CN111420706B - Cu 2 O/Bi 2 O 2 CO 3 Preparation method and application of semiconductor heterojunction composite silk fibroin fibrous membrane - Google Patents
Cu 2 O/Bi 2 O 2 CO 3 Preparation method and application of semiconductor heterojunction composite silk fibroin fibrous membrane Download PDFInfo
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Abstract
本发明公开了一种Cu2O/Bi2O2CO3半导体异质结复合丝素蛋白纤维膜的制备方法及应用。本发明一方面通过简单的还原溶液化学途径合成了具有优异光催化性能的半导体异质结,另一方面通过对天然蚕丝进行脱胶、溶解、冻干处理获得所需的再生丝素蛋白海绵,并将丝素蛋白海绵按一定的配比溶解在甲酸中混和均匀制得丝素蛋白‑甲酸溶液。然后以丝素蛋白为载体将配比不同的半导体异质结粉末超声均匀分散在丝素蛋白‑甲酸溶液中制得混合纺丝液,并通过静电纺丝设备在一定的纺丝条件下制备了新型半导体材料复合丝素蛋白纳米纤维膜。本发明复合纳米膜具有优异的光催化降解氯霉素的性能,可用于有机污染的水处理。
The invention discloses a preparation method and application of Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction composite silk fibroin fiber membrane. On the one hand, the present invention synthesizes a semiconductor heterojunction with excellent photocatalytic performance through a simple reducing solution chemical approach; The silk fibroin sponge is dissolved in formic acid according to a certain proportion and mixed evenly to prepare a silk fibroin-formic acid solution. Then, using silk fibroin as a carrier, the semiconductor heterojunction powders with different ratios were ultrasonically dispersed in the silk fibroin-formic acid solution to obtain a mixed spinning solution, and the electrospinning equipment was used to prepare the spinning solution under certain spinning conditions. Novel semiconductor material composite silk fibroin nanofiber membrane. The composite nano film of the invention has excellent photocatalytic degradation performance of chloramphenicol, and can be used for water treatment of organic pollution.
Description
技术领域technical field
本发明属于复合纳米功能材料技术领域,具体涉及一种Cu2O/Bi2O2CO3半导体异质结复合丝素蛋白纤维膜的制备方法及应用。The invention belongs to the technical field of composite nano functional materials, and in particular relates to a preparation method and application of a Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction composite silk fibroin fiber membrane.
背景技术Background technique
目前水污染日益严重,传统物理法只能转移污染物而不能降解污染物,化学氧化法(如氧化剂氧化法,光催化剂催化法)可以有效地降解污染物。其中氧化剂成本贵,而光催化剂具有稳定、高效、成本低、无污染等特点。At present, water pollution is becoming more and more serious. Traditional physical methods can only transfer pollutants but cannot degrade them. Chemical oxidation methods (such as oxidant oxidation method, photocatalytic method) can effectively degrade pollutants. Among them, the oxidant is expensive, while the photocatalyst has the characteristics of stability, high efficiency, low cost, and no pollution.
氧化亚铜具有2.1eV左右的窄带隙, 是一种p型半导体材料,制备方法简单, 成本较低, 并且没有毒性, 所以在光催化领域中的前景十分广阔,然而研究表明纯氧化亚铜的光催化率都远低于理想的光催化率。碳酸氧铋带隙2.8-3.5eV之间,是一种n型半导体材料,带隙较宽使其对太阳光的实际应用受到限制,有研究表明,将其与窄带隙氧化亚铜结合制成异质结具有显著提高的光催化活性。Cuprous oxide has a narrow band gap of about 2.1eV. It is a p-type semiconductor material with simple preparation method, low cost and no toxicity, so it has a bright prospect in the field of photocatalysis. However, studies have shown that pure cuprous oxide The photocatalytic efficiency is far below the ideal photocatalytic efficiency. Bismuth oxycarbonate has a bandgap of 2.8-3.5eV. It is an n-type semiconductor material. The wide bandgap limits its practical application to sunlight. Studies have shown that it can be made by combining it with narrow bandgap cuprous oxide. The heterojunction has significantly enhanced photocatalytic activity.
