CN102489290A - Preparation method of nano bismuth vanadate photocatalyst loaded on active carbon fiber - Google Patents
Preparation method of nano bismuth vanadate photocatalyst loaded on active carbon fiber Download PDFInfo
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Abstract
本发明涉及一种活性碳纤维负载纳米钒酸铋光催化剂的制备方法,包括:(1)将铋盐、稳定剂加入到磷酸盐缓冲液中,搅拌形成悬浊液;将偏钒酸盐溶于磷酸盐缓冲液中,然后加入到上述悬浊液中,搅拌均匀,形成透明溶液;(2)用碱性溶液调节上述透明溶液的pH值为6.0~8.0,然后在40~100℃下加入活性碳纤维,搅拌至混合均匀后离心、过滤、洗涤,再放入马弗炉中焙烧,最后经冷却研磨,即得。本发明制备方法简单易行,对设备的要求低,可操作性好;本发明制备的活性碳纤维粉体钒酸铋负载均匀,能够在紫外光和可见光条件下高效降解持久性有毒有害物质,利用简便且可回收再生。The invention relates to a preparation method of activated carbon fiber loaded nano bismuth vanadate photocatalyst, comprising: (1) adding bismuth salt and stabilizer to phosphate buffer, stirring to form a suspension; dissolving metavanadate in Phosphate buffer, then added to the above suspension, stirred evenly to form a transparent solution; (2) Adjust the pH of the above transparent solution to 6.0-8.0 with an alkaline solution, and then add the active Carbon fiber, stirred until evenly mixed, then centrifuged, filtered, washed, then put into a muffle furnace for roasting, and finally cooled and ground to obtain the product. The preparation method of the present invention is simple and easy, has low requirements on equipment, and has good operability; the activated carbon fiber powder bismuth vanadate prepared by the present invention is evenly loaded, and can efficiently degrade persistent toxic and harmful substances under the conditions of ultraviolet light and visible light. Simple and recyclable.
Description
技术领域 technical field
本发明属于纳米钒酸铋光催化剂的制备领域,特别涉及一种活性碳纤维负载纳米钒酸铋光催化剂的制备方法。The invention belongs to the field of preparation of nano bismuth vanadate photocatalyst, in particular to a preparation method of activated carbon fiber loaded nano bismuth vanadate photocatalyst.
背景技术 Background technique
近年来,以二氧化钛(TiO2)为核心代表的光催化技术在环境污染治理领域,特别是在难生物降解废水处理和空气净化中的应用越来越广泛,但由于其带隙较宽,仅能够在紫外光照射下才具有光催化作用,从而限制了其应用领域的进一步扩大。为了能够提高TiO2对太阳光的利用效率,国内外很多专家学者围绕着可见光响应的TiO2光催化剂展开了大量的研究工作,主要针对TiO2光催化剂表面结构改性、无机元素和金属元素掺杂改性等,旨在扩大其光谱响应范围,提高其可见光催化活性。尽管如此,经过改性的TiO2光催化剂在目前阶段仍然存在着可见光催化活性不理想,光降解能力较差等问题,导致其实用性较差。In recent years, the photocatalytic technology represented by titanium dioxide (TiO 2 ) has been widely used in the field of environmental pollution control, especially in the treatment of refractory biodegradable wastewater and air purification. However, due to its wide band gap, only It can only have photocatalysis under the irradiation of ultraviolet light, which limits the further expansion of its application field. In order to improve the utilization efficiency of TiO 2 to sunlight, many experts and scholars at home and abroad have carried out a lot of research work on TiO 2 photocatalysts responding to visible light. Hybrid modification, etc., aiming to expand its spectral response range and improve its visible light catalytic activity. Nevertheless, the modified TiO2 photocatalysts still have problems such as unsatisfactory visible light catalytic activity and poor photodegradation ability at the current stage, which lead to their poor practicability.
