CN115739118B - Iron-doped bismuth oxygen sulfur photocatalyst and preparation method and application thereof - Google Patents

Iron-doped bismuth oxygen sulfur photocatalyst and preparation method and application thereof Download PDF

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CN115739118B
CN115739118B CN202211573611.6A CN202211573611A CN115739118B CN 115739118 B CN115739118 B CN 115739118B CN 202211573611 A CN202211573611 A CN 202211573611A CN 115739118 B CN115739118 B CN 115739118B
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photocatalyst
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doped bismuth
oxysulfur
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姜丽莎
刘伟
许子俊
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Guangzhou Dingjian Intellectual Property Service Co ltd
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Yantai University
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Abstract

The invention discloses an iron-doped bismuth-oxygen-sulfur photocatalyst, and a preparation method and application thereof, and belongs to the technical field of new environmental catalytic materials. The invention mainly uses Bi 2 O 2 S crystal and Fe (NO) 3 ) 3 ·9H 2 O is used as a raw material, and an iron-doped bismuth oxygen sulfur photocatalyst is prepared by adopting a high-energy ball milling method; wherein the doping amount of Fe in the Fe-doped bismuth oxide sulfur photocatalyst is 1.7-5.6%. The iron-doped bismuth oxysulfide photocatalyst obtained by the invention has higher photogenerated carrier transmission efficiency, rich reactive sites and stronger capability of activating persulfate.

Description

一种铁掺杂铋氧硫光催化剂及其制备方法与应用An iron-doped bismuth oxysulfur photocatalyst and its preparation method and application

技术领域Technical field

本发明属于环境催化新材料技术领域,具体涉及一种铁掺杂铋氧硫光催化剂及其制备方法与应用。The invention belongs to the technical field of new environmental catalytic materials, and specifically relates to an iron-doped bismuth oxygen-sulfur photocatalyst and its preparation method and application.

背景技术Background technique

世界上大量的抗生素通过家庭、医院、制药公司、废水处理厂以及水产养殖和牲畜养殖场的排放在环境中不断累积,促使水生生态系统中抗生素抗性基因(ARG)和耐抗生素细菌(ARB)的形成,威胁公众健康。四环素(TC)作为一种典型的抗生素,由于其化学稳定性和环境持久性较强,对人类健康和生态系统造成了不良影响。而且四环素的抗菌特性使其难以被传统的生物废水处理技术根除。因此,迫切需要开发经济有效的抗生素废水治理方法。The world's vast quantities of antibiotics are accumulating in the environment through emissions from households, hospitals, pharmaceutical companies, wastewater treatment plants, and aquaculture and livestock farms, driving the emergence of antibiotic resistance genes (ARGs) and antibiotic-resistant bacteria (ARBs) in aquatic ecosystems. formation, threatening public health. Tetracycline (TC), as a typical antibiotic, has adverse effects on human health and ecosystems due to its strong chemical stability and environmental persistence. And the antibacterial properties of tetracyclines make them difficult to eradicate using traditional biological wastewater treatment technologies. Therefore, there is an urgent need to develop cost-effective antibiotic wastewater treatment methods.

近年来,高级氧化技术被广泛用于降解难降解有机污染物,并将其矿化为CO2和H2O。基于羟基自由基(·OH)和硫酸根自由基(SO4 -·)的高级氧化技术是降解常见有机污染物的有效方法,如有机染料、表面活性剂、烃类、酚类、药物活性成分、农药等。然而,基于·OH的高级氧化技术对有机污染物的降解是通过非选择性的多步反应进行的,通常需要酸性环境。基于SO4 -·的高级氧化技术相较于基于·OH的高级氧化技术,反应过程更稳定,限制条件更少且反应速率更快,近年来迅速发展,在污水处理方面有越来越多的应用。In recent years, advanced oxidation technology has been widely used to degrade refractory organic pollutants and mineralize them into CO2 and H2O. Advanced oxidation technology based on hydroxyl radicals (·OH) and sulfate radicals (SO 4 - ·) is an effective method to degrade common organic pollutants, such as organic dyes, surfactants, hydrocarbons, phenols, and pharmaceutical active ingredients. , pesticides, etc. However, the degradation of organic pollutants by ·OH-based advanced oxidation technology proceeds through non-selective multi-step reactions, which usually require an acidic environment. Compared with the advanced oxidation technology based on ·OH, the advanced oxidation technology based on SO 4 - · has a more stable reaction process, fewer restrictive conditions and a faster reaction rate. It has developed rapidly in recent years, and there are more and more applications in sewage treatment. application.

