CN104338519A - Modified graphene-loaded polyurethane sponge and preparation method thereof - Google Patents
Modified graphene-loaded polyurethane sponge and preparation method thereof Download PDFInfo
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Abstract
Description
技术领域 technical field
本发明涉及一种改性石墨烯负载聚氨酯海绵及其制备方法。 The invention relates to a modified graphene-loaded polyurethane sponge and a preparation method thereof.
背景技术 Background technique
随着近代工业的迅猛发展,陆地资源的日趋匮乏和人类对能源需求的迅速增长,浅海油气资源得到不断开发。但是随着海底石油与原油等的开发,其产品也不断在海上运输,这就不可避免的产生了很多海洋油污染事件,如开发时井喷事故和运输油船的泄露事故等。海洋上的油外泄不仅给我们带来了巨大的经济损失,更重要的是对海洋生态环境及周边海岸造成了重大的污染。首先,石油会严重危害水生生物的生存,海洋哺乳类动物摄入溢油后,内脏功能遭到损害,某些石油组分能使哺乳性动物和游离菌类对化学刺激的知觉失调,并阻碍水体生物间的化学信息传递;油污会使水鸟的羽毛丧失防水保暖作用,翅膀粘有油污也难以飞行。有研究表明:水面只要有极薄的油膜,就会明显地改变阳光、空气对水体的“输入”,从而造成鸟类食用的海藻和其它低等水生生物的死亡。加之油品的毒性,造成生态环境急剧恶化,甚至能够诱发海洋赤潮。据报道,近50年来因油污染已有1000多种海生生物灭绝,海洋生物已减少了40%;另外,溢油对人体健康也产生重要的影响。Comet通过试验分析了受溢油污染的贝壳类动物体内的毒物积累,发现了一定浓度的多环芳烃(PAH),人们如果食用了吸收石油的鱼贝类,就会将石油中的长效毒物如致癌物带入体内。再者,石油挥发形成的有机蒸汽扩散到大气中也会污染大气环境,引发光化学烟雾,同样会刺激人类的视觉,损害环境中的有机物,引起植物坏死等。 With the rapid development of modern industry, the increasing scarcity of land resources and the rapid growth of human demand for energy, shallow sea oil and gas resources have been continuously developed. However, with the development of submarine oil and crude oil, their products are also continuously transported at sea, which inevitably produces many marine oil pollution incidents, such as blowout accidents during development and leakage accidents from transport tankers. Oil spills on the ocean not only brought us huge economic losses, but more importantly, caused significant pollution to the marine ecological environment and surrounding coasts. First of all, oil will seriously endanger the survival of aquatic organisms. After marine mammals ingest oil spills, their visceral functions will be damaged. Certain oil components can make mammals and free fungi lose their sense of chemical stimulation and hinder The transfer of chemical information between aquatic organisms; oil pollution will make the feathers of waterfowls lose their waterproof and warm-keeping effect, and it will be difficult to fly with oily wings. Studies have shown that as long as there is an extremely thin oil film on the water surface, the "input" of sunlight and air to the water body will be significantly changed, thereby causing the death of seaweed and other low-level aquatic organisms eaten by birds. Coupled with the toxicity of the oil, the ecological environment has deteriorated sharply, and it can even induce marine red tides. According to reports, over the past 50 years, more than 1,000 species of marine life have become extinct due to oil pollution, and marine life has decreased by 40%. In addition, oil spills also have an important impact on human health. Comet analyzed the accumulation of toxins in shellfish polluted by oil spills through experiments, and found a certain concentration of polycyclic aromatic hydrocarbons (PAH). Such as carcinogens into the body. Furthermore, the diffusion of organic vapors formed by volatilization of oil into the atmosphere will also pollute the atmospheric environment and cause photochemical smog, which will also stimulate human vision, damage organic matter in the environment, and cause plant necrosis.