最近的研究发现,具有单斜晶系白钨矿结构的复合氧化物钒酸铋(BiVO4)在可见光照射下就具有光催化活性,能够分解水分子产氧和降解有机污染物,是一种潜在的光催化剂。然而,BiVO4的吸附性能很差,而且产生的光生载流子难以迁移,容易复合,从而影响了其可见光活性。目前关于针对BiVO4的复合改性和掺杂的研究报道较少,另外关于将其负载于吸附性能好的多孔材料,如活性炭等的报道也不多,因此,如何增强其在可见光范围内的吸收,以及提高其可见光催化活性,是目前研究开发BiVO4高效光催化剂的主要研究重点。Recent studies have found that bismuth vanadate (BiVO 4 ), a compound oxide with a monoclinic scheelite structure, has photocatalytic activity under visible light irradiation, and can decompose water molecules to produce oxygen and degrade organic pollutants. potential photocatalyst. However, the adsorption performance of BiVO 4 is poor, and the generated photogenerated carriers are difficult to migrate and easy to recombine, which affects its visible light activity. At present, there are few research reports on the compound modification and doping of BiVO 4 , and there are not many reports on loading it on porous materials with good adsorption properties, such as activated carbon. Therefore, how to enhance its performance in the visible light range Absorption, as well as improving its catalytic activity under visible light, are the main research focuses in the current research and development of BiVO4 high-efficiency photocatalysts.
污水处理常规方法主要有:物理分离法、生物降解法、化学分解法等,但这些方法都存在一定的局限性,因此,研究人员开始致力于开发高效、低能耗、适用范围广和有深度氧化能力的水净化技术。近年来,很多学者将TiO2用于光催化降解水体中的有机污染物,虽然取得了一定的效果,但由于其光响应范围的限制,导致处理效果往往不够理想。The conventional methods of sewage treatment mainly include: physical separation method, biodegradation method, chemical decomposition method, etc., but these methods have certain limitations. Therefore, researchers have begun to work on the development of high efficiency, low energy consumption, wide application range and deep oxidation Capable water purification technology. In recent years, many scholars have used TiO 2 for photocatalytic degradation of organic pollutants in water bodies. Although some effects have been achieved, the treatment effect is often not ideal due to the limitation of its photoresponse range.
发明内容 Contents of the invention
本发明所要解决的技术问题是提供一种活性碳纤维负载纳米钒酸铋光催化剂的制备方法,该方法操作简单易行,对设备的要求低,制备的活性碳纤维钒酸铋负载均匀,能够在紫外光和可见光条件下高效降解持久性有毒有害物质。The technical problem to be solved by the present invention is to provide a preparation method of activated carbon fiber-loaded nano-bismuth vanadate photocatalyst. The method is simple and easy to operate, and has low requirements on equipment. Efficiently degrade persistent toxic and harmful substances under light and visible light conditions.
本发明的一种活性碳纤维负载纳米钒酸铋光催化剂的制备方法,包括:A kind of preparation method of activated carbon fiber loaded nano-bismuth vanadate photocatalyst of the present invention comprises:
(1)将铋盐、稳定剂加入到磷酸盐缓冲液中,搅拌形成悬浊液;将偏钒酸盐溶于磷酸盐缓冲液中,然后加入到上述悬浊液中,搅拌均匀,形成透明溶液;其中铋盐和偏钒酸盐的物质的量浓度均为0.05~0.25mol/L,稳定剂的物质的量浓度为0.01~0.05mol/L;(1) Add bismuth salt and stabilizer to phosphate buffer, stir to form a suspension; dissolve metavanadate in phosphate buffer, then add to the above suspension, stir evenly, and form a transparent Solution; wherein the molar concentration of bismuth salt and metavanadate is 0.05-0.25 mol/L, and the molar concentration of stabilizer is 0.01-0.05 mol/L;
(2)用碱性溶液调节上述透明溶液的pH值为6.0~8.0,然后在40~100℃下加入活性碳纤维,搅拌至混合均匀后离心、过滤、洗涤,再放入马弗炉中,在250~400℃下焙烧3~6h,最后经冷却研磨,即得;其中加入的活性碳纤维与铋盐的质量比为2~10∶1。(2) Adjust the pH value of the above-mentioned transparent solution to 6.0 to 8.0 with an alkaline solution, then add activated carbon fiber at 40 to 100 ° C, stir until evenly mixed, then centrifuge, filter, and wash, then put it in a muffle furnace, Calcined at 250-400°C for 3-6 hours, and finally cooled and ground to obtain the product; the mass ratio of activated carbon fiber to bismuth salt is 2-10:1.
