CN109989273A - A kind of preparation method and application of photocatalytic coating fabric - Google Patents

A kind of preparation method and application of photocatalytic coating fabric Download PDF

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CN109989273A
CN109989273A CN201910268569.9A CN201910268569A CN109989273A CN 109989273 A CN109989273 A CN 109989273A CN 201910268569 A CN201910268569 A CN 201910268569A CN 109989273 A CN109989273 A CN 109989273A
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fabric
titanium dioxide
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titania
neoprene
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CN109989273B (en
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项顼
曹振
苏辉
张建强
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Yisheng Environmental Protection Technology Co Ltd
Beijing University of Chemical Technology
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Beijing University of Chemical Technology
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/26Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24
    • B01J31/38Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24 of titanium, zirconium or hafnium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • DTEXTILES; PAPER
    • D06TREATMENT OF TEXTILES OR THE LIKE; LAUNDERING; FLEXIBLE MATERIALS NOT OTHERWISE PROVIDED FOR
    • D06NWALL, FLOOR, OR LIKE COVERING MATERIALS, e.g. LINOLEUM, OILCLOTH, ARTIFICIAL LEATHER, ROOFING FELT, CONSISTING OF A FIBROUS WEB COATED WITH A LAYER OF MACROMOLECULAR MATERIAL; FLEXIBLE SHEET MATERIAL NOT OTHERWISE PROVIDED FOR
    • D06N3/00Artificial leather, oilcloth or other material obtained by covering fibrous webs with macromolecular material, e.g. resins, rubber or derivatives thereof
    • D06N3/0056Artificial leather, oilcloth or other material obtained by covering fibrous webs with macromolecular material, e.g. resins, rubber or derivatives thereof characterised by the compounding ingredients of the macro-molecular coating
    • D06N3/0063Inorganic compounding ingredients, e.g. metals, carbon fibres, Na2CO3, metal layers; Post-treatment with inorganic compounds
    • DTEXTILES; PAPER
    • D06TREATMENT OF TEXTILES OR THE LIKE; LAUNDERING; FLEXIBLE MATERIALS NOT OTHERWISE PROVIDED FOR
    • D06NWALL, FLOOR, OR LIKE COVERING MATERIALS, e.g. LINOLEUM, OILCLOTH, ARTIFICIAL LEATHER, ROOFING FELT, CONSISTING OF A FIBROUS WEB COATED WITH A LAYER OF MACROMOLECULAR MATERIAL; FLEXIBLE SHEET MATERIAL NOT OTHERWISE PROVIDED FOR
    • D06N3/00Artificial leather, oilcloth or other material obtained by covering fibrous webs with macromolecular material, e.g. resins, rubber or derivatives thereof
    • D06N3/04Artificial leather, oilcloth or other material obtained by covering fibrous webs with macromolecular material, e.g. resins, rubber or derivatives thereof with macromolecular compounds obtained by reactions only involving carbon-to-carbon unsaturated bonds
    • D06N3/10Artificial leather, oilcloth or other material obtained by covering fibrous webs with macromolecular material, e.g. resins, rubber or derivatives thereof with macromolecular compounds obtained by reactions only involving carbon-to-carbon unsaturated bonds with styrene-butadiene copolymerisation products or other synthetic rubbers or elastomers except polyurethanes
    • D06N3/106Elastomers
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/36Organic compounds containing halogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/40Organic compounds containing sulfur
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
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  • Textile Engineering (AREA)
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Abstract

本发明公开了一种可见光催化涂层织物的制备方法及其应用,该方法选用富含氯元素的氯丁橡胶为粘合剂,先将其涂覆在织物表面,再将光催化剂二氧化钛喷涂到涂覆有粘合剂的织物表面,使光催化剂稳定于织物表面。氯丁橡胶作粘合剂不仅能够稳定地将二氧化钛固定在织物表面,且氯丁橡胶脱氯,同时氯离子对二氧化钛进行改性,部分氯离子能稳定地吸附在二氧化钛表面显著改变了二氧化钛表面带电性,促使二氧化钛表面带负电,对阳离子染料有更好的吸附从而有更优的降解性能。部分氯会进入二氧化钛晶格取代晶格氧,使得二氧化钛产生氧缺陷,减小二氧化钛带隙增强了二氧化钛对可见光的吸收,从而提高二氧化钛可见光催化降解性能。The invention discloses a preparation method and application of a visible light catalytic coated fabric. The method selects chlorine-rich chloroprene rubber as a binder, first coats it on the surface of the fabric, and then sprays photocatalyst titanium dioxide onto the surface of the fabric. The surface of the fabric is coated with an adhesive to stabilize the photocatalyst on the surface of the fabric. As an adhesive, neoprene rubber can not only stably fix titanium dioxide on the surface of the fabric, but also dechlorinate the neoprene rubber. At the same time, chloride ions can modify titanium dioxide, and part of the chloride ions can be stably adsorbed on the surface of titanium dioxide, which significantly changes the surface charge of titanium dioxide. It promotes the negative charge on the surface of titanium dioxide, and has better adsorption to cationic dyes and thus has better degradation performance. Part of the chlorine will enter the titania lattice to replace the lattice oxygen, causing titania to generate oxygen defects, reducing the titania band gap and enhancing titania's absorption of visible light, thereby improving the visible light catalytic degradation performance of titania.