为了治理海洋石油污染,最大限度降低其危害,国内外众多学者进行了多方面的研究。而目前常见的治理方法有机械法、燃烧法、生物修复法、材料吸收法等。物理上的机械回收法,不仅解决了海洋上浮油问题,还将能源回收利用没有浪费,但围油栏却不能确保迅速、完全地控制油扩散的趋势,故其还是有一定局限性。燃烧法看似是最简单的方法,但是燃烧后的产物会给环境造成二次污染,因此到目前为止所有的公海漏油事件都没有采用过该种方法。生物修复法多采用的是表面活性剂来实现,尤其是生物表面活性剂结合了表面活性剂的疏水性和微生物的降解功能,可以达到高效、无毒、抗菌、经济、易降解及无二次污染等优点,但是考虑到工业成本、生态平衡和时间较长等问题,也不被常用作溢油污染处理。目前材料吸收法,由于其高效、快速、不产生二次污染,且能进行回收利用等优点,成为溢油污染处理的首选方法。现今吸收剂的种类有聚合类吸收剂、天然材料吸收剂以及纤维材料吸收剂等,其中石墨烯由于其独特的二维结构,及其特殊的疏水亲油特性,其作为一种涂层材料已经成为吸油材料研究的热点,但是利用γ-甲基丙烯酰氧基丙基三甲氧基硅烷(KH-570)改性石墨烯负载到聚氨酯海绵上的方法尚未被研究。 In order to control marine oil pollution and minimize its harm, many scholars at home and abroad have conducted various researches. At present, the common treatment methods include mechanical method, combustion method, bioremediation method, material absorption method and so on. The physical mechanical recovery method not only solves the problem of oil slicks on the ocean, but also recycles energy without wasting energy. However, the oil boom cannot ensure rapid and complete control of the oil diffusion trend, so it still has certain limitations. The combustion method seems to be the simplest method, but the products after combustion will cause secondary pollution to the environment, so all oil spills on the high seas have not adopted this method so far. Bioremediation is mostly implemented by surfactants, especially biosurfactants that combine the hydrophobicity of surfactants and the degradation function of microorganisms, which can achieve high efficiency, non-toxic, antibacterial, economical, easy to degrade and no secondary Pollution and other advantages, but considering the industrial cost, ecological balance and long time, it is not often used for oil spill pollution treatment. At present, the material absorption method has become the preferred method for oil spill pollution treatment due to its high efficiency, rapidity, no secondary pollution, and the ability to recycle. The types of absorbents today include polymeric absorbents, natural material absorbents, and fiber material absorbents. Among them, graphene has been used as a coating material due to its unique two-dimensional structure and special hydrophobic and lipophilic properties. It has become a hotspot in the research of oil-absorbing materials, but the method of using γ-methacryloxypropyltrimethoxysilane (KH-570) to modify graphene loaded on polyurethane sponge has not been studied.
发明内容 Contents of the invention
本发明的目的之一在于提供一种改性石墨烯负载聚氨酯海绵。 One of the objects of the present invention is to provide a modified graphene loaded polyurethane sponge.
本发明的目的之二在于提供该聚氨酯海绵的制备方法。 Two of object of the present invention is to provide the preparation method of this polyurethane sponge.
本发明所提供的是一种使聚氨酯海绵表面达到超疏水超亲油的方法,具体采用的技术方案是:用KH-570的水解产物将氧化石墨烯改性后再还原生成改性的石墨烯,并将其负载到海绵表面,形成具有超疏水性和超亲油性质的材料,对其进行疏水吸油性能测试。 What the present invention provides is a method for making the surface of polyurethane sponge superhydrophobic and superoleophilic. The specific technical solution is: modify graphene oxide with the hydrolyzate of KH-570 and then reduce it to generate modified graphene , and load it on the surface of the sponge to form a material with superhydrophobic and superoleophilic properties, and test its hydrophobic and oil-absorbing properties.
为达到上述目的,本发明采用如下技术方案: To achieve the above object, the present invention adopts the following technical solutions:
一种改性石墨烯负载聚氨酯海绵,其特征在于该聚氨酯海绵是在聚氨酯海绵的表面负载有改性石墨烯涂层,该涂层厚度为0.5~1.0mm;所述的改性石墨烯是在石墨烯表面包覆硅烷偶联剂,其中硅烷偶联剂与石墨烯的质量比为1:100。 A modified graphene-loaded polyurethane sponge is characterized in that the polyurethane sponge is loaded with a modified graphene coating on the surface of the polyurethane sponge, and the coating thickness is 0.5 ~ 1.0mm; the modified graphene is The surface of graphene is coated with silane coupling agent, wherein the mass ratio of silane coupling agent to graphene is 1:100.
