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CN104874298A - Method for preparing nanometer ZnS/cellulose complex film with photocatalytic activity - Google Patents

Method for preparing nanometer ZnS/cellulose complex film with photocatalytic activity Download PDF

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CN104874298A
CN104874298A CN201510268048.5A CN201510268048A CN104874298A CN 104874298 A CN104874298 A CN 104874298A CN 201510268048 A CN201510268048 A CN 201510268048A CN 104874298 A CN104874298 A CN 104874298A
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余群燕
李文江
蒋一正
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Tianjin University of Technology
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Abstract

本发明公开了一种制备具有光催化活性的纳米ZnS/纤维素复合膜的方法,先采用NMMO工艺制备出纯棉浆纤维素膜,然后采用液体浸渍法制备纳米ZnS/纤维素复合膜,利用来源丰富、安全无毒及成本低廉的可再生资源作为原材料,制备纤维素基复合材料;工艺流程简单、制备过程绿色环保、无污染,所得到的纳米ZnS/纤维素复合膜具有良好的紫外吸收光催化降解水体污染物性能;同时保留纯纤维素膜的特性,如良好的耐化学稳定性及热稳定性等;还具有良好的光电和光催化性能,广泛应用于光电器件、发光材料、污水处理材料及生物医用材料等。

The invention discloses a method for preparing a nano-ZnS/cellulose composite membrane with photocatalytic activity. Firstly, a pure cotton pulp cellulose membrane is prepared by using an NMMO process, and then a nano-ZnS/cellulose composite membrane is prepared by a liquid impregnation method. Abundant, safe, non-toxic and low-cost renewable resources are used as raw materials to prepare cellulose-based composite materials; the process is simple, the preparation process is green and pollution-free, and the obtained nano-ZnS/cellulose composite film has good UV absorption Photocatalytic degradation of water pollutants; while retaining the characteristics of pure cellulose film, such as good chemical resistance and thermal stability; also has good photoelectric and photocatalytic properties, widely used in optoelectronic devices, luminescent materials, sewage treatment materials and biomedical materials.

Description

一种制备具有光催化活性的纳米ZnS/纤维素复合膜的方法A method for preparing nano-ZnS/cellulose composite film with photocatalytic activity

技术领域technical field

本发明涉及无机纳米半导体ZnS颗粒与天然有机高分子纤维素膜相结合,制备出具有光催化功能的纳米ZnS/纤维素复合膜,可有效光催化降解污水中有机染料,可广泛应用于化工、生物医用及环保等领域。The invention relates to the combination of inorganic nano-semiconductor ZnS particles and natural organic polymer cellulose film to prepare a nano-ZnS/cellulose composite film with photocatalytic function, which can effectively photocatalyze and degrade organic dyes in sewage, and can be widely used in chemical industry, Biomedical and environmental protection and other fields.

背景技术Background technique

无机纳米ZnS粒子是一种重要的金属硫系半导体材料,具有独特的量子尺寸效应、体积效应、表面效应及量子隧道效应等特性,在电学、光学、磁学、力学及催化等领域呈现出许多优异的性能,有着广阔的应用前景。Inorganic nano-ZnS particles are an important metal chalcogenide semiconductor material, which has unique properties such as quantum size effect, volume effect, surface effect and quantum tunneling effect. Excellent performance, has broad application prospects.

无机纳米ZnS具有安全无毒、3.6~3.8eV之间的宽带隙、强吸收性及优异的光电催化性能,被广泛做为发光材料、非线性光学材料及光催化材料等。但由于纳米ZnS粒径小、表面能大等特点易引起团聚;另外,由于其水溶性差,难以均匀地分散在水溶液中;同时,纳米粒子光催化剂材料在分离和回收处理方面仍存在很大问题。因而,ZnS纳米半导体材料在光催化领域的实际应用中受到很大的限制。为解决以上问题,需要制备出一种高效、经济及环保的光催化材料。如:Zhang Guanghui等使用蛋壳膜(ESM)作为ZnS的基体材料,采用液体浸渍法成功制备了具有光催化活性的ZnS/蛋壳膜复合材料。众所周知,纤维素是自然界中最丰富的可再生资源之一,具有安全无毒、成本低廉、成膜性好、化学稳定性及热稳定性好等优点,广泛应用于包装、化工、水处理及生物医用等方面,是理想的绿色环保材料,可以作为一种有效的有机高分子基底材料。Inorganic nano-ZnS is safe and non-toxic, has a wide bandgap between 3.6 and 3.8eV, strong absorption and excellent photoelectric catalytic performance, and is widely used as a luminescent material, nonlinear optical material and photocatalytic material. However, due to the small particle size and large surface energy of nano-ZnS, it is easy to cause agglomeration; in addition, due to its poor water solubility, it is difficult to disperse uniformly in aqueous solution; at the same time, there are still great problems in the separation and recycling of nano-particle photocatalyst materials. . Therefore, the practical application of ZnS nano-semiconductor materials in the field of photocatalysis is greatly limited. In order to solve the above problems, it is necessary to prepare an efficient, economical and environmentally friendly photocatalytic material. For example, Zhang Guanghui et al. used eggshell membrane (ESM) as the matrix material of ZnS, and successfully prepared ZnS/eggshell membrane composite materials with photocatalytic activity by liquid impregnation method. As we all know, cellulose is one of the most abundant renewable resources in nature. It has the advantages of safety, non-toxicity, low cost, good film-forming property, good chemical stability and thermal stability, etc. It is widely used in packaging, chemical industry, water treatment and It is an ideal green environmental protection material for biomedicine and other aspects, and can be used as an effective organic polymer base material.