Description

一种光催化涂层织物的制备方法及其应用A kind of preparation method and application of photocatalytic coating fabric

技术领域technical field

本发明属于功能织物制备及表面改性领域,涉及功能织物表面改性负载光催化剂的制备方法,该涂层织物应用于光催化降解印染废水及水体中其他污染物。The invention belongs to the field of functional fabric preparation and surface modification, and relates to a preparation method of a functional fabric surface modified and supported photocatalyst. The coated fabric is used for photocatalytic degradation of printing and dyeing wastewater and other pollutants in water bodies.

背景技术Background technique

随着现代社会工业的迅速发展,环境污染的问题是变得越来越严重。各种水体污染,如来自工厂有机染料,在合成涂料、塑料、制革、纺织过程等产生的废水等。尤其是含有芳香族分子结构的染料一般都是有很好的光稳定性和热稳定性。这些染料废水如果不能得到有效处理,将严重破坏生态环境、甚至威胁人类身体健康。因此,从废水中有效去除染料非常重要。处理含染料废水的方法很多,目前主要有吸附,絮凝,电解、生物降解和光催化降解方法。其中吸附法可以很好的将染料从废水中移除,但是并不能从根本上解决染料对环境的危害。因为吸附只是将染料与废水分离,并不是将染料分解为对环境无害的物质。With the rapid development of modern social industry, the problem of environmental pollution is becoming more and more serious. Various water pollution, such as organic dyes from factories, wastewater from synthetic coatings, plastics, tanning, textile processes, etc. In particular, dyes containing aromatic molecular structures generally have good photostability and thermal stability. If these dye wastewater cannot be effectively treated, it will seriously damage the ecological environment and even threaten human health. Therefore, the efficient removal of dyes from wastewater is very important. There are many methods for treating dye-containing wastewater, and currently there are adsorption, flocculation, electrolysis, biodegradation and photocatalytic degradation. Among them, the adsorption method can remove dyes from wastewater very well, but it cannot fundamentally solve the harm of dyes to the environment. Because adsorption only separates dyes from wastewater, it does not decompose dyes into environmentally friendly substances.

光催化降解污染物技术是近来发展的一种有效的处理污染物的手段,它利用紫外光甚至是太阳光作为能源,激发半导体催化剂产生强氧化性自由基,可以成功的降解水中的大多数有机物。它运行成本低,是一种高效节能技术,具有良好的应用前景。TiO2光催化剂目前已广泛使用,它有着高化学稳定性、无毒无害、低成本、高活性等优点。但是它存在着禁带较宽、量子产率较低、对污染物吸附能力弱、固体粉末颗粒小易团聚等缺点。另外TiO2光催化不吸收可见光且在降解污染物完成后,纳米光催化剂无法回收利用,限制了它们在真实水处理系统中的适用性。因此,通过改性TiO2提高TiO2对可见光的吸收并将TiO2光催化剂固体载体上面上实现催化剂的回收利用至关重要。纺织面料织物作为支撑可以增加纳米光催化剂的可用性,可以提高催化剂与污染物接触面积,且纺织面料织物具有耐久性。此外,纳米光催化剂的改性可以增加催化剂对染料的吸附。Photocatalytic pollutant degradation technology is a recently developed effective means of treating pollutants. It uses ultraviolet light or even sunlight as an energy source to stimulate semiconductor catalysts to generate strong oxidative free radicals, which can successfully degrade most organic compounds in water. . It has low operating cost, is a high-efficiency energy-saving technology, and has good application prospects. TiO2 photocatalyst has been widely used at present, it has the advantages of high chemical stability, non-toxic and harmless, low cost, high activity and so on. However, it has shortcomings such as wide band gap, low quantum yield, weak adsorption capacity for pollutants, small solid powder particles and easy agglomeration. In addition, TiO2 photocatalysis does not absorb visible light and after the degradation of pollutants is completed, the nanophotocatalysts cannot be recycled, limiting their applicability in real water treatment systems. Therefore, it is very important to improve the absorption of visible light by TiO2 by modifying TiO2 and to realize the recycling of the catalyst on the solid support of TiO2 photocatalyst. The textile fabric as a support can increase the availability of nano-photocatalysts, which can improve the contact area between the catalyst and pollutants, and the textile fabric has durability. In addition, the modification of nanophotocatalysts can increase the adsorption of dyes by the catalysts.