上述的改性石墨烯负载聚氨酯海绵的制备方法,其特征在于所述的硅烷偶联剂有:γ-氨丙基三乙氧基硅烷(KH-550),γ-缩水甘油醚氧丙基三甲氧基硅烷(KH-560),γ-甲基丙烯酰氧基丙基三甲氧基硅烷(KH-570)等。 The preparation method of the above-mentioned modified graphene-loaded polyurethane sponge is characterized in that the silane coupling agent has: γ-aminopropyltriethoxysilane (KH-550), γ-glycidyl etheroxypropyltrimethyl Oxysilane (KH-560), γ-methacryloxypropyltrimethoxysilane (KH-570), etc.
一种制备上述的改性石墨烯负载聚氨酯海绵的方法,其特征在于该方法的具体步骤为: A method for preparing above-mentioned modified graphene loaded polyurethane sponge is characterized in that the concrete steps of the method are:
a. 将氧化石墨溶于无水乙醇中配制成浓度为2mg/ml的悬浮液; a. dissolving graphite oxide in absolute ethanol to prepare a suspension with a concentration of 2mg/ml;
b. 将硅烷偶联剂、蒸馏水和无水乙醇按1:1:18的体积比混合,调节该溶液的pH值为4.0~4.5,再加入步骤a所得到的悬浮液中,使氧化石墨与硅烷偶联剂的质量比为100:1;回流反应4h;然后抽滤,滤饼用蒸馏水洗涤,再用乙醇洗涤,将所得改性氧化石墨烯从滤纸上刮下,充分烘干之后称重;分散到乙醇溶液中,配成2mg/ml氧化石墨烯乙醇悬浮液,留待使用; b. Mix the silane coupling agent, distilled water and absolute ethanol in a volume ratio of 1:1:18, adjust the pH value of the solution to 4.0~4.5, and then add it to the suspension obtained in step a to make graphite oxide and The mass ratio of the silane coupling agent is 100:1; reflux reaction for 4 hours; then suction filtration, the filter cake is washed with distilled water, and then washed with ethanol, the obtained modified graphene oxide is scraped off the filter paper, fully dried and weighed ; Dispersed in ethanol solution, made into 2mg/ml graphene oxide ethanol suspension, reserved for use;
c. 将清洗干净的聚氨酯海绵浸没在步骤b所得的悬浮液中1h,然后调节pH为9,之后用水合肼在95℃下将氧化石墨烯还原1.5h;将海绵取出,用去离子水清洗,烘干,即得到改性石墨烯负载聚氨酯海绵 c. Immerse the cleaned polyurethane sponge in the suspension obtained in step b for 1 hour, then adjust the pH to 9, and then reduce the graphene oxide with hydrazine hydrate at 95°C for 1.5 hours; take out the sponge and wash it with deionized water , and dry to obtain the modified graphene-loaded polyurethane sponge
经硅烷偶联剂改性石墨烯负载的海绵对柴油的吸附速率远大于对水的吸附速率,且其吸水率比原始海绵明显下降,而吸油率有所增加,对柴油的饱和吸附量可达37.89g;改性海绵对水的接触角(CA)为161o,具有超疏水性。因此,在聚氨酯海绵表面负载经硅烷偶联剂改性的石墨烯,使得原本既吸水又吸油的海绵具有很好的疏水性和更强的吸油性,这些特征均证明了由硅烷偶联剂水解改性石墨烯负载海绵所制备的海绵材料在吸附水体中石油类污染物的应用中具有更大的潜力。 The adsorption rate of diesel oil on the sponge loaded with graphene modified by silane coupling agent is much higher than that of water, and its water absorption rate is significantly lower than that of the original sponge, while its oil absorption rate is increased, and the saturated adsorption capacity of diesel oil can reach 37.89g; the contact angle (CA) of the modified sponge to water is 161o, which is superhydrophobic. Therefore, loading graphene modified by silane coupling agent on the surface of polyurethane sponge makes the sponge, which is originally both water-absorbing and oil-absorbing, have good hydrophobicity and stronger oil absorption. The sponge material prepared by the modified graphene-loaded sponge has greater potential in the application of adsorbing petroleum pollutants in water bodies.
