CN107597194A - A kind of preparation method of new ZnO/ fungies fiber optic catalytic composite material - Google Patents
A kind of preparation method of new ZnO/ fungies fiber optic catalytic composite material Download PDFInfo
- Publication number
- CN107597194A CN107597194A CN201710893775.XA CN201710893775A CN107597194A CN 107597194 A CN107597194 A CN 107597194A CN 201710893775 A CN201710893775 A CN 201710893775A CN 107597194 A CN107597194 A CN 107597194A
- Authority
- CN
- China
- Prior art keywords
- fungal
- fiber
- preparation
- zno
- composite material
- 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.)
- Pending
Links
Landscapes
- Catalysts (AREA)
- Chemical Or Physical Treatment Of Fibers (AREA)
Abstract
一种新型ZnO/真菌纤维光催化复合材料的制备方法,它涉及一种对有机染料进行光降解的新型真菌纤维复合材料的制备方法。本发明方法以醋酸锌、六亚甲基四胺和真菌纤维为反应物,采用溶剂热合成法制备了新型ZnO/真菌纤维复合纤维材料。在乙醇处理的真菌纤维中加入醋酸锌和六亚甲基四胺,经过超声,溶剂热合成和冷冻干燥,得ZnO/真菌纤维复合纤维材料。真菌纤维的表面附了一层球形ZnO纳米颗粒,粒径尺寸约为600nm,真菌纤维起到很好的模板作用。真菌纤维表面ZnO颗粒的生成,提高其热稳定性。采用5mg/L的罗丹明B溶液进行光催化实验,ZnO/真菌纤维复合纤维材料对罗丹明B染料的光催化降解效果能够达到92.28%。The invention discloses a preparation method of a novel ZnO/fungus fiber photocatalytic composite material, which relates to a preparation method of a novel fungus fiber composite material which photodegrades an organic dye. The method of the invention uses zinc acetate, hexamethylenetetramine and fungal fiber as reactants, and adopts a solvothermal synthesis method to prepare a novel ZnO/fungal fiber composite fiber material. Zinc acetate and hexamethylenetetramine were added to ethanol-treated fungal fibers, and ZnO/fungus fiber composite fiber materials were obtained through ultrasonication, solvothermal synthesis and freeze-drying. A layer of spherical ZnO nanoparticles with a particle size of about 600nm is attached to the surface of the fungal fiber, and the fungal fiber acts as a good template. Generation of ZnO particles on the surface of fungal fibers to improve their thermal stability. Using 5mg/L Rhodamine B solution for photocatalytic experiments, the photocatalytic degradation effect of ZnO/fungal fiber composite fiber material on Rhodamine B dye can reach 92.28%.
Description
技术领域technical field
本发明涉及一种新型ZnO/真菌纤维光催化复合材料的制备方法。The invention relates to a preparation method of a novel ZnO/fungus fiber photocatalytic composite material.
