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CN109999809A - A kind of preparation method and applications of the compound bead of ferriferous oxide biomass carbon fiber pDA-PVDF light Fenton - Google Patents

A kind of preparation method and applications of the compound bead of ferriferous oxide biomass carbon fiber pDA-PVDF light Fenton Download PDF

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CN109999809A
CN109999809A CN201910180636.1A CN201910180636A CN109999809A CN 109999809 A CN109999809 A CN 109999809A CN 201910180636 A CN201910180636 A CN 201910180636A CN 109999809 A CN109999809 A CN 109999809A
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李彬榕
孟敏佳
吴春笃
崔颜华
郑健
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Abstract

本发明属于材料制备及环境污染治理的技术领域,提供了一种铁氧化物@生物质碳纤维@pDA‑PVDF光芬顿复合珠粒的制备方法,制备方法如下:步骤1、制备铁氧化物@生物质碳纤维复合光芬顿催化剂;步骤2、制备pDA‑PVDF粉末;步骤3、基于相转化技术、多巴胺自聚合技术制备光芬顿复合珠粒。本发明利用pDA‑PVDF珠粒作为光芬顿催化剂的载体,既能固定粉体催化剂,有利于实际应用,又能有效抑制铁离子的流失,提高催化体系稳定性。该方法具有合成简单,降解效率高等优点。

The invention belongs to the technical field of material preparation and environmental pollution control, and provides a preparation method of iron oxide@biomass carbon fiber@pDA-PVDF optical Fenton composite beads. The preparation method is as follows: Step 1, preparing iron oxide@ Biomass carbon fiber composite photo-Fenton catalyst; step 2, preparing pDA-PVDF powder; step 3, preparing photo-Fenton composite beads based on phase inversion technology and dopamine self-polymerization technology. The invention uses pDA-PVDF beads as the carrier of the photo-Fenton catalyst, which can not only fix the powder catalyst, which is beneficial to practical application, but also effectively suppress the loss of iron ions and improve the stability of the catalytic system. This method has the advantages of simple synthesis and high degradation efficiency.

Description

一种铁氧化物@生物质碳纤维@pDA-PVDF光芬顿复合珠粒的制 备方法及其应用Preparation of an iron oxide@biomass carbon fiber@pDA-PVDF photo-Fenton composite beads preparation method and its application

技术领域technical field

本发明属于材料制备及环境污染治理的技术领域,涉及一种高效降解甲基橙的铁氧化物@生物质碳纤维@pDA-PVDF光芬顿复合珠粒的制备方法及用途。The invention belongs to the technical field of material preparation and environmental pollution control, and relates to a preparation method and use of iron oxide@biomass carbon fiber@pDA-PVDF optical Fenton composite beads for efficiently degrading methyl orange.

背景技术Background technique

偶氮染料是指含有一个或以上偶氮基(-N=N-),并连接有至少一个芳香结构的染料。偶氮染料具有颜色多样、工艺简单、生产成本低、染色能力强的特点,因此被广泛应用于纺织品的染色,纸张、皮革、塑料等产品的着色,而且在食品、化妆品中也有应用。偶氮染料虽然应用广泛,但是部分偶氮染料经还原裂解,会产生24种致癌的芳香胺化合物,如被人体吸收,会严重威胁人体的健康。尤其在用于纺织品、服装和皮革等制品中,这些染料与人体长期接触,可通过呼吸道、食道及皮肤黏膜进入人体,随着体内的新陈代谢,特定条件下会还原分解出致癌的芳香胺。因此,高效降解水体中残留的偶氮染料具有重要意义。Azo dyes refer to dyes that contain one or more azo groups (-N=N-) and are linked with at least one aromatic structure. Azo dyes have the characteristics of various colors, simple process, low production cost and strong dyeing ability, so they are widely used in the dyeing of textiles, the coloring of paper, leather, plastics and other products, and also in food and cosmetics. Although azo dyes are widely used, some azo dyes will produce 24 kinds of carcinogenic aromatic amine compounds after reductive cracking. If absorbed by the human body, it will seriously threaten human health. Especially in textiles, clothing and leather products, these dyes are in contact with the human body for a long time and can enter the human body through the respiratory tract, esophagus and skin mucous membranes. Therefore, it is of great significance to efficiently degrade residual azo dyes in water.