附图说明 Description of drawings
图1:原始海绵(a)与改性后海绵(b)直观对比图。 Figure 1: Visual comparison of original sponge (a) and modified sponge (b).
图2:原始海绵(a)与改性后海绵(b)疏水性接触角(CA)对比图。 Figure 2: Comparison of the hydrophobic contact angle (CA) of the original sponge (a) and the modified sponge (b).
图3:原始海绵(a)与改性后海绵(b)扫描电镜(SEM)对比图。 Figure 3: Scanning electron microscope (SEM) comparison of original sponge (a) and modified sponge (b).
具体实施方式 Detailed ways
1. 材料准备 1. Material preparation
(1)试剂的准备 (1) Preparation of reagents
主要的试剂有:浓硫酸(H2SO4,98%),硝酸钠(NaNO3),氨水(NH4OH),冰醋酸(CH3COOH),高锰酸钾(KMnO4),过氧化氢(H2O2,30%),盐酸(HCl,5%),氯化钡(BaCl2),无水乙醇(CH3CH2OH),γ-甲基丙烯酰氧基丙基三甲基硅氧烷(KH-570),水合肼(N2H4·H2O)。 The main reagents are: concentrated sulfuric acid (H 2 SO 4 , 98%), sodium nitrate (NaNO 3 ), ammonia water (NH 4 OH), glacial acetic acid (CH 3 COOH), potassium permanganate (KMnO 4 ), peroxide Hydrogen (H 2 O 2 , 30%), hydrochloric acid (HCl, 5%), barium chloride (BaCl 2 ), absolute ethanol (CH 3 CH 2 OH), γ-methacryloxypropyl trimethyl Siloxane (KH-570), Hydrazine Hydrate (N 2 H 4 ·H 2 O).
氧化石墨的制备方法请参考文献:Singh, E., Chen, Z., Houshmand, F., Ren, W., Peles, Y., Cheng, H. M. and Koratkar, N., Superhydrophobic graphene foams, Small, 2013, 9(1): 75-80. For the preparation method of graphite oxide, please refer to the literature: Singh, E., Chen, Z., Houshmand, F., Ren, W., Peles, Y., Cheng, H. M. and Koratkar, N., Superhydrophobic graphene foams, Small, 2013, 9(1): 75-80.
(2)供试海绵 (2) Test sponge
聚氨酯海绵(密度为0.025g/cm3),本地厂家购买。 Polyurethane sponge (density 0.025g/cm 3 ), purchased from a local manufacturer.
(3)实验仪器和设备 (3) Experimental instruments and equipment
集热式磁力搅拌器,FA1004B—分析天平,真空干燥箱,烘箱,超声波清洗机,高速离心机,水浴锅,真空抽滤泵,磁力搅拌油浴锅 Collector magnetic stirrer, FA1004B—analytical balance, vacuum drying oven, oven, ultrasonic cleaner, high-speed centrifuge, water bath, vacuum filter pump, magnetic stirring oil bath
2. 海绵的处理及其疏水亲油特性的测定 2. Treatment of sponges and determination of their hydrophobic and lipophilic properties
(1)海绵的处理 (1) Disposal of sponge
将海绵用去离子水和乙醇进行超声清洗,待用。 The sponges were ultrasonically cleaned with deionized water and ethanol until use.
(2)供试石油 (2) Test oil
零号柴油(中石化明和加油站)。 Zero Diesel (Sinopec Minghe Gas Station).