发明内容Contents of the invention

本发明的目的在于克服现有技术的不足,包括降低成本、有限的技术支持及环保要求等方面,提供一种具有光催化活性的纳米ZnS/纤维素复合膜材料及其制备方法。本发明工艺流程简单、环保无污染、易于操作、价格低廉、不需要使用昂贵的仪器及复杂的操作步骤,易于推广;同时,制备的纳米ZnS/纤维素复合膜材料具有良好的紫外光催化降解有机污染物的性质。The purpose of the present invention is to overcome the deficiencies of the prior art, including aspects such as cost reduction, limited technical support and environmental protection requirements, and provide a nano-ZnS/cellulose composite membrane material with photocatalytic activity and a preparation method thereof. The technological process of the present invention is simple, environmental protection and pollution-free, easy to operate, low in price, does not need to use expensive instruments and complicated operation steps, and is easy to popularize; at the same time, the prepared nano-ZnS/cellulose composite membrane material has good ultraviolet photocatalytic degradation The nature of organic pollutants.

本发明将无机纳米ZnS颗粒和天然植物纤维素再生膜首次复合,制备了具有光催化活性的ZnS/纤维素复合膜材料。为无机纳米材料选择有机高分子纤维素膜作为载体材料,有利于改善无机纳米ZnS粒子的稳定性差和易于团聚的问题,提高催化剂的催化活性,并且有利于催化剂的分离和回收。The invention combines inorganic nano ZnS particles and natural plant cellulose regenerated membrane for the first time, and prepares a ZnS/cellulose composite membrane material with photocatalytic activity. Selecting the organic polymer cellulose membrane as the carrier material for inorganic nanomaterials is beneficial to improve the poor stability and easy aggregation of inorganic nano ZnS particles, improve the catalytic activity of the catalyst, and facilitate the separation and recovery of the catalyst.

为实现上述目的,本发明采用如下技术方案:To achieve the above object, the present invention adopts the following technical solutions:

一种制备具有光催化活性的纳米ZnS/纤维素复合膜的方法,其特征在于通过采用NMMO工艺制备纯纤维素膜,然后采用液体浸渍法原位合成ZnS粒子而制备纳米ZnS/纤维素复合膜材料,包括以下步骤:A method for preparing a nano-ZnS/cellulose composite film with photocatalytic activity, characterized in that the nano-ZnS/cellulose composite film is prepared by using the NMMO process to prepare a pure cellulose film, and then using a liquid immersion method to synthesize ZnS particles in situ materials, including the following steps:

步骤(1):纯纤维素膜的制备Step (1): Preparation of pure cellulose membrane

纤维素膜中纤维素为木浆纤维素、棉浆纤维素或草浆纤维素中的一种或两种混合,将经粉碎处理的原材料纤维素加入到含有经浓缩的含水量约为13.3%的NMMO溶剂和质量为纤维素质量0.5~1.5%的抗氧化剂中,配制成纤维素铸膜液,所得棉浆纤维含量为铸膜液质量的5~11%;搅拌均匀,溶胀0.5~3.0个小时,置于100~120℃的真空干燥箱中溶解完全,待溶液呈琥珀色、均匀透明的溶液时,在60~80℃下真空脱泡2~5h,刮膜;随后,经凝固浴及水洗浴处理,得到湿的纯纤维素膜,其中凝固浴及水洗浴是在20~40℃去离子水中进行;The cellulose in the cellulose film is one or a mixture of wood pulp cellulose, cotton pulp cellulose or straw pulp cellulose, and the pulverized raw material cellulose is added to the concentrated water content of about 13.3%. The NMMO solvent and the antioxidant whose quality is 0.5-1.5% of the cellulose mass are prepared into a cellulose casting liquid, and the fiber content of the obtained cotton pulp is 5-11% of the mass of the casting liquid; stir evenly, and swell 0.5-3.0 After 1 hour, put it in a vacuum drying oven at 100-120°C to dissolve completely. When the solution is amber, uniform and transparent, degas it in vacuum at 60-80°C for 2-5 hours, and scrape the film; then, pass through a coagulation bath and Water bath treatment to obtain a wet pure cellulose film, wherein the coagulation bath and water bath are carried out in deionized water at 20-40°C;