步骤(1)中所述的搅拌形成悬浊液中的搅拌时间为30~60min。The stirring time in the step (1) to form the suspension by stirring is 30 to 60 minutes.
步骤(1)中所述的铋盐为硝酸铋、氯化铋或醋酸铋。The bismuth salt described in step (1) is bismuth nitrate, bismuth chloride or bismuth acetate.
步骤(1)中所述的稳定剂为葡萄糖酸钠、乙二胺四乙酸二钠或丁烷四羧酸。The stabilizer described in step (1) is sodium gluconate, disodium edetate or butane tetracarboxylic acid.
步骤(1)中所述的偏钒酸盐为偏钒酸钠、偏钒酸钾或偏钒酸铵。The metavanadate described in step (1) is sodium metavanadate, potassium metavanadate or ammonium metavanadate.
步骤(1)中所述的铋盐和偏钒酸盐的摩尔比为1∶1。The molar ratio of bismuth salt and metavanadate described in step (1) is 1:1.
步骤(1)中所述的磷酸盐缓冲液由物质的量浓度为0.05mol/L的磷酸二氢钾和0.035mol/L的氢氧化钠组成。The phosphate buffer solution described in the step (1) is composed of potassium dihydrogen phosphate and 0.035mol/L sodium hydroxide with a substance concentration of 0.05mol/L.
步骤(2)中所述的碱性溶液为浓度1.0mol/L~3.0mol/L的氢氧化钠或氢氧化钾水溶液。The alkaline solution described in step (2) is an aqueous solution of sodium hydroxide or potassium hydroxide with a concentration of 1.0 mol/L-3.0 mol/L.
活性碳纤维本身是一种性能良好的吸附剂,具有比表面积大和吸附能力强等特点,在水处理应用中还能够同时达到吸附去除重金属离子等无机污染物的有益效果。本发明利用活性碳纤维独特的层状中空结构特征、比表面积大、吸附能力强等特点,结合BiVO4的可见光催化活性,成功的将纳米BiVO4负载到活性碳纤维上,制备成具有高催化活性可见光响应的光催化材料,并且将其应用于生物难降解废水的深度处理,可以实现对水中有机污染物的高效去除,特别是对常规处理难以有效去除的持久性微污染物,而且无二次污染问题。Activated carbon fiber itself is a kind of adsorbent with good performance. It has the characteristics of large specific surface area and strong adsorption capacity. It can also achieve the beneficial effect of adsorbing and removing inorganic pollutants such as heavy metal ions in water treatment applications. The present invention utilizes the characteristics of the unique layered hollow structure, large specific surface area, and strong adsorption capacity of activated carbon fibers, and combines the visible light catalytic activity of BiVO 4 to successfully load nano-BiVO 4 onto activated carbon fibers to prepare a visible light active carbon fiber with high catalytic activity. Responsive photocatalytic materials, and applying them to the advanced treatment of biologically refractory wastewater, can achieve efficient removal of organic pollutants in water, especially for persistent micro-pollutants that are difficult to effectively remove by conventional treatment, and without secondary pollution question.