研究设计者在棉材料上固化TiO2和Fe-C-TiO2光催化剂,用硅酸钠与纳米光催化剂混合然后涂覆在棉织物上面。然后是功能化的棉质材料插入流动光催化反应器内进行苯酚分解(Hazard.Mater.151(2008)62-64)。这种方法有一定的缺陷,光催化剂与粘合剂混合后,表面覆盖着硅酸钠粘合剂,吸收光效果差,且硅酸钠粘合力不是很强在织物表面易脱落从而降低了光催化活性。The study designers cured TiO2 and Fe-C- TiO2 photocatalysts on cotton materials, mixed sodium silicate with nanophotocatalysts and then coated them on cotton fabrics. Then the functionalized cotton material was inserted into a flow photocatalytic reactor for phenol decomposition (Hazard. Mater. 151 (2008) 62-64). This method has certain defects. After the photocatalyst is mixed with the binder, the surface is covered with sodium silicate binder, which has poor light absorption effect, and the sodium silicate adhesion is not very strong. photocatalytic activity.

田兴友等通过逐层自组装技术在棉织物上构建易回收的TiO2/海藻酸钾-CNTs光催化剂涂层。模拟太阳光照射下纳米涂层对甲醛和罗丹明B(RhB)表现出优异的催化性能(Xingyou Tian.et.al.Cellulose(2017)24:4569–4580)但自组装方法比较复杂,不适宜大规模生产制备。本发明选用粘结强度高、稳定性好、耐酸耐碱富含氯的氯丁橡胶作为粘合剂,通过简单涂覆在织物表面,喷涂二氧化钛悬浮液的方式将二氧化钛分散负载到织物表面,同时实现氯对二氧化钛的改性,提高二氧化钛光催化效果。该方法操作简便,成本低可进行规模生产光催化涂层织物,在印染废水降解领域有很好的应用。Tian Xingyou et al. constructed an easily recyclable TiO2 /potassium alginate-CNTs photocatalyst coating on cotton fabrics through a layer-by-layer self-assembly technique. Nanocoatings exhibit excellent catalytic performance for formaldehyde and rhodamine B (RhB) under simulated sunlight irradiation (Xingyou Tian.et.al.Cellulose (2017) 24:4569–4580), but the self-assembly method is complicated and unsuitable Mass production preparation. The present invention selects chloroprene rubber with high bonding strength, good stability, acid and alkali resistance, and chlorine-rich as the adhesive, and disperses and loads the titanium dioxide on the surface of the fabric by simply coating the surface of the fabric and spraying the titanium dioxide suspension. The modification of titanium dioxide by chlorine is realized, and the photocatalytic effect of titanium dioxide is improved. The method is easy to operate, low in cost, and can be used for large-scale production of photocatalytic coated fabrics, and has a good application in the field of printing and dyeing wastewater degradation.

发明内容SUMMARY OF THE INVENTION

本发明的目的是提供一种光催化涂层织物的制备方法,该涂层织物应用于光催化降解印染废水及水体中其他污染物。The purpose of the present invention is to provide a preparation method of a photocatalytic coated fabric, which is used for photocatalytic degradation of printing and dyeing wastewater and other pollutants in water bodies.

本发明选用富含氯元素的氯丁橡胶为粘合剂,先将其涂覆在织物表面,再将光催化剂二氧化钛喷涂到涂覆有粘合剂的织物表面,使光催化剂稳定于织物表面,该氯丁橡胶粘合剂还对二氧化钛具有改性作用,使二氧化钛对染料的降解性能增强。The present invention selects chlorine-rich chloroprene rubber as the adhesive, first coats it on the surface of the fabric, and then sprays the photocatalyst titanium dioxide on the surface of the fabric coated with the adhesive to stabilize the photocatalyst on the surface of the fabric, The neoprene adhesive also has a modification effect on titanium dioxide, so that the degradation performance of titanium dioxide on dyes is enhanced.

上述光催化涂层织物的制备方法,具体制备步骤如下:The preparation method of above-mentioned photocatalytic coating fabric, concrete preparation steps are as follows:

A.将乙醇和丙酮按1:1的比例加入到容器中并混合均匀得到混合溶液,将所选的织物根据使用需要裁剪成合适的尺寸浸泡在上述混合溶液中,超声60-100min清洗织物,再将织物于60-80℃烘干;所述的织物为厚2-4mm、多孔、表面积为10-30m2/g的质材,其中有氟美斯、亚克滤料、珊瑚绒、双面绒等。A. Add ethanol and acetone into the container at a ratio of 1:1 and mix them evenly to obtain a mixed solution. Cut the selected fabric into a suitable size according to the needs of use, soak it in the above mixed solution, and ultrasonically clean the fabric for 60-100min. Then dry the fabric at 60-80 ° C; the fabric is a material with a thickness of 2-4mm, porous, and a surface area of 10-30m 2 /g, including flumes, acrylic filter material, coral fleece, double Velvet, etc.