背景技术Background technique
随着人民生活水平提高,越来越多的染料广泛地用在印染、造纸、纺织等行业。行业的快速发展,提高经济效益的同时,染料废水排放给环境带来了严重的危害。染料废水色度大、成分复杂、有毒、化学稳定性高,具有致癌、致畸、致突变等特点。目前处理染料废水的主要方法大致分为化学法、物理法、生物法和吸附法。物理法和化学法操作成本较高,过程复杂,在处理过程中容易产生一些有害气体,这些气体排放到空气中产生二次危害。生物法主要利用细菌,真菌等对染料进行脱色降解,相对来说对染料的种类、温度和pH等有一定的要求,限制应用范围。吸附法操作简单,适应性强,不需要投入大量的人力物力,被普遍认为是快速净化染料废水的一种方式。采用吸附法的重点是找到合适的吸附剂,良好的吸附剂一般要求有较大的比表面积、适宜的孔结构、较好的吸附能力、吸附过程中性质稳定、原料来源广泛、制备方便、有良好的机械强度、可以循环利用等。在环境压力日益增大的今天,采用环保可降解的吸附材料就显得尤为重要。目前,半导体无机纳米材料在高分子材料制备中也得到广泛的应用,其对高分子材料能够起到功能改性和力学性能改性的作用。半导体光催化剂能够在光照射作用下发生氧化还原反应,经有机污染物降解为水、二氧化碳、盐和酸等小分子的物质,从而减少对环境的污染。With the improvement of people's living standards, more and more dyes are widely used in printing and dyeing, papermaking, textile and other industries. With the rapid development of the industry and the improvement of economic benefits, the discharge of dye wastewater has brought serious harm to the environment. Dye wastewater has the characteristics of large chroma, complex composition, toxicity, high chemical stability, carcinogenicity, teratogenicity and mutagenicity. At present, the main methods of treating dye wastewater are roughly divided into chemical methods, physical methods, biological methods and adsorption methods. Physical and chemical methods have high operating costs and complicated processes, and some harmful gases are likely to be generated during the treatment process, and these gases are discharged into the air to cause secondary hazards. Biological methods mainly use bacteria and fungi to decolorize and degrade dyes. Relatively speaking, there are certain requirements for the type, temperature and pH of dyes, which limits the scope of application. The adsorption method is simple to operate, has strong adaptability, and does not require a lot of manpower and material resources. It is generally regarded as a way to quickly purify dye wastewater. The focus of the adsorption method is to find a suitable adsorbent. A good adsorbent generally requires a large specific surface area, a suitable pore structure, a good adsorption capacity, stable properties during the adsorption process, a wide range of raw material sources, convenient preparation, and effective adsorption. Good mechanical strength, can be recycled, etc. Today, with increasing environmental pressure, it is particularly important to use environmentally friendly and degradable adsorbent materials. At present, semiconductor inorganic nanomaterials are also widely used in the preparation of polymer materials, which can play a role in functional modification and mechanical property modification of polymer materials. Semiconductor photocatalysts can undergo oxidation-reduction reactions under light irradiation, and degrade organic pollutants into small molecules such as water, carbon dioxide, salts, and acids, thereby reducing environmental pollution.
植物纤维素及细菌纤维素作为生物模板剂已得到广泛的应用研究。研究发现,真菌在生物培养过程中能产生类似细菌纤维素的三维网络纤维结构,且表面含有大量反应活性基团的纤维物质,将其称之为真菌纤维。真菌纤维具有与细菌纤维素相似的三维网络结构以及多羟基基团活性位点,可与多种类半导体纳米微粒进行复合掺杂,使其固定在微纤维的各个反应位点上,避免相互之间的碰撞以及团聚,解决了纳米材料的稳定性问题,使纳米效应得到保障。开发出具有高光催化效率的半导体粒子及其复合材料以及负载型有机-无机复合光催化材料,对于半导体光催化剂在工业上的规模化应用,具有重要理论意义和实践价值。本实验以真菌纤维、醋酸锌以及硫脲为原料,通过溶剂热合成法制备了具有光催化作用的染料吸附降解新型材料。本实验具有操作简单、产品易得、可生物降解、成本低、对环境适应能力强等优点。Plant cellulose and bacterial cellulose have been widely used as biological templates. Studies have found that fungi can produce a three-dimensional network fiber structure similar to bacterial cellulose in the process of biological culture, and the fiber material with a large number of reactive groups on the surface is called fungal fiber. Fungal fibers have a three-dimensional network structure similar to bacterial cellulose and active sites of polyhydroxyl groups, and can be compounded and doped with various types of semiconductor nanoparticles to fix them on each reaction site of the microfibers and avoid interaction with each other. The collision and agglomeration of nano-materials solve the stability problem of nano-materials and ensure the nano-effects. The development of semiconductor particles with high photocatalytic efficiency and their composite materials, as well as supported organic-inorganic composite photocatalytic materials, has important theoretical significance and practical value for the large-scale application of semiconductor photocatalysts in industry. In this experiment, fungal fiber, zinc acetate and thiourea were used as raw materials to prepare a new material with photocatalytic dye adsorption and degradation by solvothermal synthesis. This experiment has the advantages of simple operation, easy-to-obtain product, biodegradable, low cost, and strong adaptability to the environment.