实施例一: Embodiment one:
1) 氧化石墨烯(GO)的制备。主要方法是冰水浴中,在500mL的烧杯中加入 2g天然鳞片石墨,然后加入46mL 浓H2SO4(98%),加入1g NaNO3,将温度控制在20℃ 以下,边搅拌边加入6g KMnO4,将温度升到35~36℃,溶液在此温度下保持1.5h,此时会有气体放出;将92mL去离子水缓慢加入混合液中,水浴温度随后升至98℃,并在此保持15min,以增加GO的氧化程度;用280mL去离子水稀释混合液,并将6mL 30%的H2O2溶液缓慢加入上述溶液中,若未有亮黄色生成,则继续滴加直至生成亮黄色,混合物经抽滤或离心分离,用5% HCl溶液多次冲洗直至用BaCl2未检出SO4 2-,再用去离子水多次冲洗去除酸,将得到的滤后块状物在60℃干燥,称重后留待备用。 1) Preparation of graphene oxide (GO). The main method is to add 2g of natural flake graphite to a 500mL beaker in an ice-water bath, then add 46mL of concentrated H 2 SO 4 (98%), add 1g of NaNO 3 , control the temperature below 20°C, and add 6g of KMnO while stirring. 4. Raise the temperature to 35~36°C, keep the solution at this temperature for 1.5 hours, at this time, gas will be released; slowly add 92mL deionized water into the mixture, then raise the temperature of the water bath to 98°C, and keep it there 15min to increase the oxidation degree of GO; dilute the mixed solution with 280mL deionized water, and slowly add 6mL 30% H 2 O 2 solution to the above solution, if no bright yellow is formed, continue to drop until bright yellow is formed , the mixture was suction filtered or centrifuged, washed with 5% HCl solution several times until no SO 4 2- was detected with BaCl 2 , then washed with deionized water several times to remove the acid, and the obtained filtered block was °C, dried and weighed for later use.
2) KH-570改性氧化石墨烯的制备。将100mg GO加入250ml烧杯中,加入100ml无水乙醇成为悬浮液,超声2h。另取一个干净小烧杯,加入10ml硅烷偶联剂KH-570,再向其中加入10ml蒸馏水和180ml无水乙醇溶液(三者体积比为1:1:18),进行搅拌,加入36%的乙酸溶液直至溶液的pH值为4.0~4.5,混合均匀后加入到氧化石墨烯的乙醇悬浮液中,继续对体系进行30min超声处理。将体系转入80℃恒温油浴中,进行冷凝回流4h。然后将反应体系真空抽滤,滤饼用100ml蒸馏水洗涤2遍,再用100ml乙醇洗涤3遍。将所得改性氧化石墨烯从滤纸上刮下,充分烘干之后称重;分散到乙醇溶液中,配成2mg/ml氧化石墨烯乙醇悬浮液,留待使用。 2) Preparation of KH-570 modified graphene oxide. Add 100mg GO into a 250ml beaker, add 100ml absolute ethanol to form a suspension, and sonicate for 2h. Take another clean small beaker, add 10ml of silane coupling agent KH-570, then add 10ml of distilled water and 180ml of absolute ethanol solution (the volume ratio of the three is 1:1:18), stir, and add 36% acetic acid Solution until the pH value of the solution is 4.0-4.5, mix evenly, add to the ethanol suspension of graphene oxide, and continue to ultrasonicate the system for 30 minutes. The system was transferred to an 80°C constant temperature oil bath for condensing and reflux for 4 hours. Then the reaction system was vacuum filtered, and the filter cake was washed twice with 100 ml of distilled water, and then washed three times with 100 ml of ethanol. The obtained modified graphene oxide was scraped off from the filter paper, fully dried and then weighed; dispersed in an ethanol solution to prepare a 2 mg/ml graphene oxide ethanol suspension for use.
3) KH-570改性石墨烯负载海绵的制备。将海绵切成长宽高均等的块状,并在乙醇溶液中超声清洗,然后用去离子水冲洗海绵,在60℃烘箱中烘干;将海绵浸入2mg/ml 的GO悬浮液中1h,然后缓慢将氨水溶液滴至GO悬浮液至pH为9,之后用水合肼在95℃下将GO还原1.5h;将海绵取出,用去离子水清洗,并在30℃的真空烘箱中烘干24h,即可得到还原后的GO即改性石墨烯涂层的PU海绵。 3) Preparation of KH-570 modified graphene loaded sponge. Cut the sponge into blocks of equal length, width and height, and ultrasonically clean it in ethanol solution, then rinse the sponge with deionized water, and dry it in an oven at 60°C; soak the sponge in 2mg/ml GO suspension for 1h, then slowly Ammonia solution was dropped into the GO suspension until the pH was 9, and then GO was reduced with hydrazine hydrate at 95 °C for 1.5 h; the sponge was taken out, washed with deionized water, and dried in a vacuum oven at 30 °C for 24 h, that is The reduced GO, that is, the modified graphene-coated PU sponge, can be obtained.