步骤(2):纳米ZnS/纤维素复合膜材料的制备Step (2): Preparation of nano ZnS/cellulose composite membrane material

将步骤(1)中所得湿膜裁剪成一定大小的膜,浸泡到Zn前驱体溶液中,反应3~6h后,取出并用去离子水冲洗;然后再将其浸入含S前驱体溶液中,反应3~6h后,取出并用去离子水冲洗;以上过程为一个循环周期,浸渍完成后,将样品置于室温下自然干燥,得到浸渍一次具有光催化活性的纳米ZnS/纤维素复合膜材料。Cut the wet film obtained in step (1) into a film of a certain size, soak it in the Zn precursor solution, react for 3 to 6 hours, take it out and rinse it with deionized water; then immerse it in the S-containing precursor solution, react After 3 to 6 hours, take it out and rinse it with deionized water; the above process is a cycle. After the impregnation is completed, the sample is placed at room temperature to dry naturally, and a nano-ZnS/cellulose composite membrane material with photocatalytic activity is obtained once impregnated.

所述的步骤(1)中原材料纤维素为农业废弃物或者植物纤维素。The raw material cellulose in the step (1) is agricultural waste or plant cellulose.

所述的步骤(1)中所述的农业废弃物为芦苇、秸秆、麦秆、稻草、甘蔗渣、稻壳、花生壳。The agricultural wastes described in the step (1) are reeds, straws, wheat straws, straw, bagasse, rice husks, and peanut husks.

所述的步骤(1)中溶剂NMMO的纯化处理过程如下:取一定量市售的含水量为50~60%的NMMO装入旋转蒸发仪中,在真空度为-0.08~-0.1MPa,温度为90~95℃的条件下,旋转蒸发出一定量的水,直到NMMO含水量为13.3%为止,得到溶解纤维素的NMMO·H2O溶剂。The purification process of the solvent NMMO in the described step (1) is as follows: take a certain amount of commercially available NMMO with a water content of 50-60% and put it into a rotary evaporator, and the vacuum degree is -0.08--0.1MPa, the temperature Under the condition of 90-95°C, a certain amount of water was evaporated by rotary evaporation until the water content of NMMO was 13.3%, and NMMO·H2O solvent for dissolving cellulose was obtained.

所述的步骤(1)中抗氧化剂为抗坏血酸或没食子酸。In the described step (1), the antioxidant is ascorbic acid or gallic acid.

所述的步骤(2)使用的Zn前驱体溶液为水溶性的锌源,S前驱体溶液为水溶性的硫源。The Zn precursor solution used in the step (2) is a water-soluble zinc source, and the S precursor solution is a water-soluble sulfur source.

所述的水溶性的锌源为硫酸锌溶液、氯化锌溶液、醋酸锌溶液中的一种;水溶性的硫源为硫化钠溶液、硫代硫酸钠溶液、硫代乙酰胺溶液中的一种。The water-soluble zinc source is one of zinc sulfate solution, zinc chloride solution, and zinc acetate solution; the water-soluble sulfur source is one of sodium sulfide solution, sodium thiosulfate solution, and thioacetamide solution. kind.

所述的Zn前驱体溶液与S前驱体溶液的摩尔浓度之比为1:1。The molar concentration ratio of the Zn precursor solution to the S precursor solution is 1:1.

本发明中使用的抗氧化剂为最常用的抗氧化剂——抗坏血酸,也称为维生素C。The antioxidant used in the present invention is the most commonly used antioxidant - ascorbic acid, also known as vitamin C.

本发明方法制备的是具有光催化活性的纳米ZnS/纤维素复合膜材料。The method prepared by the invention is a nanometer ZnS/cellulose composite film material with photocatalytic activity.

将上面所述方法制备的具有光催化活性的纳米ZnS/纤维素复合膜材料,在紫外光的照射下,可用于降解废水中的有机染料。The photocatalytically active nano ZnS/cellulose composite membrane material prepared by the above method can be used to degrade organic dyes in wastewater under the irradiation of ultraviolet light.

与现有技术相比,本发明具有如下优点:Compared with prior art, the present invention has following advantage:

1.所用的原材料为可再生的天然高分子纤维素,这种多羟基的高分子聚合物具有良好的物理和化学改性的活性,且纤维素来源广泛,价格低廉;1. The raw material used is renewable natural high-molecular cellulose. This polyhydroxy high-molecular polymer has good physical and chemical modification activity, and the cellulose has a wide range of sources and low price;

2.纤维素膜的制备工艺采用的是一种新型的绿色生产工艺—NMMO工艺,此工艺溶剂为NMMO,该溶剂无毒无污染,可回收;工艺流程简单、化学原料使用量和能耗较低,是一种纯物理过程的绿色生产工艺;2. The preparation process of cellulose film adopts a new green production process - NMMO process. The solvent of this process is NMMO. The solvent is non-toxic, non-polluting and recyclable; Low, it is a green production process of pure physical process;