发明内容Contents of the invention
本发明提供一种新型ZnO/真菌纤维光催化复合材料的制备方法,以解决目前印染废水排放严重、生产成本高、产品难降解等问题。The invention provides a preparation method of a novel ZnO/fungus fiber photocatalytic composite material to solve the current problems of serious discharge of printing and dyeing wastewater, high production cost, difficult degradation of products and the like.
本发明一种新型ZnO/真菌纤维光催化复合材料的制备方法,具体按下述步骤进行:一、真菌菌丝体,用0.1%~2%稀碱液煮沸10~30min,过滤,得到真菌纤维,用去离子水洗涤至中性,冷冻干燥备用。二、配置一系列梯度浓度为40%~99%的乙醇溶液浸泡处理经过去离子水溶胀的真菌纤维,然后对真菌纤维进行离心分离,离心速度为5000~10000rpm。三、离心分离的真菌纤维加入到以醋酸锌溶液(真菌纤维与醋酸锌的用量比为1:0.1~1:3)为锌源及以硫脲(硫脲乙醇溶液的摩尔比为1:2~1:10)作为沉淀剂的乙醇混合溶液中,室温下进行磁力分散;四、将混合物移入到含有聚四氟乙烯内衬的不锈钢反应釜中,在80~200℃温度下保温反应6~10h;五、反应结束后,温度降至室温,将混合溶液进行离心分离(6000~10000rpm),经无水乙醇、去离子水反复洗涤和冷冻干燥等步骤得到具有光催化降解作用的新型ZnO/真菌纤维复合材料。A kind of preparation method of novel ZnO/fungal fiber photocatalytic composite material of the present invention, specifically carry out according to the following steps: 1, fungal mycelia, boil 10-30min with 0.1%~2% dilute lye, filter, obtain fungal fiber , washed with deionized water until neutral, freeze-dried for later use. 2. Prepare a series of ethanol solutions with a gradient concentration of 40% to 99% to soak the fungal fibers swollen with deionized water, and then perform centrifugal separation on the fungal fibers at a centrifugal speed of 5000 to 10000 rpm. 3. Add the centrifuged fungal fiber to zinc acetate solution (the ratio of fungal fiber to zinc acetate is 1:0.1~1:3) as the zinc source and thiourea (the molar ratio of thiourea-ethanol solution is 1:2) ~1:10) in ethanol mixed solution as precipitating agent, carry out magnetic dispersion at room temperature; 4. Move the mixture into a stainless steel reaction kettle with polytetrafluoroethylene lining, and keep it warm at 80~200°C for 6~ 10h; 5. After the reaction, the temperature was lowered to room temperature, and the mixed solution was centrifuged (6000-10000rpm), and the new ZnO/ Fungal fiber composites.
本发明制备的真菌纤维表面附着了一层球形的ZnO纳米颗粒,粒子尺寸约600nm分布均匀,真菌起到良好的模板作用;真菌纤维表面的活性基团与ZnO纳米粒子之间存在着相互作用,有利于提高ZnO粒子在真菌纤维表面的稳定性。在5mg/L的罗丹明B溶液中光催化降解效率能够达到92.28%。本发明的制备技术工艺简单、易于操作、环保无污染、可生物降解,生产过程绿色环保符合可持续绿色发展的理念。A layer of spherical ZnO nanoparticles is attached to the surface of the fungal fiber prepared by the present invention, the particle size is about 600nm, and the distribution is uniform, and the fungus plays a good template role; there is an interaction between the active groups on the surface of the fungal fiber and the ZnO nanoparticles, It is beneficial to improve the stability of ZnO particles on the surface of fungal fibers. The photocatalytic degradation efficiency can reach 92.28% in 5mg/L rhodamine B solution. The preparation technology of the invention is simple, easy to operate, environmentally friendly, pollution-free, and biodegradable, and the production process is environmentally friendly and conforms to the concept of sustainable green development.