有益效果Beneficial effect
(1)本发明制备方法简单易行,对设备的要求低,可操作性好;(1) The preparation method of the present invention is simple and easy, has low requirements on equipment, and has good operability;
(2)本发明制备的活性碳纤维粉体钒酸铋负载均匀,能够在紫外光和可见光条件下高效降解持久性有毒有害物质,利用简便且可回收再生。(2) The activated carbon fiber powder prepared by the invention is evenly loaded with bismuth vanadate, can efficiently degrade persistent toxic and harmful substances under the conditions of ultraviolet light and visible light, and is easy to use and recyclable.
具体实施方式 Detailed ways
下面结合具体实施例,进一步阐述本发明。应理解,这些实施例仅用于说明本发明而不用于限制本发明的范围。此外应理解,在阅读了本发明讲授的内容之后,本领域技术人员可以对本发明作各种改动或修改,这些等价形式同样落于本申请所附权利要求书所限定的范围。Below in conjunction with specific embodiment, further illustrate the present invention. It should be understood that these examples are only used to illustrate the present invention and are not intended to limit the scope of the present invention. In addition, it should be understood that after reading the teachings of the present invention, those skilled in the art can make various changes or modifications to the present invention, and these equivalent forms also fall within the scope defined by the appended claims of the present application.
实施例1Example 1
(1)将硝酸铋、乙二胺四乙酸二钠加入到磷酸盐缓冲液中,磁力搅拌30min,形成悬浊液;将偏钒酸钠先均匀溶于磷酸盐缓冲液,然后逐滴加入到上述悬浊液中,不断磁力搅拌均匀,形成透明溶液;其中硝酸铋和偏矾酸钠的物质的量浓度均为0.05mol/L,乙二胺四乙酸二钠物质的量浓度为0.01mol/L,磷酸盐缓冲液由物质的量浓度为0.05mol/L的磷酸二氢钾和0.035mol/L的氢氧化钠组成;(1) Add bismuth nitrate and disodium edetate into the phosphate buffer, and stir magnetically for 30 minutes to form a suspension; dissolve sodium metavanadate evenly in the phosphate buffer, and then add it dropwise to the In the above-mentioned suspension, the constant magnetic stirring is uniform to form a transparent solution; wherein the molar concentration of bismuth nitrate and sodium metavanate is 0.05mol/L, and the molar concentration of disodium edetate is 0.01mol/L. L, phosphate buffer saline is made up of potassium dihydrogen phosphate and 0.035mol/L sodium hydroxide that the concentration of substance is 0.05mol/L;
(2)采用浓度为1.0mol/L的氢氧化钠溶液调节上述透明溶液的pH值为6.0,然后在40℃下加入活性碳纤维,硝酸铋与活性碳纤维的质量比为1∶2,连续磁力搅拌混合,离心、过滤,洗涤后,放入马弗炉,在250℃下焙烧3h,经冷却研磨后,即得负载了纳米钒酸铋的活性碳纤维光催化剂粉体。(2) Adopt the sodium hydroxide solution that concentration is 1.0mol/L to adjust the pH value of above-mentioned transparent solution to be 6.0, then add activated carbon fiber at 40 ℃, the mass ratio of bismuth nitrate and activated carbon fiber is 1: 2, continuous magnetic stirring Mix, centrifuge, filter, wash, put into muffle furnace, bake at 250°C for 3 hours, cool and grind, and then get activated carbon fiber photocatalyst powder loaded with nano-bismuth vanadate.