B.将二氧化钛加入无水乙醇中,搅拌10-30min再超声1-3h使二氧化钛在乙醇中完全分散得到二氧化钛悬浮液,其中二氧化钛的浓度为2.5-10g/L。所述的二氧化钛为型号为P25的商业二氧化钛(简称P25),其晶型为锐钛矿型与金红石型比例为4:1组成的混合晶型。B. Add titanium dioxide into absolute ethanol, stir for 10-30min and then ultrasonicate for 1-3h to completely disperse titanium dioxide in ethanol to obtain a titanium dioxide suspension, wherein the concentration of titanium dioxide is 2.5-10g/L. The titanium dioxide is commercial titanium dioxide with a model of P25 (P25 for short), and its crystal form is a mixed crystal form consisting of anatase type and rutile type in a ratio of 4:1.

C.将氯丁橡胶溶于二甲苯中搅拌直至完全溶解,其中氯丁橡胶浓度为80-280g/L,然后将其均匀的涂覆在步骤A所述的织物的双面。C. Dissolve the neoprene in xylene and stir until it is completely dissolved, wherein the neoprene concentration is 80-280 g/L, and then evenly coat it on both sides of the fabric described in step A.

D.将步骤B的二氧化钛悬浮液加入高压喷枪中,摇匀,在步骤C织物表面氯丁橡胶未干之前均匀地喷涂在织物两面,将其于50-90℃烘干或室温晾干,即得到双面负载二氧化钛的涂层织物;在室温下陈化96-168h得到光催化涂层织物。D. Add the titanium dioxide suspension of step B into the high-pressure spray gun, shake well, spray evenly on both sides of the fabric before the neoprene rubber on the surface of the fabric in step C is dry, and dry it at 50-90 ° C or dry it at room temperature, i.e. The double-sided titanium dioxide-supported coated fabric was obtained; the photocatalytic coated fabric was obtained by aging at room temperature for 96-168 h.

本发明通过喷涂的方法在织物上负载纳米光催化剂二氧化钛,选用氯丁橡胶作为粘合剂,能够将二氧化钛稳定分散固定到织物表面,通过长时间陈化二氧化钛能促使氯丁橡胶部分微弱老化脱氯。而氯离子能够稳定吸附在二氧化钛表面,显著改变二氧化钛表面带电性,使得在不同pH范围内涂层织物表面的二氧化钛表面带负电荷(图2的zeta电位表征已经证明了这一点),从而使光催化涂层织物对阳离子染料有更好吸附性能,吸附在二氧化钛表面染料会产生自敏化降解,所以光催化涂层织物对阳离子染料有更优的降解效果。此外,部分氯能掺杂到二氧化钛的晶格,取代了晶格氧(图4XPS表征已经证明了这一点),由于氯原子半径大于氧,能使二氧化钛产生缺陷,这些缺陷可能促进二氧化钛表面电子-空穴对的分离,同时减小二氧化钛带隙,增强二氧化钛对可见光的吸收(图3UV-vis表征已经证明了这一点)从而增强了可见光下涂层织物对染料的降解性能。In the present invention, nanometer photocatalyst titanium dioxide is loaded on the fabric by spraying, and chloroprene rubber is used as the adhesive, so that the titanium dioxide can be stably dispersed and fixed on the surface of the fabric, and the chloroprene rubber can be partially aged and dechlorinated by aging titanium dioxide for a long time. . However, chloride ions can be stably adsorbed on the surface of TiO2, which significantly changes the surface charge of TiO2, making the surface of TiO2 on the surface of coated fabrics negatively charged in different pH ranges (this has been proved by the zeta potential characterization in Figure 2), thereby making the surface of TiO2 negatively charged. The catalytic coated fabric has better adsorption performance for cationic dyes, and the dyes adsorbed on the surface of titanium dioxide will cause self-sensitized degradation, so the photocatalytic coated fabric has better degradation effect on cationic dyes. In addition, part of the chlorine can be doped into the lattice of TiO2, displacing the lattice oxygen (this has been proved by the XPS characterization in Figure 4), since the atomic radius of chlorine is larger than that of oxygen, it can cause defects in TiO2, and these defects may promote the electron- The separation of hole pairs, while reducing the bandgap of TiO2, enhances the absorption of visible light by TiO2 (this has been demonstrated by UV-vis characterization in Figure 3), thereby enhancing the degradation performance of the coated fabrics to dyes under visible light.

图1是实例1光催化涂层织物扫描电镜图,由图可知二氧化钛稳定分散在织物表面,在织物表面形成纳米涂层。Fig. 1 is a scanning electron microscope image of the photocatalytic coated fabric of Example 1. It can be seen from the figure that titanium dioxide is stably dispersed on the surface of the fabric, and a nano-coating is formed on the surface of the fabric.

图2是从实例1的光催化涂层织物获取的Cl-TiO2粉末(通过碾碎、超声、洗涤、过滤获取)与P25粉末的Zeta电位图,由图可知Cl-TiO2在整个pH范围内均为负值,说明氯离子吸附在二氧化钛表面能显著改变二氧化钛表面带电性,促使二氧化钛表面带负电荷。Fig. 2 is the Zeta potential diagram of Cl-TiO 2 powder obtained from the photocatalytic coated fabric of Example 1 (obtained by grinding, ultrasonication, washing, filtration) and P25 powder, it can be seen from the figure that Cl-TiO 2 is in the whole pH range Both are negative values, indicating that the adsorption of chloride ions on the surface of titanium dioxide can significantly change the chargeability of the surface of titanium dioxide and promote the negative charge on the surface of titanium dioxide.