具体实施方式detailed description
实施例1:Example 1:
本发明一种光催化作用的ZnO/真菌纤维新型复合材料的制备方法,具体按下述步骤进行:将2.0g真菌菌丝体,用0.1%~2%稀碱液煮沸10~30min,过滤,得到真菌纤维,用去离子水洗涤至中性,冷冻干燥备用;配置一系列梯度浓度为40%~99%的乙醇溶液浸泡处理经过去离子水溶胀的真菌纤维,然后对真菌纤维进行离心分离,离心速度为5000~10000rpm;离心分离的真菌纤维加入到以醋酸锌溶液作为锌源(真菌纤维与醋酸锌的用量比为1:0.1~1:3)及以硫脲作为沉淀剂的乙醇混合溶液中,室温下进行磁力分散;将混合物移入到含有聚四氟乙烯内衬的不锈钢反应釜中,在80~200℃温度下保温反应6~10h;反应结束后,温度降至室温,将混合溶液进行离心分离(6000~10000rpm),用无水乙醇和去离子水反复洗涤,经冷冻干燥后得到具有光催化降解作用的新型复合纤维材料。A kind of preparation method of the ZnO/fungal fiber novel composite material of photocatalysis of the present invention, specifically carry out according to the following steps: with 0.1%~2% dilute lye, boil 10~30min with 2.0g fungal mycelium, filter, The fungal fibers were obtained, washed with deionized water until neutral, and freeze-dried for later use; a series of ethanol solutions with a gradient concentration of 40% to 99% were prepared to soak the fungal fibers swollen by deionized water, and then the fungal fibers were centrifuged. The centrifugal speed is 5000~10000rpm; the centrifugally separated fungal fiber is added to the ethanol mixed solution with zinc acetate solution as zinc source (the dosage ratio of fungal fiber and zinc acetate is 1:0.1~1:3) and thiourea as precipitant , carry out magnetic dispersion at room temperature; move the mixture into a stainless steel reactor with polytetrafluoroethylene lining, and keep it warm at 80-200°C for 6-10 hours; after the reaction, cool down to room temperature, and mix the solution Perform centrifugal separation (6000-10000rpm), repeatedly wash with absolute ethanol and deionized water, and freeze-dry to obtain a novel composite fiber material with photocatalytic degradation.
实施例2Example 2
将2.0g真菌菌丝体,用5%稀碱液煮沸30min,过滤,得到真菌纤维,用去离子水洗涤至中性,冷冻干燥备用;配置一系列浓度梯度为40%~99%的乙醇溶液浸泡处理经过去离子水溶胀的真菌纤维,然后对真菌纤维进行离心分离,离心速度为8000rpm;离心分离的真菌纤维加入到以醋酸锌溶液作为锌源(真菌纤维与醋酸锌用量比为1:0.1~1:3)及以硫脲作为沉淀剂的乙醇混合溶液中,室温下进行磁力分散;将混合物移入到烧瓶中,在95℃温度下保温反应6h;反应结束后,温度降至室温,将混合溶液进行离心分离(6000~10000rpm),用无水乙醇和去离子水反复洗涤,经冷冻干燥后得到具有光催化降解作用的新型复合纤维材料。实验结果,真菌纤维表面并没有成型的ZnO生成,且表面的附着较少。在5mg/L的罗丹明B溶液中的光催化降解效果较差。Boil 2.0 g of fungal mycelium with 5% dilute lye for 30 minutes, filter to obtain fungal fibers, wash with deionized water until neutral, and freeze-dry for later use; prepare a series of ethanol solutions with a concentration gradient of 40% to 99% Soak the fungal fibers swollen with deionized water, then centrifuge the fungal fibers at a centrifugal speed of 8000rpm; add the fungal fibers to zinc acetate solution as the zinc source (the ratio of fungal fiber to zinc acetate is 1:0.1) ~1:3) and ethanol mixed solution with thiourea as precipitating agent, carry out magnetic dispersion at room temperature; move the mixture into a flask, and keep it at 95°C for 6h; after the reaction, the temperature is lowered to room temperature, and The mixed solution is subjected to centrifugation (6000-10000rpm), washed repeatedly with absolute ethanol and deionized water, and freeze-dried to obtain a novel composite fiber material with photocatalytic degradation. The experimental results showed that there was no formed ZnO on the surface of the fungal fiber, and the adhesion on the surface was less. The photocatalytic degradation effect in 5mg/L rhodamine B solution is poor.