目前,许多金属离子及非均相催化剂被用于基于SO4 -·的高级氧化技术中,尤其非均相光催化剂在光催化活化过硫酸盐降解污染物方面具有较大应用潜力。此外,向光催化剂中掺杂过渡金属可显著提高光催化剂的催化活性,达到高效活化过硫酸盐降解污染物的目的。然而,过渡金属掺杂通常是采用水热法或溶剂热法制备的,此过程时间较长,可能会产生二次污染,且样品无法大批量制备。Currently, many metal ions and heterogeneous catalysts are used in advanced oxidation technologies based on SO 4 - ·. In particular, heterogeneous photocatalysts have great application potential in photocatalytic activation of persulfate to degrade pollutants. In addition, doping transition metals into photocatalysts can significantly improve the catalytic activity of the photocatalyst, achieving the purpose of efficiently activating persulfate to degrade pollutants. However, transition metal doping is usually prepared by hydrothermal or solvothermal methods. This process takes a long time, may cause secondary pollution, and samples cannot be prepared in large quantities.

发明内容Contents of the invention

有鉴于此,本发明提出一种铁掺杂铋氧硫光催化剂及其制备方法与应用,以克服上述现有技术中的不足。In view of this, the present invention proposes an iron-doped bismuth oxysulfur photocatalyst and its preparation method and application to overcome the above-mentioned shortcomings in the prior art.

为实现上述目的,本发明提出如下技术方案:In order to achieve the above objects, the present invention proposes the following technical solutions:

一种铁掺杂铋氧硫光催化剂,以Bi2O2S晶体和Fe(NO3)3·9H2O为原料,采用高能球磨法,制备铁掺杂铋氧硫光催化剂;其中,Fe在铁掺杂铋氧硫光催化剂中的掺杂量为1.7-5.6%。An iron-doped bismuth oxysulfur photocatalyst uses Bi 2 O 2 S crystal and Fe(NO 3 ) 3 ·9H 2 O as raw materials, and uses a high-energy ball milling method to prepare an iron-doped bismuth oxysulfur photocatalyst; wherein, Fe The doping amount in the iron-doped bismuth oxysulfur photocatalyst is 1.7-5.6%.

进一步地,所述Bi2O2S晶体的粒径为为纳米片状结构。Further, the particle size of the Bi 2 O 2 S crystal is a nanosheet structure.

本发明还提供一种铁掺杂铋氧硫光催化剂的制备方法,包括以下步骤:The invention also provides a method for preparing an iron-doped bismuth oxysulfur photocatalyst, which includes the following steps:

以Bi2O2S晶体和Fe(NO3)3·9H2O为原料,采用高能球磨法,制备铁掺杂铋氧硫光催化剂,其中,Bi2O2S晶体和Fe(NO3)3·9H2O的质量比为0.5:(0.0625-0.2142)。Using Bi 2 O 2 S crystal and Fe(NO 3 ) 3 ·9H 2 O as raw materials, an iron-doped bismuth oxysulfur photocatalyst was prepared using high-energy ball milling method, in which Bi 2 O 2 S crystal and Fe(NO 3 ) The mass ratio of 3 ·9H 2 O is 0.5: (0.0625-0.2142).

进一步地,球磨过程中,球磨转运强度为800rpm,球磨时间为20min。Further, during the ball milling process, the ball milling transfer intensity was 800 rpm, and the ball milling time was 20 minutes.

进一步地,球磨后的样品在室温下加入水中搅拌,去除多余的铁盐,再将其干燥。Further, the ball-milled sample was added to water at room temperature and stirred to remove excess iron salt, and then dried.

更进一步地,所述搅拌时间为120min。Furthermore, the stirring time is 120 minutes.

本发明还提供一种铁掺杂铋氧硫光催化剂在光催化活化过硫酸盐处理含有有机物废水中的应用。The invention also provides an application of an iron-doped bismuth oxysulfur photocatalyst in photocatalytically activated persulfate treatment of wastewater containing organic matter.

进一步地,所述有机物为四环素。Further, the organic substance is tetracycline.

与现有技术相比,本发明的有益效果为:Compared with the prior art, the beneficial effects of the present invention are:

1)本发明中铁掺杂铋氧硫光催化剂的制备采用高能球磨法,具有操作相对简单、安全、成本低、可大批量制备等优点;1) The iron-doped bismuth oxysulfur photocatalyst in the present invention is prepared by high-energy ball milling, which has the advantages of relatively simple operation, safety, low cost, and can be prepared in large quantities;