3.纳米ZnS粒子在纤维素膜上发生原位合成,该反应在常温下进行,条件温和,操作方便;3. Nano-ZnS particles are synthesized in situ on the cellulose film, the reaction is carried out at room temperature, the conditions are mild, and the operation is convenient;

4.具有光催化活性的纳米ZnS/纤维素复合膜材料作为光催化剂时,易于分离和回收;4. Nano-ZnS/cellulose composite membrane material with photocatalytic activity is easy to separate and recycle when used as a photocatalyst;

5.本发明中的具有光催化活性的纳米ZnS/纤维素复合膜材料的制备工艺简单、易于操作、设备简单、成本低廉、易于推广。5. The nano-ZnS/cellulose composite membrane material with photocatalytic activity in the present invention has a simple preparation process, easy operation, simple equipment, low cost and easy popularization.

附图说明Description of drawings

图1为本发明所得到的重复浸渍4次的纳米ZnS/纤维素复合膜随接触时间变化的紫外光催化降解甲基橙的吸收变化图。Fig. 1 is a diagram of the absorption change of the ultraviolet photocatalytic degradation methyl orange of the nano-ZnS/cellulose composite film dipped 4 times in the present invention as a function of the contact time.

图2本发明所得到的纳米ZnS/纤维素复合膜紫外光催化降解甲基橙的降解率图。Fig. 2 is a diagram of the degradation rate of the nano-ZnS/cellulose composite film obtained by the present invention for the ultraviolet photocatalytic degradation of methyl orange.

图中:a~h代表光催化实验中的不同的取样时间,即:0min,20min,40min,60min,80min,100min,120min,150min;C1代表浸渍1次的膜试样;C2代表浸渍2次的膜试样;C3代表浸渍3次的膜试样;C4代表浸渍4次的膜试样。In the figure: a~h represent different sampling times in the photocatalytic experiment, namely: 0min, 20min, 40min, 60min, 80min, 100min, 120min, 150min; C1 represents the membrane sample impregnated once; C2 represents the impregnated twice C3 represents the membrane sample dipped 3 times; C4 represents the membrane sample dipped 4 times.

具体实施方式Detailed ways

本发明中,NMMO溶剂为氮甲基吗啉氧化物溶剂。In the present invention, the NMMO solvent is nitrogen methylmorpholine oxide solvent.

实施例1:Example 1:

1.纤维素膜的制备1. Preparation of Cellulose Membrane

将经粉碎处理后的2g棉浆纤维素、木浆纤维素或草浆纤维素中的一种加入到含有经浓缩的31g含水量约为13.3%的NMMO溶剂和0.02g抗坏血酸(质量约为纤维素量的1%)的烧杯中,配制成纤维素含量约为6%的铸膜液,搅拌均匀;溶胀2h后,置于110℃的真空干燥箱中溶解完全,待溶液呈琥珀色、均匀透明溶液时,置于80℃下真空脱泡4h,刮膜;随后,经凝固浴(25℃左右去离子水)及水洗浴(25℃左右去离子水)处理,得到湿的纯棉浆纤维素膜。One of the 2g cotton pulp cellulose, wood pulp cellulose or straw pulp cellulose after pulverization is added to the NMMO solvent and 0.02g ascorbic acid (mass approx. 1% of the element weight) in a beaker, prepare a casting solution with a cellulose content of about 6%, and stir evenly; after swelling for 2 hours, put it in a vacuum drying oven at 110°C to dissolve completely, and wait until the solution is amber and uniform When the solution is transparent, place it at 80°C for vacuum defoaming for 4 hours, and scrape the film; then, treat it with a coagulation bath (about 25°C deionized water) and a water bath (about 25°C deionized water) to obtain wet pure cotton pulp fibers plain film.

2.具有光催化活性的纳米ZnS/纤维素复合膜材料的制备2. Preparation of nano-ZnS/cellulose composite membrane material with photocatalytic activity

将上述湿膜裁剪成大小为10㎝×15㎝的膜,浸泡到0.1M的硫酸锌前驱体溶液中,反应5h后,取出并用去离子水冲洗;然后再将其浸入0.1M的硫化钠前驱体溶液中,反应5h后,取出并用去离子水冲洗。以上过程为一个循环周期,浸渍完成后,将样品置于室温下自然干燥得到浸渍1次的具有光催化活性的纳米ZnS/纤维素复合膜材料。Cut the above wet film into a film with a size of 10cm×15cm, soak it in 0.1M zinc sulfate precursor solution, react for 5h, take it out and rinse it with deionized water; then immerse it in 0.1M sodium sulfide precursor solution After reacting for 5 hours, it was taken out and rinsed with deionized water. The above process is a cycle. After the impregnation is completed, the sample is placed at room temperature and dried naturally to obtain a photocatalytically active nano-ZnS/cellulose composite membrane material impregnated once.