实施例3Example 3
将2g真菌菌丝体,用0.5%稀碱液煮沸20min,过滤,得到真菌纤维,用去离子水洗涤至中性,冷冻干燥备用;配置一系列浓度梯度为40%~99%的乙醇溶液浸泡处理经过去离子水溶胀的真菌纤维,然后对真菌纤维进行离心分离,离心速度为5000rpm;取0.5g ZnO纳米粒子分散在去离子水中,进行超声分散30min;取0.1g真菌纤维,将ZnO悬浮液进行喷涂到纤维素的表面,得到具有光催化降解作用的新型复合纤维材料。此方法制备的材料,在真菌纤维的表面残留较少,并容易脱落。Boil 2 g of fungal mycelium with 0.5% dilute lye for 20 minutes, filter to obtain fungal fibers, wash with deionized water until neutral, and freeze-dry for later use; prepare a series of ethanol solutions with a concentration gradient of 40% to 99% for soaking Treat the fungal fibers swollen with deionized water, and then centrifuge the fungal fibers at a centrifugal speed of 5000rpm; take 0.5g of ZnO nanoparticles and disperse them in deionized water, and perform ultrasonic dispersion for 30min; take 0.1g of fungal fibers, and dissolve the ZnO suspension It is sprayed onto the surface of cellulose to obtain a novel composite fiber material with photocatalytic degradation. The material prepared by this method has less residue on the surface of the fungal fiber and is easy to fall off.
实施例4Example 4
将2g真菌菌丝体,用0.5%稀碱液煮沸30min,过滤,得到真菌纤维,用去离子水洗涤至中性,冷冻干燥备用;配置一系列浓度梯度为40%~99%的乙醇溶液浸泡处理经过去离子水溶胀的真菌纤维,然后对真菌纤维进行离心分离,离心速度为6000rpm;离心分离的真菌纤维加入到以硝酸锌溶液作为锌源(真菌纤维与醋酸锌用量比为1:0.1)及以氨水作为沉淀剂的乙醇混合溶液中,室温下进行磁力分散;将混合物移入到含有聚四氟乙烯内衬的不锈钢反应釜中,在150℃温度下保温反应4h;反应结束后,温度降至室温,将混合溶液进行离心分离(7000rpm),用无水乙醇和去离子水反复洗涤,经冷冻干燥后得到具有光催化降解作用的新型复合纤维材料。实验表明,真菌纤维的光滑表面依稀形成一些不规则的扁球形粒子,均匀性较差,没有成核生长成球形粒子。在5mg/L的罗丹明B溶液中的光催化降解效果仅61.13%。Boil 2 g of fungal mycelium with 0.5% dilute lye for 30 minutes, filter to obtain fungal fibers, wash with deionized water until neutral, and freeze-dry for later use; prepare a series of ethanol solutions with a concentration gradient of 40% to 99% for soaking Treat the fungal fibers swollen with deionized water, then centrifuge the fungal fibers at a centrifugal speed of 6000rpm; add the fungal fibers to the zinc nitrate solution as the zinc source (the ratio of fungal fiber to zinc acetate is 1:0.1) and ethanol mixed solution with ammonia water as precipitant, magnetically dispersed at room temperature; the mixture was moved into a stainless steel reaction kettle with polytetrafluoroethylene lining, and kept at 150°C for 4 hours; after the reaction, the temperature dropped After reaching room temperature, the mixed solution was centrifuged (7000 rpm), washed repeatedly with absolute ethanol and deionized water, and freeze-dried to obtain a novel composite fiber material with photocatalytic degradation. Experiments showed that the smooth surface of fungal fibers vaguely formed some irregular oblate particles with poor uniformity and no nucleation and growth into spherical particles. The photocatalytic degradation effect in 5mg/L Rhodamine B solution is only 61.13%.