实施例2Example 2
(1)将醋酸铋、丁烷四羧酸加入到磷酸盐缓冲液中,磁力搅拌45min,形成悬浊液;将偏钒酸钾先均匀溶于磷酸盐缓冲液,然后逐滴加入到上述悬浊液中,不断磁力搅拌均匀,形成透明溶液;其中醋酸铋和偏钒酸钾物质的量浓度均为0.15mol/L,丁烷四羧酸物质的量浓度为0.025mol/L,磷酸盐缓冲液由物质的量浓度为0.05mol/L的磷酸二氢钾和0.035mol/L的氢氧化钠组成;(1) Add bismuth acetate and butane tetracarboxylic acid into the phosphate buffer, and stir magnetically for 45 minutes to form a suspension; dissolve potassium metavanadate evenly in the phosphate buffer, and then add it dropwise to the above suspension In the turbid liquid, the magnetic stirring is continued to form a transparent solution; the concentration of bismuth acetate and potassium metavanadate is 0.15mol/L, the concentration of butane tetracarboxylic acid is 0.025mol/L, and the concentration of phosphate buffer The liquid is composed of potassium dihydrogen phosphate with a concentration of 0.05mol/L and sodium hydroxide with a concentration of 0.035mol/L;
(2)采用浓度为2.0mol/L的氢氧化钠水溶液调节上述透明溶液的pH值为7.0,然后在70℃下加入活性碳纤维,醋酸铋与活性碳纤维的质量比为1∶5,连续磁力搅拌混合,离心、过滤,洗涤后,放入马弗炉,在320℃下焙烧5h,经冷却研磨后,即得负载了纳米钒酸铋的活性碳纤维光催化剂粉体。(2) The pH value of the above-mentioned transparent solution is adjusted to 7.0 by using a sodium hydroxide aqueous solution with a concentration of 2.0mol/L, and then adding activated carbon fibers at 70°C, the mass ratio of bismuth acetate to activated carbon fibers is 1: 5, and the magnetic stirring is continued Mix, centrifuge, filter, wash, put into muffle furnace, bake at 320°C for 5h, cool and grind, then get activated carbon fiber photocatalyst powder loaded with nano-bismuth vanadate.
实施例3Example 3
(1)将氯化铋、葡萄糖酸钠加入到磷酸盐缓冲液中,磁力搅拌60min,形成悬浊液;将偏钒酸铵先均匀溶于磷酸盐缓冲液,然后逐滴加入到上述悬浊液中,不断磁力搅拌均匀,形成透明溶液;其中氯化铋和偏钒酸铵物质的量浓度均为0.25mol/L,葡萄糖酸钠物质的量浓度为0.05mol/L,磷酸盐缓冲液由物质的量浓度为0.05mol/L的磷酸二氢钾和0.035mol/L的氢氧化钠组成;(1) Add bismuth chloride and sodium gluconate to the phosphate buffer, stir magnetically for 60 minutes to form a suspension; dissolve ammonium metavanadate evenly in the phosphate buffer, and then add it dropwise to the above suspension In the solution, the magnetic force is constantly stirred to form a transparent solution; wherein the molar concentration of bismuth chloride and ammonium metavanadate is 0.25mol/L, the molar concentration of sodium gluconate is 0.05mol/L, and the phosphate buffer is composed of The concentration of the substance is composed of potassium dihydrogen phosphate of 0.05mol/L and sodium hydroxide of 0.035mol/L;
(2)采用浓度为3.0mol/L的氢氧化钾水溶液调节上述透明溶液的pH值为8.0,然后在100℃下加入活性碳纤维,氯化铋和活性碳纤维的质量比为1∶10,连续磁力搅拌混合,离心、过滤,洗涤后,放入马弗炉,在400℃下焙烧6h,经冷却研磨后,即得负载了纳米钒酸铋的活性碳纤维光催化剂粉体。(2) Use potassium hydroxide aqueous solution with a concentration of 3.0mol/L to adjust the pH value of the above-mentioned transparent solution to 8.0, then add activated carbon fiber at 100°C, the mass ratio of bismuth chloride and activated carbon fiber is 1: 10, continuous magnetic force Stir and mix, centrifuge, filter, wash, put into a muffle furnace, bake at 400°C for 6 hours, cool and grind, and then get activated carbon fiber photocatalyst powder loaded with nano-bismuth vanadate.