实施例2:Example 2:

1.纤维素膜的制备1. Preparation of Cellulose Membrane

纤维素膜的制备与实施例1相同。The preparation of the cellulose film was the same as in Example 1.

2.具有光催化活性的纳米ZnS/纤维素复合膜材料的制备2. Preparation of nano-ZnS/cellulose composite membrane material with photocatalytic activity

将上述湿膜裁剪成大小为10㎝×15㎝的膜,浸泡到0.1M的硫酸锌前驱体溶液中,反应5h后,取出并用去离子水冲洗;然后再将其放入0.1M的硫化钠前驱体溶液中,反应5h后,取出并用去离子水冲洗。以上过程为一个循环周期,再进行第2次循环浸渍实验,浸渍完成后,将样品膜置于室温下自然干燥得到浸渍2次的具有光催化活性的纳米ZnS/纤维素复合膜材料。Cut the above wet film into a film with a size of 10cm×15cm, soak it in 0.1M zinc sulfate precursor solution, react for 5h, take it out and rinse it with deionized water; then put it into 0.1M sodium sulfide After reacting for 5 hours in the precursor solution, take it out and rinse it with deionized water. The above process is a cycle, and then the second cycle of impregnation experiment is carried out. After the impregnation is completed, the sample film is naturally dried at room temperature to obtain a nano-ZnS/cellulose composite membrane material with photocatalytic activity that is impregnated twice.

实施例3:Example 3:

1.纤维素膜的制备1. Preparation of Cellulose Membrane

纤维素膜的制备方法与实施例1相同。The preparation method of the cellulose film is the same as that of Example 1.

2.具有光催化活性的纳米ZnS/纤维素复合膜材料的制备2. Preparation of nano-ZnS/cellulose composite membrane material with photocatalytic activity

将上述湿膜裁剪成大小为10㎝×15㎝的膜,浸泡到0.1M的硫酸锌前驱体溶液中,反应5h后,取出并用去离子水冲洗;然后再将其放入0.1M的硫化钠前驱体溶液中,反应5h后,取出并用去离子水冲洗。以上过程为一个循环周期,再重复进行2次循环浸渍实验,浸渍完成后,将样品膜置于室温下自然干燥得到浸渍3次的具有光催化活性的纳米ZnS/纤维素复合膜材料。Cut the above wet film into a film with a size of 10cm×15cm, soak it in 0.1M zinc sulfate precursor solution, react for 5h, take it out and rinse it with deionized water; then put it into 0.1M sodium sulfide After reacting for 5 hours in the precursor solution, take it out and rinse it with deionized water. The above process is a cycle, and then repeat the impregnation experiment twice. After the impregnation is completed, the sample film is naturally dried at room temperature to obtain a nano-ZnS/cellulose composite membrane material with photocatalytic activity that has been impregnated three times.

实施例4:Example 4:

1.纤维素膜的制备1. Preparation of Cellulose Membrane

纤维素膜的制备与实施例1相同。The preparation of the cellulose film was the same as in Example 1.

2.具有光催化活性的纳米ZnS/纤维素复合膜材料的制备2. Preparation of nano-ZnS/cellulose composite membrane material with photocatalytic activity

将上述湿膜裁剪成大小为10㎝×15㎝的膜,浸泡到0.1M的硫酸锌前驱体溶液中,反应5h后,取出并用去离子水冲洗;然后再将其放入0.1M的硫化钠前驱体溶液中,反应5h后,取出并用去离子水冲洗。以上过程为一个循环周期,再重复进行3次循环浸渍实验,浸渍完成后,将样品膜置于室温下自然干燥得到浸渍4次的具有光催化活性的纳米ZnS/纤维素复合膜材料。Cut the above wet film into a film with a size of 10cm×15cm, soak it in 0.1M zinc sulfate precursor solution, react for 5h, take it out and rinse it with deionized water; then put it into 0.1M sodium sulfide After reacting for 5 hours in the precursor solution, take it out and rinse it with deionized water. The above process is a cyclical period, and then repeat the impregnation experiment 3 times. After the impregnation is completed, the sample film is dried naturally at room temperature to obtain a nano-ZnS/cellulose composite membrane material with photocatalytic activity impregnated 4 times.