实施例二: Embodiment two:
1) 氧化石墨烯(GO)的制备。主要方法是冰水浴中,在500mL的烧杯中加入 2g天然鳞片石墨,然后加入46mL 浓H2SO4(98%),加入1g NaNO3,将温度控制在20℃ 以下,边搅拌边加入6g KMnO4,将温度升到35~36℃,溶液在此温度下保持1.5h,此时会有气体放出;将92mL去离子水缓慢加入混合液中,水浴温度随后升至98℃,并在此保持15min,以增加GO的氧化程度;用280mL去离子水稀释混合液,并将6mL 30%的H2O2溶液缓慢加入上述溶液中,若未有亮黄色生成,则继续滴加直至生成亮黄色,混合物经抽滤或离心分离,用5% HCl溶液多次冲洗直至用BaCl2未检出SO4 2-,再用去离子水多次冲洗去除酸,将得到的滤后块状物在60℃干燥,称重后留待备用。 1) Preparation of graphene oxide (GO). The main method is to add 2g of natural flake graphite to a 500mL beaker in an ice-water bath, then add 46mL of concentrated H 2 SO 4 (98%), add 1g of NaNO 3 , control the temperature below 20°C, and add 6g of KMnO while stirring. 4. Raise the temperature to 35~36°C, keep the solution at this temperature for 1.5 hours, at this time, gas will be released; slowly add 92mL deionized water into the mixture, then raise the temperature of the water bath to 98°C, and keep it there 15min to increase the oxidation degree of GO; dilute the mixed solution with 280mL deionized water, and slowly add 6mL 30% H 2 O 2 solution to the above solution, if no bright yellow is formed, continue to drop until bright yellow is formed , the mixture was suction filtered or centrifuged, washed with 5% HCl solution several times until no SO 4 2- was detected with BaCl 2 , then washed with deionized water several times to remove the acid, and the obtained filtered block was °C, dried and weighed for later use.
2) KH-560改性氧化石墨烯的制备(吕翔,2011)。将100mg石墨烯分散于100ml无水乙醇中,加入2ml水,5ml乙酸和10mgKH-560(硅烷偶联剂与石墨烯的比例为7:100),超声均匀后在80℃下反应4h,所得改性产物充分干燥后于乙醇体系中还原,最终产物即为KH-560改性石墨烯。改性石墨烯较未改性石墨烯的亲油性增强,但相比于KH-570,其用量增加,还原效果相对较低,且由于KH-560改性石墨烯未经过负载海绵进行吸油量测定,所以其吸油效果未知。 2) Preparation of KH-560 modified graphene oxide (Lv Xiang, 2011). Disperse 100mg of graphene in 100ml of absolute ethanol, add 2ml of water, 5ml of acetic acid and 10mg of KH-560 (the ratio of silane coupling agent to graphene is 7:100), ultrasonically uniform and react at 80°C for 4h, the obtained The final product is KH-560 modified graphene after being fully dried and reduced in an ethanol system. The lipophilicity of modified graphene is stronger than that of unmodified graphene, but compared with KH-570, its dosage is increased, and the reduction effect is relatively low, and since KH-560 modified graphene has not been loaded with sponge for oil absorption measurement , so its oil-absorbing effect is unknown.
