 2023-05-26 | 北京科技大学 | A kind of composite airgel based on graphyne unit sequence and its preparation method |
US20240228297A1 (en) * | 2023-01-09 | 2024-07-11 | University Of Science And Technology Beijing | Composite aerogel based on graphdiyne motif arrangement and preparation method thereof |
US12071349B2 (en) * | 2023-01-09 | 2024-08-27 | University Of Science And Technology Beijing | Composite aerogel based on graphdiyne motif arrangement and preparation method thereof |
Also Published As
Publication number | Publication date |
---|---|
CN115400699B (en) | 2023-06-16 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN115400699B (en) | Preparation method and application of reduced graphene oxide/phosphate polyvinyl alcohol composite aerogel | |
CN114405421B (en) | A kind of cellulose nanofiber airgel photothermal interface water evaporation material and preparation method thereof | |
CN104355302B (en) | The preparation method of a kind of Graphene/polyimide-based carbon aerogels | |
CN112934129B (en) | Efficient photo-thermal water evaporation carbon nanotube hydrogel and preparation method and application thereof | |
CN111285704B (en) | Cellulose source carbon-based photothermal conversion material for seawater desalination and preparation method thereof | |
CN104925796B (en) | A kind of preparation method of porous class grapheme material | |
CN104250005A (en) | Graphene aerogel as well as preparation method and application thereof | |
CN104086783A (en) | Method for preparing graphene oxide/carbon nano tube/cellulose composite gel from ionic liquid | |
CN113321939B (en) | Polypyrrole-coated fragrant cattail wool-based ultra-light biomass porous foam and preparation method and application thereof | |
CN104671241B (en) | A method of activating waste bakelite to prepare activated carbon with high specific surface area | |
CN106744789A (en) | A kind of utilization lignin prepares porous charcoal and the application in ultracapacitor | |
CN113860413A (en) | Solar evaporator based on biomass hydrogel/nano carbon material and application thereof | |
Zhang et al. | A self-floating integrated hydrogel evaporator with efficient salt resistance and thermal localization for efficient solar water desalination | |
Song et al. | Biomass-derived porous carbon aerogels for effective solar thermal energy storage and atmospheric water harvesting | |
Hu et al. | A novel metal-organic framework aerogel based hydrated salt composite phase change material for enhanced solar thermal utilization | |
Zheng et al. | Compressible polyaniline-coated sodium alginate-cattail fiber foam for efficient and salt-resistant solar steam generation | |
CN110217774A (en) | A kind of starch base hollow carbon micro-sphere material and preparation method thereof and heat accumulation application | |
CN111346576A (en) | Preparation method of graphene-based hydrogel with three-dimensional network structure and photo-thermal desalted water treatment application of graphene-based hydrogel | |
Li et al. | Highly efficient carbonization of nanocellulose to biocarbon aerogels with ultrahigh light absorption efficiency and evaporation rate as bifunctional solar/electric driven steam generator for water purification | |
CN106185921A (en) | A kind of method and purposes preparing porous carbon materials with NaCl for hard template | |
Li et al. | Catkins based flexible photothermal materials for solar driven interface evaporation collaborative power generation | |
Wang et al. | All-biobased porous aerogels with low evaporation enthalpy for efficient solar interfacial evaporation | |
CN111204829B (en) | Solar sewage purification aerogel based on waste paper and graphite and preparation method thereof | |
Lu et al. | Double-layered solar evaporator based on polymeric ionic liquid grafted attapulgite and MXene/PPy for efficient desalination and photodegradation | |
CN113122190A (en) | Aerogel composite material 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 |