高级氧化工艺(AOPs)的特点是产生具有强氧化作用的羟基自由基(·OH),能够将这些有机污染物降解为低毒或无毒的小分子。非均相光芬顿工艺是一种有前途的、可代替均相芬顿试剂的水处理策略。然而,在非均相光芬顿反应过程中存在两个巨大的挑战:(i)粉末状的光芬顿催化剂在实际应用中较难回收,操作困难;(ii)由于操作中活性金属的严重流失,催化剂的稳定性差。Advanced oxidation processes (AOPs) are characterized by the generation of hydroxyl radicals ( OH) with strong oxidizing effects, which can degrade these organic pollutants into low- or non-toxic small molecules. The heterogeneous photo-Fenton process is a promising water treatment strategy as an alternative to homogeneous Fenton reagents. However, there are two great challenges in the process of heterogeneous photo-Fenton reaction: (i) powdered photo-Fenton catalysts are difficult to recover in practical applications and difficult to operate; (ii) due to the seriousness of active metals in operation loss, the stability of the catalyst is poor.

发明内容SUMMARY OF THE INVENTION

针对现有技术存在的问题,本发明利用简便的相转化技术构建的聚合物珠粒能够轻松、有效的固定光芬顿催化剂,同时珠粒内部的多级孔结构不会阻碍有机污染物的扩散。此外,聚多巴胺(pDA)是一种多功能的表面工程涂层,几乎可以应用于任何材料的表面,不会影响聚合物珠的固有结构。由于邻苯二酚基团丰富,具有较强的金属离子配位能力,pDA层可以抑制铁离子的损失。而且,聚多巴胺可作为促进电子传递的介质,从而提高光芬顿反应的光催化性能。In view of the problems existing in the prior art, the polymer beads constructed by the simple phase inversion technology of the present invention can easily and effectively fix the photo-Fenton catalyst, and at the same time, the hierarchical porous structure inside the beads will not hinder the diffusion of organic pollutants . Furthermore, polydopamine (pDA) is a versatile surface engineering coating that can be applied to the surface of almost any material without affecting the inherent structure of the polymer beads. Due to the abundant catechol groups and strong coordination ability of metal ions, the pDA layer can suppress the loss of iron ions. Moreover, polydopamine can act as a mediator to facilitate electron transfer, thereby enhancing the photocatalytic performance of the photo-Fenton reaction.

本发明将铸膜液逐滴滴入凝固浴中制备光芬顿复合珠粒。所得珠粒直径为3mm左右,相较于分体光芬顿催化剂更易于回收利用和实际水样的连续处理。在光芬顿体系中,聚多巴胺、生物制炭以及铁氧化物中的单质铁均能促进Fe3+/Fe2+的循环,从而提高催化性能。此外,聚多巴胺修饰的PVDF起到一种“屏障”作用,能够有效抑制铁例子的流失,提升光芬顿复合珠粒的稳定性。本发明为光芬顿粉体催化剂的扩大化应用提供了一种普遍适用的新方法,在一定程度上能够实现实际环境废水的有效降解。In the present invention, the film casting liquid is dropped dropwise into the solidification bath to prepare the optical Fenton composite beads. The diameter of the obtained beads is about 3 mm, which is easier for recycling and continuous treatment of actual water samples than the split photo-Fenton catalyst. In the photo-Fenton system, polydopamine, biochar, and elemental iron in iron oxides can promote the Fe 3+ /Fe 2+ cycle, thereby improving the catalytic performance. In addition, the polydopamine-modified PVDF acts as a "barrier", which can effectively inhibit the loss of iron samples and improve the stability of the photo-Fenton composite beads. The invention provides a universally applicable new method for the enlarged application of the photo-Fenton powder catalyst, and can achieve effective degradation of actual environmental wastewater to a certain extent.

一种铁氧化物@生物质碳纤维@pDA-PVDF光芬顿复合珠粒的制备方法,步骤如下:A preparation method of iron oxide@biomass carbon fiber@pDA-PVDF optical Fenton composite beads, the steps are as follows:

步骤1、铁氧化物@生物质碳纤维的制备:Step 1. Preparation of iron oxide@biomass carbon fiber:

取野生蒲绒洗净烘干,称取一定量的蒲绒于坩埚中,然后转移至管式炉,于一定温度、氮气气氛下煅烧一定时间,待自然冷却后取出,得到生物质碳纤维(Carbon fiber,CF);Take wild velvet, wash and dry, weigh a certain amount of velvet in a crucible, then transfer to a tube furnace, calcine for a certain period of time at a certain temperature and a nitrogen atmosphere, and take out after natural cooling to obtain biomass carbon fibers (Carbon fiber, CF);