丝素蛋白是一种天然的生物高聚合物,由于其可生物降解、生物相容性好、化学反应活性高、力学性能优良等特点,近年来在纤维新材料的开发中引起了人们的广泛关注,大多都应用于生物医用材料,鲜有人用于光催化方面的研究,而作为一种低廉易获取的天然高分子材料,显然它可通过一定的技术用作粉末光催化剂的优良载体。Silk fibroin is a natural biopolymer. Due to its biodegradability, good biocompatibility, high chemical reactivity, and excellent mechanical properties, it has attracted widespread attention in the development of new fiber materials in recent years. Attention, most of them are used in biomedical materials, and few people are used in photocatalytic research. As a cheap and easy-to-obtain natural polymer material, it is obvious that it can be used as an excellent carrier for powder photocatalysts through certain technologies.
静电纺丝是一种简单、方便且有效地制备纤维膜的技术。通过静电纺丝技术制备纤维材料,具有制造设备简单,工艺技术容易控制等优点,其生产出的支架具有大的表面积及超长纤维形成的宏观席状结构,能够为光催化反应提供足够的反应位点,在水污染处理应用中还具备易于分离回收的优势。Electrospinning is a simple, convenient, and effective technique for fabricating fibrous membranes. The preparation of fiber materials by electrospinning technology has the advantages of simple manufacturing equipment and easy control of process technology. The scaffold produced by it has a large surface area and a macroscopic sheet structure formed by ultra-long fibers, which can provide sufficient reaction for photocatalytic reactions. It also has the advantage of easy separation and recovery in water pollution treatment applications.
目前,半导体异质结材料已有大量报道,以氧化亚铜p型半导体与碳酸氧铋n型半导体制异质结的研究并不多,同时以丝素蛋白天然高分子材料为基底,通过静电纺丝制备出一种Cu2O/Bi2O2CO3半导体异质结复合丝素蛋白纤维膜尚未见报道,本发明通过将半导体异质结粉末超声分散在制备好的一定浓度的丝素蛋白-甲酸溶液中,克服了粉末型光催化剂易散落,不易回收再利用的特点,所制备的Cu2O/Bi2O2CO3半导体异质结复合丝素蛋白纤维膜毒性低,光催化效果好。At present, there have been a large number of reports on semiconductor heterojunction materials. There are not many studies on heterojunctions made of cuprous oxide p-type semiconductors and bismuth oxycarbonate n-type semiconductors. It has not been reported that a Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction composite silk fibroin fiber membrane is prepared by spinning. The present invention disperses the semiconductor heterojunction powder ultrasonically in the prepared silk fibroin fiber film of a certain concentration. In the protein - formic acid solution, it overcomes the characteristics that the powder photocatalyst is easy to scatter and is not easy to recycle. The effect is good.
发明内容Contents of the invention
本发明是为了填补该技术领域的空白,所提供Cu2O/Bi2O2CO3半导体异质结复合丝素蛋白纤维膜的制备方法及应用。The present invention aims to fill the gap in this technical field, and provides a preparation method and application of a Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction composite silk fibroin fiber membrane.