3.纳米ZnS/纤维素复合膜材料光催化性能的检测:本发明以甲基橙(MO)为有机污染物,以纳米ZnS/纤维素复合膜材料为光催化剂,在紫外光的照射下进行光催化实验,以表征样品膜的光催化活性。具体实验过程如下:用天平分别称取等量的2g上述4个实施例中制备好的纳米ZnS/纤维素复合膜材料,以及1个纯纤维素膜,用50ml的量筒平行量取40ml,10㎎/L的MO溶液5份,将两者都加入到石英试管中;然后放入磁子,把试管都放进BL-GHX-V型光化学反应仪中,在暗室中搅拌放置20min,待吸附平衡后,开启300W的汞灯照射,反应150min,每隔20min取一次试样,将所取试样进行标号1-7,将原MO液标记为试样0。每个所取降解样品经离心后,取上清液用紫外-可见分光光度计测量在λ=464nm处溶液的吸光度值,由此得出光催化反应前后MO溶液的浓度,计算出降解率,公式如下:3. The detection of the photocatalytic property of nano-ZnS/cellulose composite film material: the present invention takes methyl orange (MO) as organic pollutant, takes nano-ZnS/cellulose composite film material as photocatalyst, carries out under the irradiation of ultraviolet light Photocatalytic experiment to characterize the photocatalytic activity of the sample film. The specific experimental process is as follows: Weigh the same amount of 2g of nano-ZnS/cellulose composite membrane materials prepared in the above-mentioned 4 embodiments and 1 pure cellulose membrane with a balance, and measure 40ml in parallel with a 50ml graduated cylinder. ㎎/L MO solution 5 parts, add both into the quartz test tube; then put the magneton, put the test tubes into the BL-GHX-V photochemical reaction apparatus, stir and place in the dark room for 20min, wait for adsorption After equilibration, turn on the 300W mercury lamp to irradiate, react for 150min, take a sample every 20min, label the samples taken as 1-7, and mark the original MO solution as sample 0. After each degraded sample is centrifuged, take the supernatant and measure the absorbance value of the solution at λ=464nm with a UV-visible spectrophotometer, so as to obtain the concentration of the MO solution before and after the photocatalytic reaction, and calculate the degradation rate, the formula as follows:

降解率D=(A0-A)/A0×100%=(C0-C)/C0×100%Degradation rate D=(A 0 -A)/A 0 ×100%=(C 0 -C)/C 0 ×100%

式中:D代表催化剂膜试样降解MO的降解率;In the formula: D represents the degradation rate of catalyst membrane sample degradation MO;

A0-初始的甲基橙MO溶液在相同波长λ=464nm下的吸光度;A 0 -absorbance of the initial methyl orange MO solution at the same wavelength λ=464nm;

A-反应一段时间后溶液中MO溶液在λ=464nm下的吸光度;The absorbance of the MO solution in the solution at λ=464nm after a period of time after the A-reaction;

C0-初始的甲基橙MO溶液在相同波长λ=464nm下的MO溶液的浓度;C 0 -the concentration of the MO solution under the same wavelength λ=464nm of the initial methyl orange MO solution;

C-反应一段时间后溶液中MO溶液在λ=464nm下的MO溶液的浓度。The concentration of the MO solution at λ=464nm of the MO solution in the solution after C-reaction for a period of time.

由附图1可知:以重复浸渍4次的纳米ZnS/纤维素复合膜为光催化剂,在300W汞灯的照射下,溶液中的有机染料甲基橙(MO)的浓度随光照时间的增加而降低,光照150min后,溶液中的甲基橙的浓度很低,说明本发明制备的光催化剂对甲基橙的光催化效果较好。As can be seen from accompanying drawing 1: take the nanometer ZnS/cellulose composite membrane that impregnates repeatedly 4 times as photocatalyst, under the irradiation of 300W mercury lamp, the concentration of the organic dye methyl orange (MO) in the solution increases with the increase of illumination time After 150min of light irradiation, the concentration of methyl orange in the solution is very low, indicating that the photocatalyst prepared by the present invention has a better photocatalytic effect on methyl orange.

由附图2可知:当以纯纤维素膜作为光催化剂时,溶液中的甲基橙的浓度变化不大,即降解效果不好,不到10%,这说明纯纤维素膜不具有光催化性能,而此时溶液中的甲基橙浓度有所变化的原因是由纯纤维素膜的微量物理吸附作用导致的;随着膜的重复浸渍次数从1增加到4,纳米ZnS/纤维素复合膜对溶液中的甲基橙的降解率从60%增加到90%,这说明纳米ZnS/纤维素复合膜具有光催化性能,并且随着重复浸渍次数的增加,负载在纤维素膜上的ZnS纳米粒子的量增加,这样纳米ZnS/纤维素复合膜的光催化降解有机染料的效果增加。As can be seen from accompanying drawing 2: when using pure cellulose film as photocatalyst, the concentration change of the methyl orange in the solution is little, promptly degradation effect is bad, less than 10%, this shows that pure cellulose film does not have photocatalytic performance , and the reason for the change in the concentration of methyl orange in the solution at this time is caused by the microscopic physical adsorption of the pure cellulose membrane; as the number of repeated dipping of the membrane increases from 1 to 4, the nano-ZnS/cellulose composite membrane The degradation rate of methyl orange in the solution increased from 60% to 90%, which shows that the nano-ZnS/cellulose composite film has photocatalytic properties, and with the increase of the number of repeated immersion, the ZnS nanoparticles loaded on the cellulose film The amount of particles increases, so the effect of photocatalytic degradation of organic dyes of the nano-ZnS/cellulose composite film increases.