图3是实例1的光催化涂层织物与未涂覆氯丁橡胶的二氧化钛涂层织物的UV-vis图,由图可知光催化涂层织物对大于400nm的可见光吸收强度明显高于二氧化钛涂层织物。Fig. 3 is the UV-vis image of the photocatalytic coated fabric of Example 1 and the titanium dioxide coated fabric without neoprene coating, it can be seen from the figure that the visible light absorption intensity of the photocatalytic coated fabric greater than 400 nm is significantly higher than that of the titanium dioxide coating fabric.

图4是从实例1的光催化涂层织物获取的Cl-TiO2粉末的XPS谱图,其中a是Cl-TiO2的XPS全谱图,b是Cl元素XPS谱图。由图a知Cl-TiO2中含有C、O、Ti、Cl四种元素。由图b知存在三种形式的Cl,位于197.9eV低结合能主要归因于化学吸附在二氧化钛表面的氯离子,位于约200.0eV结合能可能是掺杂入TiO2晶格的阴离子Cl的峰值,通过取代TiO2晶格中的氧,可能形成的Ti-Cl-Ti键。而位于201.7eV的高结合能可能是粘合在TiO2表面氯丁橡胶中的氯。4 is the XPS spectrum of Cl-TiO 2 powder obtained from the photocatalytic coated fabric of Example 1, wherein a is the XPS full spectrum of Cl-TiO 2 , and b is the Cl element XPS spectrum. It can be seen from Figure a that Cl-TiO 2 contains four elements of C, O, Ti, and Cl. It can be seen from Figure b that there are three forms of Cl, the low binding energy at 197.9 eV is mainly attributed to the chemisorption of chloride ions on the surface of TiO, and the binding energy at about 200.0 eV may be the peak of anionic Cl doped into the TiO lattice , by displacing oxygen in the TiO lattice, possibly forming Ti-Cl-Ti bonds. And the high binding energy at 201.7 eV might be the chlorine bound in the neoprene on the TiO surface.

图5是实例1光催化涂层织物可见光下多次降解染料罗丹明B曲线图,由图可知光催化涂层织物多次使用后降解罗丹明B效果没有降低,具有很好循环使用性能。Figure 5 is a graph of the photocatalytic coating fabric of Example 1 that degrades the dye Rhodamine B multiple times under visible light. It can be seen from the figure that the photocatalytic coating fabric has no reduction in the effect of degrading Rhodamine B after multiple uses, and has good recycling performance.

本发明的有益效果:Beneficial effects of the present invention:

(1)本发明提供的光催化织物制备方法过程简单,条件温和,室温下进行,无需后续煅烧过程,显著节能降耗,适合于规模化处理和生产。(1) The preparation method of the photocatalytic fabric provided by the present invention is simple in process, mild in conditions, carried out at room temperature, does not require a subsequent calcination process, significantly saves energy and reduces consumption, and is suitable for large-scale treatment and production.

(2)制备的光催化织物涂层对水体中染料的光降解性能良好,适合对工业生产和环境中的染料污染物进行光降解处理,且可以很好的实现催化剂的回收利用,节约处理成本,有良好的商业应用前景。.(2) The prepared photocatalytic fabric coating has good photodegradation performance of dyes in water, is suitable for photodegradation treatment of dye pollutants in industrial production and environment, and can well realize the recycling of catalysts and save the treatment cost. , has good commercial application prospects. .

附图说明Description of drawings

图1是实例1光催化涂层织物电镜(SEM)图;Fig. 1 is the electron microscope (SEM) figure of example 1 photocatalytic coating fabric;

图2是实例1从实例1的光催化涂层织物获取的Cl-TiO2粉末与P25粉末的Zeta电位图;Fig. 2 is the Zeta potential diagram of Cl-TiO 2 powder and P25 powder obtained from the photocatalytic coated fabric of Example 1 in Example 1;

图3是实例1与对比例得到的织物的UV-vis图;Fig. 3 is the UV-vis figure of the fabric obtained in Example 1 and Comparative Example;

图4是从实例1的光催化涂层织物获取的Cl-TiO2粉末的XPS谱图,a为Cl-TiO2XPS全谱图,b为Cl XPS谱图;Fig. 4 is the XPS spectrum of Cl-TiO 2 powder obtained from the photocatalytic coated fabric of Example 1, a is the Cl-TiO 2 XPS full spectrum, and b is the Cl XPS spectrum;

图5是实例1光催化涂层织物可见光下循环降解染料罗丹明B图;Fig. 5 is the photocatalytic coating fabric of example 1 photocatalytic coating fabric under visible light cycle degradation dye rhodamine B figure;

具体实施方式Detailed ways

实施例1:Example 1:

A.选取氟美斯织物,剪取20cm*20cm的织物,量取100ml的乙醇和100ml的丙酮混合加入到400ml的烧杯中,将织物折叠放入浸泡在溶液中,超声60min清洗织物,随后将织物放入烘箱80℃干燥120min,待混合液完全蒸发取出织物。A. Select the fluoromex fabric, cut the fabric of 20cm*20cm, measure 100ml of ethanol and 100ml of acetone and mix it into a 400ml beaker, fold the fabric and soak it in the solution, ultrasonically clean the fabric for 60min, and then put The fabric was placed in an oven at 80°C for drying for 120 min, and the fabric was taken out after the mixture was completely evaporated.