本发明是通过以下技术方案实现的:The present invention is achieved through the following technical solutions:
一种Cu2O/Bi2O2CO3半导体异质结复合丝素蛋白纤维膜的制备方法,包括以下步骤:A method for preparing a Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction composite silk fibroin fiber membrane, comprising the following steps:
a.剪碎的蚕茧放入煮沸的质量浓度为0.5%的碳酸钠水溶液中,浴比为1:30-1:50,沸煮30-60min后捞起,用去离子水冲洗干净,重复三次以进行脱胶处理,将所述蚕丝室温风干,拉松封装备用;a. Put the shredded silkworm cocoons into a boiled aqueous solution of sodium carbonate with a mass concentration of 0.5%, the bath ratio is 1:30-1:50, boil for 30-60min, pick up, rinse with deionized water, repeat three times To carry out degumming treatment, the silk is air-dried at room temperature, loosened and packaged for later use;
b.将步骤a得到的脱胶丝在40-60℃下溶解于9mol/L的溴化锂水溶液中,2-4小时后,放置恒温实验室静置8-12小时;b. Dissolve the degummed silk obtained in step a in 9mol/L lithium bromide aqueous solution at 40-60°C, and after 2-4 hours, place it in a constant temperature laboratory for 8-12 hours;
c.将步骤b得到的溶液注入透析袋中,用去离子水进行透析,低温下持续搅拌,每隔2-4小时换一次去离子水,透析持续2-3天;c. Inject the solution obtained in step b into a dialysis bag, perform dialysis with deionized water, keep stirring at low temperature, change the deionized water every 2-4 hours, and continue dialysis for 2-3 days;
d.将步骤c透析后的溶液离心10-20min以去除杂质,得到的丝素蛋白溶液;d. Centrifuge the dialyzed solution in step c for 10-20 minutes to remove impurities, and obtain a silk fibroin solution;
e.将步骤d得到丝素蛋白溶液经真空冷冻干燥获得丝素蛋白海绵;e. Vacuum freeze-drying the silk fibroin solution obtained in step d to obtain a silk fibroin sponge;
f.将步骤e得到的丝素蛋白海绵溶解在98%甲酸有机溶剂中混合均匀后备用;f. dissolving the silk fibroin sponge obtained in step e in 98% formic acid organic solvent and mixing uniformly for subsequent use;
g.按质量比1~5wt%制备氧化亚铜/碳酸氧铋半导体异质结,首先将一定量的十六烷基三甲基溴化铵和乙二胺四乙酸溶解在蒸馏水中,接着加入一定量制备好的碳酸氧铋混合均匀,随后向溶液中加入不同量乙酸铜持续进行磁力搅拌,在搅拌状态下逐滴滴加NaOH溶液,溶液出现蓝色悬浊物并持续搅拌30-60min,最后向溶液中缓慢滴加抗坏血酸并持续搅拌,以上步骤中先确定乙酸铜的量,按摩尔比十六烷基三甲基溴化铵:乙二胺四乙酸: 乙酸铜=2 : 3 : 5-2 : 4 : 5;乙酸铜: NaOH:抗坏血酸=1 : 5 : 10-1 : 30 : 20称取试剂,操作过程中尽量隔绝空气;将得到的样品蒸馏水洗涤数次,然后60-70℃,真空干燥6-12h得到Cu2O/Bi2O2CO3半导体异质结样品;g. Prepare cuprous oxide/bismuth oxycarbonate semiconductor heterojunction according to the mass ratio of 1-5wt%. First, dissolve a certain amount of cetyltrimethylammonium bromide and ethylenediaminetetraacetic acid in distilled water, and then add A certain amount of prepared bismuth oxycarbonate is mixed evenly, and then different amounts of copper acetate are added to the solution for continuous magnetic stirring, and NaOH solution is added drop by drop under the stirring state, the solution appears blue suspension and continues to stir for 30-60min, Finally, ascorbic acid is slowly added dropwise to the solution and continuously stirred. In the above steps, the amount of copper acetate is first determined, and the molar ratio of hexadecyltrimethylammonium bromide: ethylenediaminetetraacetic acid: copper acetate=2: 3: 5 -2 : 4 : 5; copper acetate: NaOH: ascorbic acid=1 : 5 : 10-1 : 30 : 20 Weigh the reagent, try to isolate the air during the operation; wash the obtained sample with distilled water several times, and then 60-70 ℃ , vacuum dried for 6-12h to obtain Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction samples;
h.将步骤g得到的半导体异质结粉末分散在丝素蛋白-甲酸溶液中以制备纺丝液;h. dispersing the semiconductor heterojunction powder obtained in step g in a silk fibroin-formic acid solution to prepare a spinning solution;
i.将步骤h所述纺丝液盛装在静电纺丝装置注射器中,注射器针头与高压发生器正极连接,铝箔接收器与高压接受器负极连接,进行电纺,静电纺丝出的纤维膜承接在铝箔平板接收器上;i. Put the spinning solution described in step h in the syringe of the electrospinning device, connect the needle of the syringe to the positive pole of the high-voltage generator, connect the aluminum foil receiver to the negative pole of the high-voltage receiver, and perform electrospinning, and the fiber membrane produced by electrospinning On foil flat receivers;
j.将步骤i所述纤维膜在90%甲醇中浸泡8-15分钟后用去离子水冲洗,室温风干后得不溶化Cu2O/Bi2O2CO3半导体异质结复合丝素蛋白纤维膜。j. Soak the fibrous membrane in step i in 90% methanol for 8-15 minutes, rinse it with deionized water, and air-dry it at room temperature to obtain an insoluble Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction composite silk fibroin fiber membrane.