取一定量CF分散在水中,然后在上述分散液中加入一定量的FeSO4·7H2O并振荡一定时间,烘干后,将所得固体转移至管式炉,于一定温度、氮气气氛下第二次煅烧一定时间,待自然冷却后取出,得到铁氧化物@生物质碳纤维(Fe-based oxide@Carbon fiber,FCF),用研钵将其研磨至粉末,备用。Take a certain amount of CF and disperse it in water, then add a certain amount of FeSO 4 ·7H 2 O to the above dispersion liquid and shake it for a certain period of time, after drying, transfer the obtained solid to a tube furnace, and at a certain temperature and under a nitrogen atmosphere for the first time. After secondary calcination for a certain period of time, it was taken out after natural cooling to obtain Fe-based oxide@Carbon fiber (FCF), which was ground into powder with a mortar for use.

步骤2、制备pDA-PVDF粉末;Step 2, prepare pDA-PVDF powder;

按比例将多巴胺(DA)和聚偏二氟乙烯(PVDF)分散在Tris-HCl缓冲溶液中,再加入一定量的乙醇,然后调节pH=8.5,随后在室温下剧烈搅拌,最后过滤得到pDA-PVDF粉末并烘干;Dopamine (DA) and polyvinylidene fluoride (PVDF) were dispersed in Tris-HCl buffer solution in proportion, and then a certain amount of ethanol was added, and then adjusted to pH=8.5, followed by vigorous stirring at room temperature, and finally filtered to obtain pDA- PVDF powder and drying;

步骤3、制备铁氧化物@生物质碳纤维@pDA-PVDF光芬顿复合珠粒:Step 3. Preparation of iron oxide@biomass carbon fiber@pDA-PVDF photo-Fenton composite beads:

按比例将步骤1制备的FCF粉末、步骤2制备的pDA-PVDF粉末和N-甲基吡咯烷酮(NMP)混合,随后于一定温度下机械搅拌得到珠粒铸造液A,最后将珠粒铸造液A逐滴滴入去离子水中,并多次更换去离子水,保证NMP溶剂完全置换到水中,形成FCF@pDA-PVDF光芬顿复合珠粒,备用。The FCF powder prepared in step 1, the pDA-PVDF powder prepared in step 2, and N-methylpyrrolidone (NMP) were mixed in proportion, and then mechanically stirred at a certain temperature to obtain a bead casting solution A. Finally, the bead casting solution A was mixed Drop by drop into deionized water, and replace the deionized water several times to ensure that the NMP solvent is completely replaced into the water to form FCF@pDA-PVDF photo-Fenton composite beads, which are ready for use.

步骤1中,所述蒲绒煅烧温度为800~850℃,煅烧时间为3~5h,管式炉的升温速率为5℃/min;所述CF和FeSO4·7H2O的比例为0.3g:1~3mmol;所述振荡时间为12h;所述第二次煅烧温度为550~850℃,煅烧时间为3~5h,升温速率为5℃/min;In step 1, the calcination temperature of the velvet is 800-850°C, the calcination time is 3-5h, and the heating rate of the tube furnace is 5°C/min; the ratio of the CF to FeSO 4 ·7H 2 O is 0.3g : 1~3mmol; the shaking time is 12h; the second calcination temperature is 550~850℃, the calcination time is 3~5h, and the heating rate is 5℃/min;

步骤2中,所述DA和PVDF的质量比为1:10,所述Tris-HCl缓冲溶液中多巴胺的浓度为2mg/mL;Tris-HCl缓冲溶液和乙醇的体积比为30:1;所述剧烈搅拌时间为6h;转速为500~800r/min;In step 2, the mass ratio of DA and PVDF is 1:10, the concentration of dopamine in the Tris-HCl buffer solution is 2 mg/mL; the volume ratio of Tris-HCl buffer solution and ethanol is 30:1; the The vigorous stirring time is 6h; the rotating speed is 500~800r/min;

步骤3中,所述珠粒铸造液A中的FCF粉末、pDA-PVDF粉末和NMP的质量比为0.05~0.15g:2g:17.85~17.95g;所述机械搅拌温度为50℃,搅拌时间为4~6h。In step 3, the mass ratio of FCF powder, pDA-PVDF powder and NMP in the bead casting solution A is 0.05-0.15g: 2g: 17.85-17.95g; the mechanical stirring temperature is 50°C, and the stirring time is 4 to 6 hours.