实施例4Example 4
废水处理实验:以某印染厂最终排放的混合印染废水为处理对象,经过微滤膜过滤预处理后,在其中分别加入相同量通过实施例1~例3所制得的光催化剂,连续在太阳光下照射4h,对印染废水的脱色率和CODCr去除率分别如下表所示:Wastewater treatment experiment: take the mixed printing and dyeing wastewater finally discharged from a printing and dyeing factory as the treatment object, after pretreatment by microfiltration membrane filtration, add the same amount of photocatalysts prepared in Examples 1 to 3, and continuously After 4 hours of light irradiation, the decolorization rate and COD Cr removal rate of printing and dyeing wastewater are shown in the following table:
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Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1683074A (en) * | 2005-03-11 | 2005-10-19 | 南京大学 | Preparation method of visible light-responsive photocatalytic thin film layer |
CN101791548A (en) * | 2010-04-22 | 2010-08-04 | 华中科技大学 | Visible light catalyst BiVO4 and preparation method thereof |
WO2011048128A2 (en) * | 2009-10-22 | 2011-04-28 | Basf Se | Photocatalyst having increased daylight activity |
CN102125832A (en) * | 2011-01-19 | 2011-07-20 | 南京理工大学 | Visible light responsive pucherite-graphene composite photocatalyst and preparation method thereof |
-
2011
- 2011-11-11 CN CN2011103583342A patent/CN102489290A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1683074A (en) * | 2005-03-11 | 2005-10-19 | 南京大学 | Preparation method of visible light-responsive photocatalytic thin film layer |
WO2011048128A2 (en) * | 2009-10-22 | 2011-04-28 | Basf Se | Photocatalyst having increased daylight activity |
CN101791548A (en) * | 2010-04-22 | 2010-08-04 | 华中科技大学 | Visible light catalyst BiVO4 and preparation method thereof |
CN102125832A (en) * | 2011-01-19 | 2011-07-20 | 南京理工大学 | Visible light responsive pucherite-graphene composite photocatalyst and preparation method thereof |
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CN103623805A (en) * | 2013-07-17 | 2014-03-12 | 上海市环境科学研究院 | Activated carbon fiber-loaded composite oxide based on NaBiO3 and its preparation method and method for using it to degrade organic dye wastewater |
CN103623805B (en) * | 2013-07-17 | 2015-12-09 | 上海市环境科学研究院 | Activated carbon fiber-loaded composite oxide based on NaBiO3 and its preparation method and method for using it to degrade organic dye wastewater |
CN103736480A (en) * | 2013-12-24 | 2014-04-23 | 桂林电子科技大学 | Quadrangle starlike pucherite for optical catalytic materials as well as preparation method thereof |
CN103736480B (en) * | 2013-12-24 | 2016-06-08 | 桂林电子科技大学 | A kind of corner star pucherite as catalysis material and preparation method thereof |
CN103920508A (en) * | 2014-03-28 | 2014-07-16 | 山东大学 | Nitrated carbon fiber loaded bismuth oxyhalide nanoflower and preparation method of nanoflower |
CN104475100A (en) * | 2014-12-25 | 2015-04-01 | 东华大学 | Preparation method of carbon nano tube composite bismuth molybdate environmentally friendly and deep water treatment agent |
CN104475100B (en) * | 2014-12-25 | 2016-11-16 | 东华大学 | A preparation method of carbon nanotube composite bismuth molybdate green deep water treatment agent |
CN106732805A (en) * | 2016-12-02 | 2017-05-31 | 东华大学 | A kind of fiber/CNT/BiVO4 three-dimensional recyclable efficient catalytic material and its preparation and application |
CN107413326A (en) * | 2017-05-03 | 2017-12-01 | 东北大学 | A kind of carbon fiber supported liquid membrane burning prepares high activity CQDs/BiVO4The method of composite Nano catalysis material |
CN112221483A (en) * | 2020-10-27 | 2021-01-15 | 上海市环境科学研究院 | Modularized supported bismuth vanadate photocatalytic material and preparation method and application thereof |
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