B.量取100ml的无水乙醇加入200ml的烧杯中,准确称取1.0g的商业二氧化钛加入到无水乙醇中搅拌10min然后超声1h,使得二氧化钛在乙醇中分散完全即得二氧化钛悬浮液。B. Measure 100ml of absolute ethanol into a 200ml beaker, accurately weigh 1.0g of commercial titanium dioxide, add it to absolute ethanol, stir for 10min and then ultrasonicate for 1h, so that titanium dioxide is completely dispersed in ethanol to obtain a titanium dioxide suspension.

C.称取10g氯丁橡胶溶于60ml二甲苯中搅拌12h待氯丁橡胶完全溶解后呈粘稠状,均匀涂覆在织物的两面。C. Weigh 10g of neoprene and dissolve it in 60ml of xylene and stir for 12h. After the neoprene is completely dissolved, it will be viscous and evenly coated on both sides of the fabric.

D.将二氧化钛悬浮液体加入高压喷枪中,摇匀,接通真空泵。在步骤C所述的织物表面氯丁橡胶未干前均匀喷涂在织物表面,即得双面负载二氧化钛的涂层织物。将涂层织物置于烘箱80℃干燥2h,随后将其在室温下陈化108h即得光催化涂层织物。D. Add the titanium dioxide suspension liquid to the high-pressure spray gun, shake well, and connect the vacuum pump. The neoprene rubber on the surface of the fabric described in step C is evenly sprayed on the surface of the fabric before it is dry, so as to obtain a coated fabric loaded with titanium dioxide on both sides. The coated fabric was dried in an oven at 80°C for 2 h, and then aged at room temperature for 108 h to obtain a photocatalytic coated fabric.

性能评价:分别在两个烧杯中配制100ml浓度为10mg/L的染料溶液,将阳离子染料罗丹明B和阴离子甲基橙两种染料分别加入到烧杯中,再剪取两块5cm*5cm的光催化涂层织物放入两个烧杯,磁力搅拌吸附30min,取样一次,然后用功率300W的氙灯(波长λ>420nm)模拟太阳光照射(光强度100mW/cm2),并每隔10min取样测定染料的吸光度并计算降解率。Performance evaluation: Prepare 100ml of dye solution with a concentration of 10mg/L in two beakers respectively, add cationic dye Rhodamine B and anionic methyl orange to the beakers respectively, and then cut two pieces of 5cm*5cm light. The catalytic coated fabric is put into two beakers, magnetic stirring is adsorbed for 30min, sampled once, and then irradiated with a xenon lamp with a power of 300W (wavelength λ>420nm) to simulate sunlight (light intensity 100mW/cm 2 ), and the dye is determined by sampling every 10min absorbance and calculate the degradation rate.

具体取样步骤为:用移液管从烧杯中取出3ml溶液,用日本岛津UV-2501PC紫外吸收分光光度计测定各时段所取样品中染料溶液的吸光度,测量在染料最大吸收波长处的原溶液及反应后溶液的吸光度值A0和At,利用At/A0=Ct/Co=η计算光催化涂层织物对染料的降解程度。结果见表1。The specific sampling steps are: take out 3ml of the solution from the beaker with a pipette, measure the absorbance of the dye solution in the samples taken at each time period with a Shimadzu UV-2501PC ultraviolet absorption spectrophotometer, and measure the original solution at the maximum absorption wavelength of the dye. and the absorbance values A 0 and At of the solution after the reaction, and calculate the degradation degree of the dye by the photocatalytic coated fabric using At/A 0 =Ct/C o =η. The results are shown in Table 1.

测试完后用乙醇和去离子水洗涤光催化涂层织物后放置烘箱中80℃干燥5h待涂层织物烘干后取出室温冷却,继续重复上述可见光降解罗丹明B实验,重复8次。结果见图5,光催化涂层织物降解染料罗丹明B效果没有明显下降,说明了其有很好的循环使用性能。After the test, the photocatalytic coated fabric was washed with ethanol and deionized water, and then placed in an oven at 80 °C for drying for 5 h. After the coated fabric was dried, it was taken out to cool at room temperature, and the above experiment of visible light degradation of rhodamine B was repeated 8 times. The results are shown in Figure 5. The photocatalytic coating fabric did not have a significant decrease in the effect of degrading the dye Rhodamine B, indicating that it has a good recycling performance.