上述的技术方案中所述的NMP,其作用为溶剂,溶解PVDF以制备珠粒铸造液A。The NMP described in the above technical scheme acts as a solvent to dissolve PVDF to prepare a bead casting solution A.

上述的技术方案中所述的PVDF,其作用为基质。The PVDF described in the above technical solutions acts as a matrix.

上述的技术方案中所述的去离子水,其作用为非溶剂。The deionized water described in the above-mentioned technical scheme acts as a non-solvent.

将本发明制备的铁氧化物@生物质碳纤维@pDA-PVDF光芬顿复合珠粒用作光催化降解甲基橙。The iron oxide@biomass carbon fiber@pDA-PVDF photo-Fenton composite beads prepared by the present invention are used as photocatalytic degradation of methyl orange.

本发明的有益效果为:The beneficial effects of the present invention are:

(1)单质铁和生物制炭的存在能够促进Fe3+/Fe2+的循环,从而产生更多的羟基自由基,提高光催化效率,有效降解有机污染物。(1) The existence of elemental iron and biochar can promote the cycle of Fe 3+ /Fe 2+ , thereby generating more hydroxyl radicals, improving the photocatalytic efficiency, and effectively degrading organic pollutants.

(2)利用pDA改性的PVDF珠粒固定光芬顿催化剂,所得到的复合珠粒很好的解决了分体光芬顿催化剂难于实际应用的问题。此外,聚多巴胺能够有效的抑制铁离子的流失,从而有效提高催化体系的稳定性。整个制备方法简单方便,为芬顿催化体系的扩大化应用提供了新的见解。(2) Using pDA-modified PVDF beads to immobilize the photo-Fenton catalyst, the obtained composite beads can well solve the problem that the split photo-Fenton catalyst is difficult to apply in practice. In addition, polydopamine can effectively inhibit the loss of iron ions, thereby effectively improving the stability of the catalytic system. The whole preparation method is simple and convenient, and provides new insights for the expanded application of Fenton's catalytic system.

附图说明Description of drawings

图1a为制备的复合材料的XRD图(其中CF表示生物质碳纤维,FCF表示铁氧化物@生物质碳纤维,PB表示PVDF珠粒,DPB表示pDA-PVDF珠粒,FPB表示铁氧化物@生物质碳纤维@PVDF珠粒,FDPB表示铁氧化物@生物质碳纤维@pDA-PVDF珠粒),图1b为复合珠粒的实物照片,图1c为珠粒的截面扫描电镜照片;Figure 1a is the XRD pattern of the prepared composites (where CF represents biomass carbon fibers, FCF represents iron oxide@biomass carbon fibers, PB represents PVDF beads, DPB represents pDA-PVDF beads, and FPB represents iron oxide@biomass Carbon fiber@PVDF beads, FDPB represents iron oxide@biomass carbon fiber@pDA-PVDF beads), Figure 1b is the real photo of the composite bead, and Figure 1c is the cross-sectional SEM photo of the bead;

图2a为不同的材料在pH为3的条件下的降解效率曲线,b为FDPB在不同pH条件下的光催化降解效率曲线。Figure 2a shows the degradation efficiency curves of different materials at pH 3, and b shows the photocatalytic degradation efficiency curves of FDPB at different pH conditions.

具体实施方式Detailed ways

下面结合说明书附图和具体实施实例对本发明做进一步说明。The present invention will be further described below with reference to the accompanying drawings and specific implementation examples.

本发明以珠粒铸造液总质量为20g为例。In the present invention, the total mass of the bead casting solution is 20 g as an example.

实施例1:Example 1:

(1)FCF复合光芬顿催化剂的制备(1) Preparation of FCF Composite Photo-Fenton Catalyst

称取干燥的蒲绒于坩埚中,转移至管式炉,于800℃下煅烧3h,升温速率为5℃/min,待自然冷却后取出,得到CF,待用;取0.3g CF和1mmol FeSO4·7H2O分散于35mL去离子水中,室温下振荡12h;烘干后,将得到的固体转移到管式炉,在850℃下煅烧3h,即获得FCF复合光芬顿催化剂。Weigh the dried velvet in a crucible, transfer it to a tube furnace, calcine it at 800 °C for 3 h, the heating rate is 5 °C/min, and take out after natural cooling to obtain CF, which is ready for use; take 0.3 g CF and 1 mmol FeSO 4 ·7H 2 O was dispersed in 35 mL of deionized water, shaken at room temperature for 12 hours; after drying, the obtained solid was transferred to a tube furnace and calcined at 850°C for 3 hours to obtain FCF composite photo-Fenton catalyst.