上述实施例为本发明较佳的实施方式,但本发明的实施方式并不受所述实施例的限制,其他的任何未背离本发明的精神实质与原理下所作的改变、修饰、替代、组合、简化,均应为等效的置换方式,都包含在本发明的保护范围之内。The above-mentioned embodiment is a preferred embodiment of the present invention, but the embodiment of the present invention is not limited by the embodiment, and any other changes, modifications, substitutions and combinations made without departing from the spirit and principle of the present invention , simplification, all should be equivalent replacement methods, and are all included in the protection scope of the present invention.

Claims (8)

1.一种制备具有光催化活性的纳米ZnS/纤维素复合膜的方法,其特征在于通过采用NMMO工艺制备纯纤维素膜,然后采用液体浸渍法原位合成ZnS粒子而制备纳米ZnS/纤维素复合膜材料,包括以下步骤:1. A method for preparing a nano ZnS/cellulose composite film with photocatalytic activity, characterized in that by adopting NMMO process to prepare pure cellulose film, then adopting liquid immersion method to synthesize ZnS particles in situ to prepare nano ZnS/cellulose Composite membrane material, comprises the following steps: 步骤(1):纯纤维素膜的制备Step (1): Preparation of pure cellulose membrane 纤维素膜中纤维素为木浆纤维素、棉浆纤维素或草浆纤维素中的一种或两种混合,将经粉碎处理的原材料纤维素加入到含有经浓缩的含水量约为13.3%的NMMO溶剂和质量为纤维素质量0.5~1.5%的抗氧化剂中,配制成纤维素铸膜液,所得棉浆纤维含量为铸膜液质量的5~11%;搅拌均匀,溶胀0.5~3.0个小时,置于100~120℃的真空干燥箱中溶解完全,待溶液呈琥珀色、均匀透明的溶液时,在60~80℃下真空脱泡2~5h,刮膜;随后,经凝固浴及水洗浴处理,得到湿的纯纤维素膜,其中凝固浴及水洗浴是在20~40℃去离子水中进行;The cellulose in the cellulose film is one or a mixture of wood pulp cellulose, cotton pulp cellulose or straw pulp cellulose, and the pulverized raw material cellulose is added to the concentrated water content of about 13.3%. The NMMO solvent and the antioxidant whose quality is 0.5-1.5% of the cellulose mass are prepared into a cellulose casting liquid, and the fiber content of the obtained cotton pulp is 5-11% of the mass of the casting liquid; stir evenly, and swell 0.5-3.0 After 1 hour, put it in a vacuum drying oven at 100-120°C to dissolve completely. When the solution is amber, uniform and transparent, degas it in vacuum at 60-80°C for 2-5 hours, and scrape the film; then, pass through a coagulation bath and Water bath treatment to obtain a wet pure cellulose film, wherein the coagulation bath and water bath are carried out in deionized water at 20-40°C; 步骤(2):纳米ZnS/纤维素复合膜材料的制备Step (2): Preparation of nano ZnS/cellulose composite membrane material 将步骤(1)中所得湿膜裁剪成一定大小的膜,浸泡到Zn前驱体溶液中,反应3~6h后,取出并用去离子水冲洗;然后再将其浸入含S前驱体溶液中,反应3~6h后,取出并用去离子水冲洗;以上过程为一个循环周期,浸渍完成后,将样品置于室温下自然干燥,得到浸渍一次具有光催化活性的纳米ZnS/纤维素复合膜材料。Cut the wet film obtained in step (1) into a film of a certain size, soak it in the Zn precursor solution, react for 3 to 6 hours, take it out and rinse it with deionized water; then immerse it in the S-containing precursor solution, react After 3 to 6 hours, take it out and rinse it with deionized water; the above process is a cycle. After the impregnation is completed, the sample is placed at room temperature to dry naturally, and a nano-ZnS/cellulose composite membrane material with photocatalytic activity is obtained once impregnated. 2.根据权利要求1所述的制备具有光催化活性的纳米ZnS/纤维素复合膜的方法,其特征在于:步骤(1)中原材料纤维素为农业废弃物或者植物纤维素。2. The method for preparing a nano-ZnS/cellulose composite film with photocatalytic activity according to claim 1, characterized in that: the raw material cellulose in step (1) is agricultural waste or plant cellulose. 3.根据权利要求2所述的制备具有光催化活性的纳米ZnS/纤维素复合膜的方法,其特征在于:步骤(1)中所述的农业废弃物为芦苇、秸秆、麦秆、稻草、甘蔗渣、稻壳、花生壳。3. the method for preparing the nano ZnS/cellulose composite film with photocatalytic activity according to claim 2, is characterized in that: the agricultural waste described in step (1) is reed, straw, wheat straw, rice straw, Bagasse, rice husk, peanut husk. 4.根据权利要求1所述的制备具有光催化活性的纳米ZnS/纤维素复合膜的方法,其特征在于:步骤(1)中溶剂NMMO的纯化处理过程如下:取一定量市售的含水量为50~60%的NMMO装入旋转蒸发仪中,在真空度为-0.08~-0.1MPa,温度为90~95℃的条件下,旋转蒸发出一定量的水,直到NMMO含水量为13.3%为止,得到溶解纤维素的NMMO·H2O溶剂。4. the preparation according to claim 1 has the method for the nanometer ZnS/cellulose composite membrane of photocatalytic activity, it is characterized in that: the purification treatment process of solvent NMMO is as follows in the step (1): get a certain amount of commercially available water content Put 50-60% NMMO into a rotary evaporator, and under the conditions of vacuum degree of -0.08-0.1MPa and temperature of 90-95°C, a certain amount of water is evaporated until the water content of NMMO is 13.3%. So far, NMMO·H2O solvent for dissolving cellulose is obtained. 5.根据权利要求1所述的制备具有光催化活性的纳米ZnS/纤维素复合膜的方法,其特征在于:步骤(1)中抗氧化剂为抗坏血酸或没食子酸。5. The method for preparing a nano-ZnS/cellulose composite film with photocatalytic activity according to claim 1, characterized in that: in the step (1), the antioxidant is ascorbic acid or gallic acid. 6.根据权利要求1所述的制备具有光催化活性的纳米ZnS/纤维素复合膜的方法,其特征在于:步骤(2)使用的Zn前驱体溶液为水溶性的锌源,S前驱体溶液为水溶性的硫源。6. the method for preparing the nanometer ZnS/cellulose composite film with photocatalytic activity according to claim 1, is characterized in that: the Zn precursor solution that step (2) uses is water-soluble zinc source, and S precursor solution It is a water-soluble sulfur source. 7.根据权利要求6所述的制备具有光催化活性的纳米ZnS/纤维素复合膜的方法,其特征在于:水溶性的锌源为硫酸锌溶液、氯化锌溶液、醋酸锌溶液中的一种;水溶性的硫源为硫化钠溶液、硫代硫酸钠溶液、硫代乙酰胺溶液中的一种。7. the method for preparing the nanometer ZnS/cellulose composite film with photocatalytic activity according to claim 6 is characterized in that: the water-soluble zinc source is one of zinc sulfate solution, zinc chloride solution, zinc acetate solution species; the water-soluble sulfur source is one of sodium sulfide solution, sodium thiosulfate solution, and thioacetamide solution. 8.根据权利要求5所述的制备具有光催化活性的纳米ZnS/纤维素复合膜的方法,其特征在于:Zn前驱体溶液与S前驱体溶液的摩尔浓度之比为1:1。8. The method for preparing a photocatalytically active nano-ZnS/cellulose composite film according to claim 5, wherein the ratio of the molar concentration of the Zn precursor solution to the S precursor solution is 1:1.
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107597194A (en) * 2017-09-28 2018-01-19 东北林业大学 A kind of preparation method of new ZnO/ fungies fiber optic catalytic composite material
CN113731186A (en) * 2021-08-23 2021-12-03 广西大学 Preparation method of metal nanoparticle/lignocellulose-based functionalized filter membrane for treating wastewater