实施例2:Example 2:

A.选取亚克滤料织物,剪取20cm*20cm的织物,量取100ml的乙醇和100ml的丙酮混合加入到400ml的烧杯中,将织物折叠放入浸泡在溶液中,超声60min清洗织物,随后将织物放入烘箱80℃干燥120min,待混合液完全蒸发取出织物。A. Select the acrylic filter fabric, cut the fabric of 20cm*20cm, measure 100ml of ethanol and 100ml of acetone and mix it into a 400ml beaker, fold the fabric and soak it in the solution, ultrasonically clean the fabric for 60min, then Put the fabric in an oven at 80°C to dry for 120 min, and take out the fabric after the mixed liquid is completely evaporated.

B.量取100ml的无水乙醇加入200ml的烧杯中,准确称取0.8g的商业二氧化钛加入到无水乙醇中搅拌10min然后超声1h,使得二氧化钛在乙醇中分散完全即得二氧化钛悬浮液。B. Measure 100ml of absolute ethanol into a 200ml beaker, accurately weigh 0.8g of commercial titanium dioxide, add it to absolute ethanol, stir for 10min and then ultrasonicate for 1h, so that titanium dioxide is completely dispersed in ethanol to obtain a titanium dioxide suspension.

C.称取12.5g氯丁橡胶溶于60ml二甲苯中搅拌12h待氯丁橡胶完全溶解后呈粘稠状,均匀涂覆在织物的两面。C. Weigh 12.5g of neoprene and dissolve it in 60ml of xylene and stir for 12h. After the neoprene is completely dissolved, it will be viscous and evenly coated on both sides of the fabric.

D.将二氧化钛悬浮液体加入高压喷枪中,摇匀,通上真空泵。待步骤C所述的织物表面氯丁橡胶未干立即均匀喷涂在织物表面即得双面负载二氧化钛的涂层织物,将涂层织物置于烘箱80℃干燥2h,随后将涂层织物在室温下陈化108h即得光催化涂层织物。D. Add the titanium dioxide suspension liquid into the high-pressure spray gun, shake well, and connect to the vacuum pump. After the chloroprene rubber on the fabric surface described in step C was evenly sprayed on the surface of the fabric immediately before it was dry, a coated fabric with titanium dioxide on both sides was obtained. After aging for 108h, the photocatalytic coated fabric was obtained.

同实施例1的方法对两种染料溶液的降解进行性能评价,结果见表1。The degradation of the two dye solutions was evaluated in the same manner as in Example 1, and the results are shown in Table 1.

实施例3:Example 3:

A.选取珊瑚绒织物,剪取20cm*20cm的织物,量取100ml的乙醇和100ml的丙酮混合加入到400ml的烧杯中,将织物折叠放入浸泡在溶液中,超声60min清洗织物,随后将织物放入烘箱80℃干燥120min,待混合液完全蒸发取出织物。A. Select coral fleece fabric, cut 20cm*20cm fabric, measure 100ml of ethanol and 100ml of acetone and mix it into a 400ml beaker, fold the fabric and soak it in the solution, ultrasonically clean the fabric for 60min, then the fabric Put it in an oven at 80°C to dry for 120min, and take out the fabric after the mixture is completely evaporated.

B.量取100ml的无水乙醇加入200ml的烧杯中,准确称取1.5g的商业二氧化钛加入到无水乙醇中搅拌10min然后超声1h,使得二氧化钛在乙醇中分散完全即得二氧化钛悬浮液。B. Measure 100ml of absolute ethanol into a 200ml beaker, accurately weigh 1.5g of commercial titanium dioxide, add it to absolute ethanol, stir for 10min and then ultrasonicate for 1h, so that titanium dioxide is completely dispersed in ethanol to obtain a titanium dioxide suspension.

C.称取7.5g氯丁橡胶溶于60ml二甲苯中搅拌12h待氯丁橡胶完全溶解后呈粘稠状,均匀涂覆在织物的表面。C. Weigh 7.5g of neoprene and dissolve it in 60ml of xylene and stir for 12h. After the neoprene is completely dissolved, it will be viscous and evenly coated on the surface of the fabric.

D.将二氧化钛悬浮液体加入高压喷枪中,摇匀,通上真空泵。待步骤C所述的织物表面氯丁橡胶未干立即均匀喷涂在织物表面即得双面负载二氧化钛的涂层织物。将涂层织物至于烘箱80℃干燥2h,随后将涂层织物在室温下陈化108h即得光催化涂层织物。D. Add the titanium dioxide suspension liquid into the high-pressure spray gun, shake well, and connect to the vacuum pump. The chloroprene rubber on the surface of the fabric described in step C is immediately and evenly sprayed on the surface of the fabric to obtain a coated fabric loaded with titanium dioxide on both sides. The coated fabric was dried in an oven at 80°C for 2 h, and then the coated fabric was aged at room temperature for 108 h to obtain a photocatalytic coated fabric.

同实施例1的方法对两种染料溶液的降解进行性能评价,结果见表1。The degradation of the two dye solutions was evaluated in the same manner as in Example 1, and the results are shown in Table 1.