(2)FCF@pDA-PVDF光芬顿复合珠粒的制备(2) Preparation of FCF@pDA-PVDF Photo-Fenton Composite Beads

首先,取0.6g多巴胺粉末、6g PVDF粉末分散在300mLTris-HCl缓冲溶液中,随后加入10mL乙醇,并调节溶液pH=8.5,将混合液并剧烈搅拌6h完成聚多巴胺在PVDF粉末表面的自聚合,最后过滤、洗涤、烘干得到pDA-PVDF粉末。称取0.05g FCF、2g pDA-PVDF粉末和17.95g NMP溶剂混合在一起,于50℃下搅拌4h,得到珠粒铸造液。随后将铸造液抽入10mL注射器中,并逐滴滴入去离子水中,经过相转化得到复合珠粒。First, 0.6g of dopamine powder and 6g of PVDF powder were dispersed in 300mL of Tris-HCl buffer solution, then 10mL of ethanol was added, and the pH of the solution was adjusted to 8.5, and the mixture was vigorously stirred for 6h to complete the self-polymerization of polydopamine on the surface of PVDF powder. Finally, filter, wash and dry to obtain pDA-PVDF powder. 0.05 g of FCF, 2 g of pDA-PVDF powder and 17.95 g of NMP solvent were weighed and mixed together, and stirred at 50° C. for 4 h to obtain a bead casting solution. Then, the casting solution was drawn into a 10 mL syringe and dropped into deionized water drop by drop to obtain composite beads through phase inversion.

实施例2:Example 2:

保证其他条件不变的情况下,建立对比试验如下:制FCF复合光芬顿催化剂时,取0.3g CF和1mmol FeSO4·7H2O分散于35mL去离子水中,室温下振荡12h;烘干后,将得到的固体转移到管式炉,通过将煅烧温度改变为550℃后煅烧3h,即获得FCF复合光芬顿催化剂。Under the condition of keeping other conditions unchanged, the comparison test was established as follows: when preparing FCF composite photo-Fenton catalyst, 0.3g CF and 1mmol FeSO 4 ·7H 2 O were dispersed in 35mL deionized water, and shaken at room temperature for 12h; after drying , the obtained solid was transferred to a tube furnace, and the FCF composite photo-Fenton catalyst was obtained by changing the calcination temperature to 550 °C and then calcining for 3 h.

实施例3:Example 3:

保证其他条件不变的情况下,建立对比试验如下:制FCF复合光芬顿催化剂时,通过改变CF和FeSO4·7H2O的比例来考察铁氧化物的负载情况,取0.3g CF和3mmol FeSO4·7H2O分散于35mL去离子水中,室温下振荡12h;烘干后,于850℃下煅烧3h,即获得FCF复合光芬顿催化剂。Under the condition of keeping other conditions unchanged, the comparative experiment was established as follows: when preparing FCF composite photo-Fenton catalyst, the loading of iron oxide was investigated by changing the ratio of CF and FeSO 4 ·7H 2 O, taking 0.3 g CF and 3 mmol FeSO 4 ·7H 2 O was dispersed in 35 mL of deionized water, shaken at room temperature for 12 hours; after drying, calcined at 850° C. for 3 hours, the FCF composite photo-Fenton catalyst was obtained.

实施例4:Example 4:

制备光芬顿复合珠粒时(其他条件不变),通过改变FCF的添加量(0.1g,0.15g)来考察芬顿催化剂的最佳添加量,以及添加量对光催化性能的影响。When preparing photo-Fenton composite beads (other conditions remain unchanged), by changing the addition amount of FCF (0.1g, 0.15g), the optimal addition amount of Fenton catalyst and the effect of addition amount on photocatalytic performance were investigated.

从图1中可以看出,复合材料具有多种铁氧化物和生物制碳纤维的特征峰,证明复合材料的成功合成。As can be seen in Figure 1, the composites have characteristic peaks of various iron oxides and bio-made carbon fibers, proving the successful synthesis of the composites.