实施例5Example 5
将2g真菌菌丝体,用0.5%稀碱液煮沸30min,过滤,得到真菌纤维,用去离子水洗涤至中性,冷冻干燥备用;配置一系列梯度浓度为40%-99%的乙醇溶液浸泡处理经过去离子水溶胀的真菌纤维,然后对真菌纤维进行离心分离,离心速度为5000rpm;离心分离的真菌纤维加入到以硝酸锌溶液作为锌源(真菌纤维与醋酸锌用量比为1:1.5)及以氨水作为沉淀剂的乙醇混合溶液中,用1mol/L氢氧化钠溶液进行pH调节,室温下进行磁力分散;将混合物移入到含有聚四氟乙烯内衬的不锈钢反应釜中,在100℃温度下保温反应10h;反应结束后,温度降至室温,将混合溶液进行离心分离(6000rpm),用无水乙醇和去离子水反复洗涤,经冷冻干燥后得到具有光催化降解作用的新型复合纤维材料。实验表明,真菌纤维的光滑表面形成球形ZnO纳米颗粒,粒子尺寸分布均匀。在5mg/L的罗丹明B溶液中的光催化降解效果达到69.48%。Boil 2 g of fungal mycelium with 0.5% dilute lye for 30 minutes, filter to obtain fungal fibers, wash with deionized water until neutral, and freeze-dry for later use; prepare a series of ethanol solutions with a gradient concentration of 40%-99% for soaking Treat the fungal fibers swollen with deionized water, then centrifuge the fungal fibers at a centrifugal speed of 5000rpm; add the fungal fibers to the zinc nitrate solution as the zinc source (the ratio of fungal fiber to zinc acetate is 1:1.5) And in the ethanol mixed solution with ammonia water as the precipitating agent, adjust the pH with 1mol/L sodium hydroxide solution, and carry out magnetic dispersion at room temperature; move the mixture into a stainless steel reaction kettle with a polytetrafluoroethylene liner, at 100 ° C Keep the reaction at high temperature for 10 hours; after the reaction, the temperature is lowered to room temperature, and the mixed solution is centrifuged (6000rpm), washed repeatedly with absolute ethanol and deionized water, and freeze-dried to obtain a new type of composite fiber with photocatalytic degradation Material. Experiments showed that the smooth surface of fungal fibers formed spherical ZnO nanoparticles with uniform particle size distribution. The photocatalytic degradation effect in 5mg/L rhodamine B solution reached 69.48%.