实施例4:Example 4:

A.选取双面绒织物,剪取20cm*20cm的织物,量取100ml的乙醇和100ml的丙酮混合加入到400ml的烧杯中,将织物折叠放入浸泡在溶液中,超声60min清洗织物,随后将织物放入烘箱80℃干燥120min,待混合液完全蒸发取出织物。A. Select the double-sided fleece fabric, cut the fabric of 20cm*20cm, measure 100ml of ethanol and 100ml of acetone and mix it into a 400ml beaker, fold the fabric and soak it in the solution, ultrasonically clean the fabric for 60min, and then put The fabric was placed in an oven at 80°C for drying for 120 min, and the fabric was taken out after the mixture was completely evaporated.

B.量取100ml的无水乙醇加入200ml的烧杯中,准确称取1.2g的商业二氧化钛(P25)加入到无水乙醇中搅拌10min然后超声1h,使得二氧化钛在乙醇中分散完全即得二氧化钛悬浮液。B. Measure 100ml of absolute ethanol and add it to a 200ml beaker, accurately weigh 1.2g of commercial titanium dioxide (P25), add it to absolute ethanol, stir for 10min and then ultrasonicate for 1h, so that titanium dioxide is completely dispersed in ethanol to obtain a titanium dioxide suspension .

C.称取15g氯丁橡胶溶于60ml二甲苯中搅拌12h待氯丁橡胶完全溶解后呈粘稠状,均匀涂覆在织物的表面。C. Weigh 15g of neoprene and dissolve it in 60ml of xylene and stir for 12h. After the neoprene is completely dissolved, it will be viscous and evenly coated on the surface of the fabric.

D.将二氧化钛悬浮液体加入高压喷枪中,摇匀,通上真空泵。待步骤C所述的织物表面氯丁橡胶未干立即均匀喷涂在织物表面即得双面负载二氧化钛的涂层织物。将涂层织物置于烘箱80℃干燥2h,随后将涂层织物在室温下陈化108h即得光催化涂层织物。D. Add the titanium dioxide suspension liquid into the high-pressure spray gun, shake well, and connect to the vacuum pump. The chloroprene rubber on the surface of the fabric described in step C is immediately and evenly sprayed on the surface of the fabric to obtain a coated fabric loaded with titanium dioxide on both sides. The coated fabric was dried in an oven at 80°C for 2 h, and then the coated fabric was aged at room temperature for 108 h to obtain a photocatalytic coated fabric.

同实施例1的方法对两种染料溶液的降解进行性能评价,结果见表1。The degradation of the two dye solutions was evaluated in the same manner as in Example 1, and the results are shown in Table 1.

对比例Comparative ratio

按照实施例1的方法,只是去掉步骤C的操作,得到未涂覆氯丁橡胶的P25织物。According to the method of Example 1, except that the operation of step C is removed, a P25 fabric without neoprene coating is obtained.

同实施例1的方法对两种染料溶液的降解进行性能评价,结果见表1。The degradation of the two dye solutions was evaluated in the same manner as in Example 1, and the results are shown in Table 1.

表1.光催化织物降解染料性能测定表Table 1. Determination of the performance of photocatalytic fabrics to degrade dyes

Claims (2)

1. a kind of preparation method of photocatalysis coating fabric, specific preparation process is as follows:
A. ethyl alcohol and acetone are added in container in the ratio of 1:1 and are uniformly mixed and obtain mixed solution, by selected fabric Be cut into according to the needs of use it is suitably sized be immersed in above-mentioned mixed solution, ultrasonic 60-100min cleans fabric, then will knit Object is dried in 60-80 DEG C;The fabric be fluorine beauty this, one of sub- gram filtrate, coral fleece, double-sided plush;
B. titanium dioxide is added to absolute ethanol, ultrasound 1-3h divides titanium dioxide completely in ethanol to stirring 10-30min again It dissipates and obtains tio_2 suspension, wherein the concentration of titanium dioxide is 2.5-10g/L;
The titanium dioxide is the commercial titanium dioxide of model P25, and crystal form is Detitanium-ore-type and rutile-type ratio is The mixing crystal form of 4:1 composition;
C. neoprene is dissolved in stirring in dimethylbenzene until being completely dissolved, wherein neoprene concentration is 80-280g/L, by it It is uniform to be coated in the two-sided of fabric described in step A;
D. the tio_2 suspension of step B is added in high-pressure spray gun, is shaken up, it is not dry in step C fabric surface neoprene It is equably sprayed on fabric two-face before, it is dried in 50-90 DEG C of drying or room temperature to get two-sided carried titanium dioxide is arrived Coated fabric;Ageing 96-168h obtains photocatalysis coating fabric at room temperature.
2. a kind of application of photocatalysis coating fabric described in claim 1, which prints and dyes applied to photocatalytic degradation Other pollutants in waste water and water body.
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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114308123A (en) * 2021-12-29 2022-04-12 中欧电子材料国际创新中心(合肥)有限公司 Photocatalytic coating material and preparation method thereof

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