从图2a中可以看出,所构建的FDPB在60min内几乎完全使甲基橙脱色,具有良好的降解效率,仅次于粉末状FCF;而其他复合材料的降解性能较低。从图2b中可以看出,所构建的FDPB在不同的pH条件下表现出不同的降解效率,其中pH=1.7时降解速率达到最高。As can be seen in Figure 2a, the constructed FDPB almost completely decolorized methyl orange within 60 min, with a good degradation efficiency, second only to that of powdered FCF; while the degradation performance of other composites was lower. It can be seen from Figure 2b that the constructed FDPB exhibited different degradation efficiencies under different pH conditions, and the degradation rate reached the highest at pH=1.7.

所构建的复合光芬顿珠粒对甲基橙的降解效果达到99%以上,并且在6次循环后保持良好的催化性能。The constructed composite photo-Fenton beads had a degradation effect of more than 99% on methyl orange, and maintained good catalytic performance after 6 cycles.

Claims (7)

1. a kind of preparation method of the compound bead of ferriferous oxide biomass carbon fiber pDA-PVDF light Fenton, which is characterized in that Include the following steps:
The preparation of step 1, ferriferous oxide@biomass carbon fiber:
Take wild cattail wool clean drying, weigh a certain amount of cattail wool in crucible, be then transferred to tube furnace, in certain temperature, Certain time is calcined under nitrogen atmosphere, is taken out after natural cooling, biomass carbon fiber CF is obtained;
It takes a certain amount of CF to be dispersed in water, a certain amount of FeSO is then added in above-mentioned dispersion liquid4·7H2O simultaneously vibrates a timing Between, after drying, obtained solid is transferred to tube furnace, second of calcining certain time under certain temperature, nitrogen atmosphere, to certainly It is so taken out after cooling, obtains ferriferous oxide@biomass carbon fiber, FCF is ground to powder with mortar, spare;
Step 2, preparation pDA-PVDF powder;
Dopamine D A and polyvinylidene fluoride PVDF are dispersed in Tris-HCl buffer solution in proportion, added a certain amount of Ethyl alcohol, then adjusts pH, is then vigorously mixed at room temperature for, and pDA-PVDF powder is finally obtained by filtration and dries;
Step 3 prepares the compound bead of ferriferous oxide biomass carbon fiber pDA-PVDF light Fenton;
PDA-PVDF powder and N-Methyl pyrrolidone NMP prepared by FCF powder prepared by step 1, step 2 are mixed in proportion It closes, then mechanical stirring obtains bead casting liquid A under certain temperature, and bead casting liquid A is finally instilled deionized water dropwise In, and deionized water is repeatedly replaced, guarantee that nmp solvent is replaced into water completely, forms FCF@pDA-PVDF light Fenton composite bead Grain, it is spare.
2. the preparation side of the compound bead of ferriferous oxide biomass carbon fiber pDA-PVDF light Fenton according to claim 1 Method, which is characterized in that in step 1, the cattail wool calcination temperature is 800~850 DEG C, and calcination time is 3~5h, the liter of tube furnace Warm rate is 5 DEG C/min.
3. the preparation side of the compound bead of ferriferous oxide biomass carbon fiber pDA-PVDF light Fenton according to claim 1 Method, which is characterized in that in step 1, the CF and FeSO4·7H2The ratio of O is 0.3g:1~3mmol;The duration of oscillation is 12h;Second of calcination temperature is 550~850 DEG C, and calcination time is 3~5h, and heating rate is 5 DEG C/min.
4. the preparation side of the compound bead of ferriferous oxide biomass carbon fiber pDA-PVDF light Fenton according to claim 1 Method, which is characterized in that in step 2, the mass ratio of the DA and PVDF are 1:10, dopamine in the Tris-HCl buffer solution Concentration be 2mg/mL;The volume ratio of Tris-HCl buffer solution and ethyl alcohol is 30:1;PH value is 8.5.
5. the preparation side of the compound bead of ferriferous oxide biomass carbon fiber pDA-PVDF light Fenton according to claim 1 Method, which is characterized in that described to be vigorously stirred the time as 6h in step 2;Revolving speed is 500~800r/min.
6. the preparation side of the compound bead of ferriferous oxide biomass carbon fiber pDA-PVDF light Fenton according to claim 1 Method, which is characterized in that in step 3, the mass ratio of FCF powder, pDA-PVDF powder and NMP in the bead casting liquid A is 0.05~0.15g:2g:17.85~17.95g;The mechanical stirring temperature is 50 DEG C, and mixing time is 4~6h.
7. by ferriferous oxide@biomass carbon fiber@pDA-PVDF made from the described in any item preparation methods of claim 1~7 The compound bead of light Fenton is used for the purposes of photo-catalytic degradation of methyl-orange.
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