实施例6Example 6
将2g的真菌菌丝体,用0.5%稀碱液煮沸30min,过滤,得到真菌纤维,用去离子水洗涤至中性,冷冻干燥备用;配置一系列浓度的乙醇溶液浸泡在经过去离子水溶胀的真菌纤维,对真菌纤维进行离心分离,离心速度为8000rpm;将真菌纤维与醋酸锌用量比为1:2的真菌纤维加入到醋酸锌溶液,用硫脲作为沉淀剂的乙醇混合溶液中,在室温下进行机械搅拌;将混合物移入到反应釜中,在120℃保温反应8h;反应结束后,进行离心处理,然后用无水乙醇和去离子水反复洗涤,经冷冻干燥后得到具有光催化降解作用的新型复合纤维材料。实验表明,真菌纤维的光滑表面形成球形ZnO纳米颗粒,粒子尺寸约为600nm且分布均匀,真菌起到了很好的模板作用。在5mg/L的罗丹明B溶液中的光催化降解效果达到73.47%。Boil 2 g of fungal mycelium with 0.5% dilute lye for 30 minutes, filter to obtain fungal fibers, wash with deionized water until neutral, and freeze-dry for later use; configure a series of ethanol solutions to soak in deionized water fungal fiber, the fungal fiber is centrifuged, and the centrifugal speed is 8000rpm; the fungal fiber and the fungal fiber with a zinc acetate dosage ratio of 1:2 are added to the zinc acetate solution, and thiourea is used as the ethanol mixed solution of the precipitating agent. Mechanical stirring was carried out at room temperature; the mixture was moved into the reaction kettle, and kept at 120°C for 8 hours; after the reaction, it was centrifuged, and then washed repeatedly with absolute ethanol and deionized water, and after freeze-drying, a photocatalytic degradation product was obtained. A new type of composite fiber material. Experiments show that spherical ZnO nanoparticles are formed on the smooth surface of the fungal fiber, the particle size is about 600nm and the distribution is uniform, and the fungus plays a good role as a template. The photocatalytic degradation effect in 5mg/L rhodamine B solution reached 73.47%.
Claims (8)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710893775.XA CN107597194A (en) | 2017-09-28 | 2017-09-28 | A kind of preparation method of new ZnO/ fungies fiber optic catalytic composite material |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710893775.XA CN107597194A (en) | 2017-09-28 | 2017-09-28 | A kind of preparation method of new ZnO/ fungies fiber optic catalytic composite material |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107597194A true CN107597194A (en) | 2018-01-19 |
Family
ID=61059067
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710893775.XA Pending CN107597194A (en) | 2017-09-28 | 2017-09-28 | A kind of preparation method of new ZnO/ fungies fiber optic catalytic composite material |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107597194A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108675460A (en) * | 2018-03-30 | 2018-10-19 | 中南大学 | A kind of ZIF-8/ mycelia composite material and preparation method and application |
CN113000031A (en) * | 2021-03-31 | 2021-06-22 | 陕西科技大学 | Zinc oxide/collagen fiber composite porous adsorption material and preparation method and application thereof |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102212806A (en) * | 2010-04-07 | 2011-10-12 | 南京理工大学 | Preparation method of bacterial cellulose-nano silver composite material |
CN102600905A (en) * | 2012-02-20 | 2012-07-25 | 合肥工业大学 | Semiconductor hetero-junction/conductive polymer fiber membrane composite photocatalyst and preparation method thereof |
CN104874298A (en) * | 2015-05-25 | 2015-09-02 | 天津理工大学 | Method for preparing nanometer ZnS/cellulose complex film with photocatalytic activity |
CN106012071A (en) * | 2016-06-24 | 2016-10-12 | 东华大学 | Preparation method of continuous cellulose/TiO2 airgel fiber with photocatalytic performance |
CN106955718A (en) * | 2017-02-27 | 2017-07-18 | 江苏大学 | A kind of ZnS/Bi2O3Hetero-junctions molecular engram photocatalysis membrana and preparation method and purposes |
-
2017
- 2017-09-28 CN CN201710893775.XA patent/CN107597194A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102212806A (en) * | 2010-04-07 | 2011-10-12 | 南京理工大学 | Preparation method of bacterial cellulose-nano silver composite material |
CN102600905A (en) * | 2012-02-20 | 2012-07-25 | 合肥工业大学 | Semiconductor hetero-junction/conductive polymer fiber membrane composite photocatalyst and preparation method thereof |