进一步的,步骤c中,透析袋的压平宽度为44mm,截留分子量为7000。Further, in step c, the flattened width of the dialysis bag is 44 mm, and the molecular weight cut-off is 7000.
进一步的,步骤d中,离心速度为8000-12000r/min。Further, in step d, the centrifugal speed is 8000-12000r/min.
进一步的,步骤e中,真空冷冻干燥的温度为-40℃~-45℃,时间为2-3天。Further, in step e, the vacuum freeze-drying temperature is -40°C~-45°C, and the time is 2-3 days.
进一步的,步骤f中,丝素蛋白海绵溶于甲酸所制备的溶液浓度为15%。Further, in step f, the concentration of the solution prepared by dissolving the silk fibroin sponge in formic acid is 15%.
进一步的,步骤g中,碳酸氧铋加入的量为0.3-0.5g,NaOH溶液加入量为20-40mL,抗坏血酸加入量为20-40mL;制备好的Bi2O2CO3形貌为花状,纳米平均粒径约为200nm。Further, in step g, the amount of bismuth oxycarbonate added is 0.3-0.5g, the amount of NaOH solution added is 20-40mL, and the amount of ascorbic acid added is 20-40mL; the prepared Bi 2 O 2 CO 3 has a flower shape , The average nanometer particle size is about 200nm.
进一步的,步骤h中,半导体异质结粉末添加的质量浓度为5~10wt%。Further, in step h, the mass concentration of the semiconductor heterojunction powder added is 5-10 wt%.
进一步的,步骤i中,注射器喷丝头内径为0.50mm,注射器喷丝头与平板接收器表面距离为8-15 cm,施加电压为15-25kV。Further, in step i, the inner diameter of the injector spinneret is 0.50 mm, the distance between the injector spinneret and the surface of the flat receiver is 8-15 cm, and the applied voltage is 15-25 kV.
进一步的,步骤i中,注射器推进速度为0.06-0.10mm∙min-1,注射器推注水平往复移动距离为30-40 mm,保证静电纺丝得到均匀的纤维膜。Further, in step i, the advancing speed of the syringe is 0.06-0.10 mm∙min −1 , and the horizontal reciprocating movement distance of the injector injection is 30-40 mm, so as to ensure a uniform fiber membrane obtained by electrospinning.
进一步的,步骤j中制备得到的Cu2O/Bi2O2CO3半导体异质结复合丝素蛋白纤维膜在废水处理中的应用。Further, the application of the Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction composite silk fibroin fiber membrane prepared in step j in wastewater treatment.
本发明的有益效果是:The beneficial effects of the present invention are:
本发明方法制备的复合纳米膜具有优异的光催化降解氯霉素的性能,并且制备的复合纳米膜具有高表面积,为光催化反应提供了足够的位点,且易于分离回收。本发明制备的复合纳米膜可作为高效光催化膜在医药废水等方面具有广阔的应用前景。The composite nano-membrane prepared by the method of the invention has excellent photocatalytic degradation performance of chloramphenicol, and the prepared composite nano-membrane has a high surface area, provides enough sites for photocatalytic reaction, and is easy to separate and recycle. The composite nanometer membrane prepared by the invention can be used as a high-efficiency photocatalytic membrane and has broad application prospects in medical wastewater and the like.