2)所获得的铁掺杂铋氧硫光催化剂具有较高的光生载流子传输效率、丰富的反应活性位点和较强的活化过硫酸盐的能力,原因在于铁掺杂会使铋氧硫光催化剂的能带结构发生变化,并产生新能级,从而可以促进光生载流子的分离;研磨后的铋氧硫光催化剂表面可以暴露更多的反应活性位点,从而有利于过硫酸盐的活化;2) The obtained iron-doped bismuth oxysulfur photocatalyst has high photogenerated carrier transmission efficiency, abundant reaction active sites and strong ability to activate persulfate, because the iron doping will cause the bismuth oxysulfide to The energy band structure of the sulfur photocatalyst changes and creates new energy levels, which can promote the separation of photogenerated carriers; the surface of the ground bismuth oxysulfur photocatalyst can expose more reactive sites, which is beneficial to persulfate activation of salt;

3)所获得的铁掺杂铋氧硫光催化剂展现了优异的光催化活化过硫酸盐降解四环素的活性和稳定性。3) The obtained iron-doped bismuth oxysulfur photocatalyst exhibits excellent photocatalytic activity and stability for persulfate degradation of tetracycline.

附图说明Description of drawings

为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其他的附图。In order to explain the embodiments of the present invention or the technical solutions in the prior art more clearly, the drawings needed to be used in the embodiments will be briefly introduced below. Obviously, the drawings in the following description are only some of the drawings of the present invention. Embodiments, for those of ordinary skill in the art, other drawings can also be obtained based on these drawings without exerting creative efforts.

图1为本发明实施例1-3制备的铁掺杂铋氧硫光催化剂和对照组制备的催化剂的X射线衍射图;Figure 1 is the X-ray diffraction pattern of the iron-doped bismuth oxysulfur photocatalyst prepared in Examples 1-3 of the present invention and the catalyst prepared in the control group;

图2为本发明实施例1-3制备的铁掺杂铋氧硫光催化剂和对照组制备的催化剂光催化活化过硫酸盐降解四环素的效果图;Figure 2 is a diagram showing the effect of photocatalytic activation of persulfate for the degradation of tetracycline by the iron-doped bismuth oxysulfur photocatalyst prepared in Examples 1-3 of the present invention and the catalyst prepared by the control group;

图3为本发明实施例2制备的铁掺杂铋氧硫光催化剂的TEM图;Figure 3 is a TEM image of the iron-doped bismuth oxysulfur photocatalyst prepared in Example 2 of the present invention;

图4为本发明实施例2制备的铁掺杂铋氧硫光催化剂光催化反应前后的XRD图;Figure 4 is an XRD pattern before and after the photocatalytic reaction of the iron-doped bismuth oxysulfur photocatalyst prepared in Example 2 of the present invention;

图5为本发明实施例2、对比例1、对比例2制备的铁掺杂铋氧硫光催化剂光催化活化过硫酸盐降解四环素的效果图。Figure 5 is a diagram showing the effect of photocatalytic activation of persulfate to degrade tetracycline by the iron-doped bismuth oxysulfur photocatalyst prepared in Example 2, Comparative Example 1, and Comparative Example 2 of the present invention.

具体实施方式Detailed ways

现详细说明本发明的多种示例性实施方式,该详细说明不应认为是对本发明的限制,而应理解为是对本发明的某些方面、特性和实施方案的更详细的描述。Various exemplary embodiments of the invention will now be described in detail. This detailed description should not be construed as limitations of the invention, but rather as a more detailed description of certain aspects, features and embodiments of the invention.

应理解本发明中所述的术语仅仅是为描述特别的实施方式,并非用于限制本发明。另外,对于本发明中的数值范围,应理解为还具体公开了该范围的上限和下限之间的每个中间值。在任何陈述值或陈述范围内的中间值以及任何其他陈述值或在所述范围内的中间值之间的每个较小的范围也包括在本发明内。这些较小范围的上限和下限可独立地包括或排除在范围内。It should be understood that the terms used in the present invention are only used to describe particular embodiments and are not intended to limit the present invention. In addition, for numerical ranges in the present invention, it should be understood that every intermediate value between the upper and lower limits of the range is also specifically disclosed. Every smaller range between any stated value or value intermediate within a stated range and any other stated value or value intermediate within a stated range is also included within the invention. The upper and lower limits of these smaller ranges may independently be included or excluded from the range.

除非另有说明,否则本文使用的所有技术和科学术语具有本发明所述领域的常规技术人员通常理解的相同含义。虽然本发明仅描述了优选的方法和材料,但是在本发明的实施或测试中也可以使用与本文所述相似或等同的任何方法和材料。本说明书中提到的所有文献通过引用并入,用以公开和描述与所述文献相关的方法和/或材料。在与任何并入的文献冲突时,以本说明书的内容为准。Unless defined otherwise, all technical and scientific terms used herein have the same meaning as commonly understood by one of ordinary skill in the art to which this invention belongs. Although only the preferred methods and materials are described herein, any methods and materials similar or equivalent to those described herein can be used in the practice or testing of the invention. All documents mentioned in this specification are incorporated by reference to disclose and describe the methods and/or materials in connection with which the documents relate. In the event of conflict with any incorporated document, the contents of this specification shall prevail.