CN104874298A (en) * | 2015-05-25 | 2015-09-02 | 天津理工大学 | Method for preparing nanometer ZnS/cellulose complex film with photocatalytic activity |
CN106012071A (en) * | 2016-06-24 | 2016-10-12 | 东华大学 | Preparation method of continuous cellulose/TiO2 airgel fiber with photocatalytic performance |
CN106955718A (en) * | 2017-02-27 | 2017-07-18 | 江苏大学 | A kind of ZnS/Bi2O3Hetero-junctions molecular engram photocatalysis membrana and preparation method and purposes |
Non-Patent Citations (2)
Title |
---|
朱高升,等: "真菌纤维_硫化镉复合纤维材料及其光催化性能研究", 《功能材料》 * |
李鑫,等: "溶剂热制备球状ZnS纳米光催化剂及其光催化性能", 《有色金属科学与工程》 * |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108675460A (en) * | 2018-03-30 | 2018-10-19 | 中南大学 | A kind of ZIF-8/ mycelia composite material and preparation method and application |
CN113000031A (en) * | 2021-03-31 | 2021-06-22 | 陕西科技大学 | Zinc oxide/collagen fiber composite porous adsorption material and preparation method and application thereof |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN1171904C (en) | A kind of nano microcrystalline cellulose and preparation method thereof | |
CN110918126B (en) | A kind of preparation method of flower-shaped molybdenum disulfide combined with UiO-66 photocatalyst | |
CN103769167B (en) | A method for preparing graphene-wrapped cadmium sulfide core-shell structure photocatalytic material | |
CN104624243B (en) | Preparation method of nanometer titanium dioxide/loofah sponge composite photocatalyst | |
CN102795661B (en) | A kind of preparation method of graded flower-shaped ZnIn2S4 ternary compound | |
CN105344328B (en) | A kind of preparation method of cotton fiber carried titanium dioxide composite material film | |
CN111777772B (en) | A method for microbial mineralization and enhanced hydrogel | |
CN106492847A (en) | It is loaded with cellulose nanometer fibril aeroge of photochemical catalyst and preparation method thereof | |
CN102583636B (en) | Mixed nanometer cobalt titanium dioxide/chitosan compound microsphere photodissociation organophosphorus pesticide wastewater | |
CN107185577A (en) | Preparation method with visible light-responded heterogeneous Fenton zinc ferrite photocatalysis composite | |
CN107597194A (en) | A kind of preparation method of new ZnO/ fungies fiber optic catalytic composite material | |
CN105540827B (en) | A kind of preparation method of the graduation titanium dioxide microballoon sphere filler based on surface orientation growing nano-rod | |
CN109201029B (en) | A kind of preparation method of efficient porous composite photocatalytic material | |
CN113275002B (en) | A kind of C/MoO2 porous photocatalyst and preparation method and application thereof | |
CN110586057B (en) | Hybrid modified TiO2 composite photocatalyst, its preparation and use | |
CN112718000A (en) | Organic-inorganic composite photocatalytic film and preparation method and application thereof | |
CN113234220B (en) | Flower-shaped structure Fe for photodegradation of ciprofloxacin 3 O 4 /Bi 2 WO 6 Process for preparing catalyst | |
CN116422380A (en) | Photocatalyst for sewage treatment and preparation method and application thereof | |
CN111450895A (en) | Alkali metal-containing honeycomb covalent triazine framework material and preparation method and application thereof | |
CN117285734B (en) | Environmentally friendly degradable plastic and preparation method thereof | |
CN110624496A (en) | A preparation method of porous boron nitride-based composite material for organic wastewater purification | |
CN111013569B (en) | Flower-like bismuth silicate/bismuth molybdate heterojunction photocatalyst and preparation method and application thereof | |
CN103537308A (en) | Preparation method of tetrahydroxy copper phosphate catalyst | |
CN118546454B (en) | Preparation and application of nanoparticle modified polyethylene plastic | |
CN108084481A (en) | A kind of high water conservation polyacrylamide water-absorbing resin 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 | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20180119 |