附图说明Description of drawings
图1是本发明实施例1-3的透射电镜图及实施例2高分辨率下的透射电镜图;Fig. 1 is the transmission electron microscope figure of embodiment 1-3 of the present invention and the transmission electron microscope figure under the high resolution of embodiment 2;
图2是本发明实施例1-3制备的复合纳米纤维膜的紫外可见光谱图;Fig. 2 is the ultraviolet-visible spectrogram of the composite nanofibrous membrane prepared by the embodiment of the present invention 1-3;
图3是本发明实施例1-3制备的复合纳米纤维膜的扫描电镜图及实施例2高放大倍数下的扫描电镜图;Fig. 3 is the scanning electron micrograph of the composite nanofiber membrane prepared by the embodiment of the present invention 1-3 and the scanning electron micrograph under the high magnification of embodiment 2;
图4是本发明实施例1-3制备的复合纳米纤维膜的光催化降解氯霉素的效果图;Fig. 4 is the effect diagram of the photocatalytic degradation of chloramphenicol of the composite nanofiber membrane prepared by the embodiment of the present invention 1-3;
图5是本发明实施例1-3制备的复合纳米纤维膜对大肠杆菌及金黄色葡萄球菌的抑菌效果图。Fig. 5 is a graph showing the antibacterial effect of the composite nanofiber membrane prepared in Example 1-3 of the present invention on Escherichia coli and Staphylococcus aureus.
具体实施方式detailed description
为了使本技术领域的人员更好地理解本发明技术方案,下面结合说明书附图并通过具体实施方式来进一步说明本发明电动放射性污染去污装置及应急保障系统的技术方案。In order to enable those skilled in the art to better understand the technical solution of the present invention, the technical solution of the electric radioactive pollution decontamination device and emergency support system of the present invention will be further described below in conjunction with the accompanying drawings and specific implementation methods.
实施例1Example 1
(1)将20g剪碎的蚕茧放入1000ml煮沸的质量浓度为0.5%的碳酸钠(Na2CO3)水溶液中,沸煮30min后捞起,用大量的去离子水冲洗干净,以上步骤重复三次以进行脱胶处理,将所述蚕丝室温风干,拉松封装备用。取2g脱胶丝40℃下在9mol/L的溴化锂(LiBr)水溶液中溶解2小时,所得溶液放置恒温实验室静置10小时后注入截留分子量为7000的透析袋中,用去离子水进行透析,低温下持续搅拌,每隔2小时换一次去离子水,持续3天后将所得溶液以10000r/min的速度离心15min以去除杂质,得到的丝素蛋白溶液在-45℃条件下真空冷冻干燥3天后获得再生的丝素蛋白海绵。配制3mL质量浓度为15%的丝素蛋白-甲酸溶液(0.6459g再生的丝素蛋白海绵溶解在3mL98%浓度的甲酸中)备用;(1) Put 20g of shredded cocoons into 1000ml of boiled 0.5% sodium carbonate (Na 2 CO 3 ) aqueous solution, boil for 30 minutes, pick up, rinse with a large amount of deionized water, repeat the above steps Three times to carry out degumming treatment, the silk is air-dried at room temperature, loosened and packaged for later use. Take 2g of degummed silk and dissolve it in 9mol/L lithium bromide (LiBr) aqueous solution at 40°C for 2 hours, place the obtained solution in a constant temperature laboratory for 10 hours, inject it into a dialysis bag with a molecular weight cut-off of 7000, and perform dialysis with deionized water. Stir continuously at low temperature, change the deionized water every 2 hours, centrifuge the obtained solution at a speed of 10000r/min for 15min to remove impurities after 3 days, and vacuum freeze-dry the obtained silk fibroin solution at -45°C for 3 days Obtain a regenerated silk fibroin sponge. Prepare 3 mL of silk fibroin-formic acid solution with a mass concentration of 15% (0.6459 g of regenerated silk fibroin sponge dissolved in 3 mL of 98% formic acid) for use;