实施例三:KH-570改性石墨烯负载聚氨酯海绵后疏水亲油效果的测定 Example Three: Determination of Hydrophobic and Lipophilic Effects of KH-570 Modified Graphene Loaded Polyurethane Sponge
1)将负载有KH-570改性石墨烯的海绵均匀八等份(形状和厚度相同,约1g),取任意三份分别称重后放于水面5min,待其吸附饱和后及时移出至网架上,静置1min,称重并计算此改性海绵的吸水率;其中,作为对照组,将一块原始海绵称重后放于水面5min,及时移出至网架上,静置1min,称重并计算原始海绵的吸水率。 1) Take eight equal parts of the sponge loaded with KH-570 modified graphene (same shape and thickness, about 1g), take any three parts and weigh them respectively, put them on the water surface for 5 minutes, and remove them to the net in time after the adsorption is saturated. Stand on the rack for 1 min, weigh and calculate the water absorption rate of the modified sponge; among them, as a control group, weigh a piece of original sponge and put it on the water surface for 5 min, then remove it to the grid rack in time, let it stand for 1 min, and weigh it. And calculate the water absorption of the original sponge.
2)另取三份已称重海绵放于油面5min,待其吸附饱和后及时移至网架上,静置1min,称重并计算此改性海绵的吸油率;同时,作为对照组,将一块原始海绵直接放于油面5min,待其吸附饱和后及时移出至网架上,静置1min,称重并计算原始海绵的吸油率。 2) Take another three weighed sponges and put them on the oil surface for 5 minutes. After the adsorption is saturated, move them to the grid in time, let them stand for 1 minute, weigh and calculate the oil absorption rate of the modified sponges; at the same time, as a control group, Put a piece of original sponge directly on the oil surface for 5 minutes, remove it to the grid rack in time after its adsorption is saturated, let it stand for 1 minute, weigh and calculate the oil absorption rate of the original sponge.
3. KH-570改性石墨烯负载聚氨酯海绵后疏水亲油效果的测定结果: 3. Determination results of hydrophobic and lipophilic effect of KH-570 modified graphene loaded polyurethane sponge:
改性海绵的吸水率=(W2-W1)/W1,原始海绵的吸水率=(m2-m1)/m1; The water absorption rate of the modified sponge=(W 2 -W 1 )/W 1 , the water absorption rate of the original sponge=(m 2 -m 1 )/m 1 ;
改性海绵的吸油率=(W3-W1)/W1,原始海绵的吸油率=(m3-m1)/m1; The oil absorption rate of the modified sponge=(W 3 -W 1 )/W 1 , the oil absorption rate of the original sponge=(m 3 -m 1 )/m 1 ;
改性海绵的吸水速率=吸水率/t,改性海绵的吸油速率=吸油率/t; Water absorption rate of modified sponge = water absorption rate/t, oil absorption rate of modified sponge = oil absorption rate/t;
原始海绵的吸水速率=吸水率/t,原始海绵的吸油速率=吸油率/t; Water absorption rate of original sponge = water absorption rate/t, oil absorption rate of original sponge = oil absorption rate/t;
其中,W1=改性海绵重量(g),W2=改性海绵+吸水量(g),m1=未改性海绵重量(g),m2=未改性海绵+吸水量(g),W3=改性海绵+吸油量(g),m3=未改性海绵+吸油量(g),t为吸附时间(g)。 Among them, W 1 = modified sponge weight (g), W 2 = modified sponge + water absorption (g), m 1 = unmodified sponge weight (g), m 2 = unmodified sponge + water absorption (g ), W 3 = modified sponge + oil absorption (g), m 3 = unmodified sponge + oil absorption (g), t is adsorption time (g).
由实验测得,海绵的吸水率和吸油率如表1所示。 The water absorption and oil absorption of the sponge are shown in Table 1.
表1 制备的新型海绵材料的吸水率和吸油率 Table 1 The water absorption and oil absorption of the new sponge material prepared
可见本发明的这种改性石墨烯负载聚氨酯海绵确实是具有超疏水性和超亲油性质的材料,效果好,应用价值高。 It can be seen that the modified graphene-loaded polyurethane sponge of the present invention is indeed a material with superhydrophobicity and superoleophilic properties, with good effect and high application value. the
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CN111302467A (en) * | 2020-04-08 | 2020-06-19 | 刘水平 | Flocculant capable of recovering dye, preparation method and application thereof |
CN111302467B (en) * | 2020-04-08 | 2020-12-01 | 湖州达立智能设备制造有限公司 | Flocculant capable of recovering dye, preparation method and application thereof |
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