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1996004069A1 (en) * 1994-08-02 1996-02-15 North West Water Group Plc Membrane
JPH1128364A (en) * 1997-07-11 1999-02-02 Toshiba Corp Photocatalyst composite body and water purification device
CN103217727A (en) * 2013-04-15 2013-07-24 东华大学 Bacterial cellulose base optical thin film and preparation method thereof
JP2013244455A (en) * 2012-05-25 2013-12-09 Mitsubishi Rayon Co Ltd Wastewater treatment apparatus and wastewater treatment method

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1996004069A1 (en) * 1994-08-02 1996-02-15 North West Water Group Plc Membrane
JPH1128364A (en) * 1997-07-11 1999-02-02 Toshiba Corp Photocatalyst composite body and water purification device
JP2013244455A (en) * 2012-05-25 2013-12-09 Mitsubishi Rayon Co Ltd Wastewater treatment apparatus and wastewater treatment method
CN103217727A (en) * 2013-04-15 2013-07-24 东华大学 Bacterial cellulose base optical thin film and preparation method thereof

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
张光辉: "硫化锌/鸡蛋膜复合材料的制备及其光催化性能", 《中国优秀硕士论文电子期刊网》 *
张耀鹏: "NMMO法纤维素膜及其形成机理的研究", 《中国博士学位论文电子期刊网》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107597194A (en) * 2017-09-28 2018-01-19 东北林业大学 A kind of preparation method of new ZnO/ fungies fiber optic catalytic composite material
CN113731186A (en) * 2021-08-23 2021-12-03 广西大学 Preparation method of metal nanoparticle/lignocellulose-based functionalized filter membrane for treating wastewater

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