(2)按质量比1wt%制备氧化亚铜(Cu2O)/碳酸氧铋(Bi2O2CO3)(p/n)半导体异质结,称取0.022g CTAB和0.026g EDTA溶解在50mL蒸馏水中,接着加入0.4g制备好的碳酸氧铋混合均匀,随后向溶液中加入0.03g乙酸铜(Cu(Ac)2)持续进行磁力搅拌,在搅拌状态下逐滴滴加20mL NaOH(0.225mol/L)溶液,溶液出现蓝色悬浊物并持续搅拌30 min,最后向溶液中缓慢滴加20mL抗坏血酸(AA,0.15mol/L)并持续搅拌,操作过程中尽量隔绝空气。将得到的样品蒸馏水洗涤数次,然后真空70℃干燥6h得到质量比为1wt%的Cu2O/Bi2O2CO3半导体异质结样品,简称C1B;(2) Cuprous oxide (Cu 2 O)/bismuth oxycarbonate (Bi 2 O 2 CO 3 ) (p/n) semiconductor heterojunction was prepared at a mass ratio of 1 wt%, and 0.022g CTAB and 0.026g EDTA were weighed and dissolved in 50mL of distilled water, then add 0.4g of the prepared bismuth oxycarbonate and mix evenly, then add 0.03g of copper acetate (Cu(Ac) 2 ) to the solution for continuous magnetic stirring, and add 20mL of NaOH (0.225 mol/L) solution, the solution appeared blue suspension and kept stirring for 30 min, and finally slowly added 20mL ascorbic acid (AA, 0.15mol/L) dropwise to the solution and kept stirring, try to isolate the air during the operation. The obtained sample was washed several times with distilled water, and then dried in vacuum at 70°C for 6 hours to obtain a Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction sample with a mass ratio of 1 wt%, referred to as C1B;
(3)称取0.3g制得的半导体异质结粉末分散在丝素蛋白-甲酸溶液中制备纺丝液;(3) Weighing 0.3 g of the prepared semiconductor heterojunction powder and dispersing it in the silk fibroin-formic acid solution to prepare spinning solution;
(4)得到的纺丝液盛装在与静电纺丝高压装置链接的医用注射器中,注射器喷丝头内径为0.50mm,推进速度为0.07mm∙min-1,推柱水平往复移动距离为35 mm,与滚筒接收器表面距离为8 cm,调节电压为22kV,进行电纺,静电纺丝出的纤维膜承接在以铝箔为基底的平板接收器上。(4) The obtained spinning solution is contained in a medical syringe linked to the electrospinning high-voltage device. The inner diameter of the spinneret of the syringe is 0.50 mm, the propulsion speed is 0.07 mm∙min -1 , and the horizontal reciprocating movement distance of the push column is 35 mm , with a distance of 8 cm from the surface of the roller receiver, and an adjustment voltage of 22kV, for electrospinning, and the electrospun fiber membrane was carried on a flat receiver based on aluminum foil.
实施例2Example 2
保持实施例1中步骤(1)、(3)、(4)不变,步骤(2)中按质量比3wt%制备氧化亚铜(Cu2O)/碳酸氧铋(Bi2O2CO3)(p/n)半导体异质结,称取0.044g CTAB和0.053g EDTA溶解在50mL蒸馏水中,接着加入0.4g制备好的碳酸氧铋混合均匀,随后向溶液中加入0.06g乙酸铜(Cu(Ac)2)持续进行磁力搅拌,在搅拌状态下逐滴滴加20mL NaOH(0.45mol/L)溶液,溶液出现蓝色悬浊物并持续搅拌30 min,最后向溶液中缓慢滴加20mL抗坏血酸(AA,0.3mol/L)并持续搅拌,操作过程中尽量隔绝空气。将得到的样品蒸馏水洗涤数次,然后真空70℃干燥6h得到质量比为3wt%的Cu2O/Bi2O2CO3半导体异质结样品,简称C3B。Keep steps (1), (3), and (4) in Example 1 unchanged, and prepare cuprous oxide (Cu 2 O)/bismuth oxycarbonate (Bi 2 O 2 CO 3 ) (p/n) semiconductor heterojunction, weigh 0.044g CTAB and 0.053g EDTA and dissolve in 50mL distilled water, then add 0.4g prepared bismuth oxycarbonate and mix well, then add 0.06g copper acetate (Cu (Ac) 2 ) Continue magnetic stirring, dropwise add 20mL NaOH (0.45mol/L) solution under stirring state, the solution appears blue suspension and keep stirring for 30 min, finally slowly add 20mL ascorbic acid into the solution (AA, 0.3mol/L) and keep stirring, try to isolate the air during the operation. The obtained sample was washed several times with distilled water, and then dried in vacuum at 70°C for 6 hours to obtain a Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction sample with a mass ratio of 3 wt%, referred to as C3B.
实施例3Example 3
保持实施例1中步骤(1)、(3)、(4)不变,步骤(2)中按质量比5wt%制备氧化亚铜(Cu2O)/碳酸氧铋(Bi2O2CO3)(p/n)半导体异质结,称取0.058g CTAB和0.073g EDTA溶解在50mL蒸馏水中,接着加入0.4g制备好的碳酸氧铋混合均匀,随后向溶液中加入0.08g乙酸铜(Cu(Ac)2)持续进行磁力搅拌,在搅拌状态下逐滴滴加20mL NaOH(0.6mol/L)溶液,溶液出现蓝色悬浊物并持续搅拌30 min,最后向溶液中缓慢滴加20mL抗坏血酸(AA,0.4mol/L)并持续搅拌,操作过程中尽量隔绝空气。将得到的样品蒸馏水洗涤数次,然后真空70℃干燥6h得到质量比为5wt%的Cu2O/Bi2O2CO3半导体异质结样品,简称C5B。Keep steps (1), (3), and (4) in Example 1 unchanged, and prepare cuprous oxide (Cu 2 O)/bismuth oxycarbonate (Bi 2 O 2 CO 3 ) (p/n) semiconductor heterojunction, weigh 0.058g CTAB and 0.073g EDTA and dissolve in 50mL distilled water, then add 0.4g prepared bismuth oxycarbonate and mix well, then add 0.08g copper acetate (Cu (Ac) 2 ) Continue magnetic stirring, dropwise add 20mL NaOH (0.6mol/L) solution under stirring state, the solution appears blue suspension and keep stirring for 30 min, finally slowly add 20mL ascorbic acid into the solution (AA, 0.4mol/L) and keep stirring, try to isolate the air during the operation. The obtained sample was washed several times with distilled water, and then dried in vacuum at 70°C for 6 hours to obtain a Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction sample with a mass ratio of 5 wt%, referred to as C5B.
实施例4Example 4
实施例1、例2、例3制得的Cu2O/Bi2O2CO3半导体异质结复合丝素蛋白纤维膜的光催化活性实验:The photocatalytic activity experiment of the Cu2O/ Bi2O2CO3 semiconductor heterojunction composite silk fibroin fiber film that embodiment 1 , example 2 , example 3 make:
光催化活性实验在配备有420nm滤光器的300W Xe灯下进行。使用氯霉素作为目标污染物,将制备好的纳米纤维剪切成4×4cm2的正方形样品,加入到目标溶液(50mL,20 mg/L)中。黑暗状态下将溶液搅拌30min以实现有机物大分子和催化剂表面之间的吸附-解吸平衡,达到平衡后开启设备在紫外光下照射3h进行光催化降解实验,以30min为间隔取出1mL反应溶液经过0.22μm过滤器过滤储存,接着用高效液相色谱法(HPLC)对水样进行分析得上述Cu2O/Bi2O2CO3半导体异质结复合丝素蛋白纤维膜对氯霉素的光解效率。Photocatalytic activity experiments were performed under a 300 W Xe lamp equipped with a 420 nm filter. Using chloramphenicol as the target pollutant, the prepared nanofibers were cut into a 4× 4 cm square sample and added to the target solution (50 mL, 20 mg/L). Stir the solution for 30 minutes in the dark to achieve the adsorption-desorption equilibrium between the organic macromolecules and the catalyst surface. After reaching the equilibrium, turn on the equipment and irradiate with ultraviolet light for 3 hours to carry out the photocatalytic degradation experiment. Take 1 mL of the reaction solution at intervals of 30 minutes for 0.22 Filter and store with a μm filter, and then analyze the water sample by high performance liquid chromatography (HPLC) to obtain the photolysis of chloramphenicol by the Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction composite silk fibroin fiber membrane efficiency.
图1为实施例1-3的透射电镜图及实施例2高分辨率下的透射电镜图, Bi2O2CO3由众多纳米片组成1-2 μm的三维花状结构,Cu2O纳米粒子均匀分布在Bi2O2CO3纳米片的表面。Figure 1 is the TEM image of Examples 1-3 and the TEM image of Example 2 under high resolution. Bi 2 O 2 CO 3 is composed of many nanosheets with a 1-2 μm three-dimensional flower-like structure, and Cu 2 O nanometer The particles are uniformly distributed on the surface of Bi2O2CO3 nanosheets.
图2为实施例1-3制备的复合纳米纤维膜的紫外可见光谱图,相对于Bi2O2CO3而言,半导体异质结对可见光的吸收利用率由明显的提高。Fig. 2 is the ultraviolet-visible spectrum of the composite nanofiber membrane prepared in Example 1-3. Compared with Bi 2 O 2 CO 3 , the utilization rate of visible light absorption by the semiconductor heterojunction is significantly improved.
图3为实施例1-3制备的复合纳米纤维膜的扫描电镜图及实施例2高放大倍数下的扫描电镜图,Cu2O/Bi2O2CO3半导体异质结被包裹在丝素蛋白纤维中,因此赋予了复合膜光催化活性。Figure 3 is the scanning electron micrograph of the composite nanofiber membrane prepared in Example 1-3 and the scanning electron micrograph at high magnification in Example 2, the Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction is wrapped in silk fibroin protein fibers, thus endowing the composite membrane with photocatalytic activity.
图4为实施例1-3制备的复合纳米纤维膜的光催化降解氯霉素的效果图。相对于纯丝素蛋白膜而言,加入Cu2O/Bi2O2CO3半导体异质结能显著增强膜的光催化活性,其中掺入C3B异质结的膜显示出最高的光催化降解氯霉素的能力,可见光照射30min时该复合膜对氯霉素的降解率达到98.33%。Fig. 4 is an effect diagram of the photocatalytic degradation of chloramphenicol by the composite nanofiber membrane prepared in Example 1-3. Compared with the pure silk fibroin film, the photocatalytic activity of the film was significantly enhanced by adding Cu 2 O/Bi 2 O 2 CO 3 semiconductor heterojunction, and the film incorporating the C3B heterojunction showed the highest photocatalytic degradation The ability of chloramphenicol, the degradation rate of the composite film to chloramphenicol reached 98.33% when visible light was irradiated for 30 minutes.
图5为实施例1-3制备的复合纳米纤维膜对大肠杆菌及金黄色葡萄球菌的抑菌效果图,所制备的复合膜有较好的抗菌活性,且抑菌率随Cu2O量的增加而提高。Fig. 5 is the antibacterial effect diagram of the composite nanofibrous membrane prepared in Example 1-3 to Escherichia coli and Staphylococcus aureus, the prepared composite membrane has better antibacterial activity, and the antibacterial rate varies with the Cu2O increase and increase.
申请人声明,以上所述仅为本发明的具体实施方式,但本发明的保护范围并不局限于此,所属技术领域的技术人员应该明了,任何属于本技术领域的技术人员在本发明揭露的技术范围内,可轻易想到的变化或替换,均落在本发明的保护范围和公开范围之内。The applicant declares that the above description is only a specific embodiment of the present invention, but the scope of protection of the present invention is not limited thereto, and those skilled in the art should understand that any person skilled in the art should be aware of any disclosure in the present invention Within the technical scope, easily conceivable changes or substitutions all fall within the scope of protection and disclosure of the present invention.
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Publication number | Priority date | Publication date | Assignee | Title |
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CN110453378A (en) * | 2019-07-03 | 2019-11-15 | 上海大学 | A kind of sulfonic acid group quantum dot/silk fibroin composite nanofiber membrane and its preparation method and application |
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CN110453378A (en) * | 2019-07-03 | 2019-11-15 | 上海大学 | A kind of sulfonic acid group quantum dot/silk fibroin composite nanofiber membrane and its preparation method and application |
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---|
Cu2O NPs/Bi2O2CO3 flower-like complex photocatalysts with enhanced visible light photocatalytic degradation of organic pollutants;Shuanglong Lin等;《Catalysis Today》;20171115;第297卷;第237-245页 * |
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