在不背离本发明的范围或精神的情况下,可对本发明说明书的具体实施方式做多种改进和变化,这对本领域技术人员而言是显而易见的。由本发明的说明书得到的其他实施方式对技术人员而言是显而易见的。本申请说明书和实施例仅是示例性的。It will be apparent to those skilled in the art that various modifications and changes can be made to the specific embodiments described herein without departing from the scope or spirit of the invention. Other embodiments will be apparent to the skilled person from the description of the invention. The specification and examples are intended to be illustrative only.

关于本文中所使用的“包含”、“包括”、“具有”、“含有”等等,均为开放性的用语,即意指包含但不限于。The words "includes", "includes", "has", "contains", etc. used in this article are all open terms, which mean including but not limited to.

本发明中所述的“室温”如无特别说明,均按25±2℃计。Unless otherwise specified, the "room temperature" mentioned in the present invention is calculated as 25±2°C.

本发明所用原料Fe(NO3)3·9H2O(分析纯)购买自国药集团;The raw material Fe(NO 3 ) 3 ·9H 2 O (analytically pure) used in the present invention was purchased from Sinopharm Group;

一种铁掺杂铋氧硫光催化剂,以Bi2O2S晶体和Fe(NO3)3·9H2O为原料,采用高能球磨法,制备铁掺杂铋氧硫光催化剂;其中,Fe在铁掺杂铋氧硫光催化剂中的掺杂量为1.7-5.6%。An iron-doped bismuth oxysulfur photocatalyst uses Bi 2 O 2 S crystal and Fe(NO 3 ) 3 ·9H 2 O as raw materials, and uses a high-energy ball milling method to prepare an iron-doped bismuth oxysulfur photocatalyst; wherein, Fe The doping amount in the iron-doped bismuth oxysulfur photocatalyst is 1.7-5.6%.

在一些优选实施例中,所述Bi2O2S晶体为纳米片状结构。In some preferred embodiments, the Bi 2 O 2 S crystal is a nanosheet structure.

本发明还提供一种铁掺杂铋氧硫光催化剂的制备方法,包括以下步骤:The invention also provides a method for preparing an iron-doped bismuth oxysulfur photocatalyst, which includes the following steps:

以Bi2O2S晶体和Fe(NO3)3·9H2O为原料,采用高能球磨法,制备铁掺杂铋氧硫光催化剂,其中,Bi2O2S晶体的质量为0.5g;Fe(NO3)3·9H2O质量为0.0625-0.2142g,更优选为0.0625g、0.125g、0.2142g。Using Bi 2 O 2 S crystal and Fe(NO 3 ) 3 ·9H 2 O as raw materials, the iron-doped bismuth oxysulfur photocatalyst was prepared by high-energy ball milling method, in which the mass of Bi 2 O 2 S crystal was 0.5g; The mass of Fe(NO 3 ) 3 ·9H 2 O is 0.0625-0.2142g, more preferably 0.0625g, 0.125g, or 0.2142g.

在一些优选实施例中,球磨过程中,球磨转运强度为800rpm,球磨时间为20min。In some preferred embodiments, during the ball milling process, the ball milling transfer intensity is 800 rpm, and the ball milling time is 20 minutes.

在一些优选实施例中,球磨后的样品在室温下加入水中搅拌,干燥。In some preferred embodiments, the ball-milled sample is added to water at room temperature, stirred, and dried.

在一些优选实施例中,所述搅拌时间为120min。In some preferred embodiments, the stirring time is 120 minutes.

本发明还提供一种铁掺杂铋氧硫光催化剂在模拟太阳光照下活化过硫酸盐降解四环素的应用。The invention also provides an application of an iron-doped bismuth oxygen-sulfur photocatalyst in activating persulfate to degrade tetracycline under simulated sunlight.

实施例1Example 1

一种铁掺杂铋氧硫光催化剂的制备方法,步骤如下:A preparation method of iron-doped bismuth oxygen-sulfur photocatalyst, the steps are as follows:

1)称取0.5g的Bi2O2S晶体、0.0625g的Fe(NO3)3·9H2O加入球磨罐中,于工作强度为800rpm的球磨机中研磨20min,得到球磨后的样品;1) Weigh 0.5g of Bi 2 O 2 S crystals and 0.0625g of Fe(NO 3 ) 3 ·9H 2 O into a ball mill tank, and grind for 20 minutes in a ball mill with a working intensity of 800 rpm to obtain a ball-milled sample;

2)室温下,将球磨后的样品加入250mL水中搅拌120min,水洗干燥后即获得铁掺杂铋氧硫光催化剂,标记1.7%Fe/BiOS。2) At room temperature, add the ball-milled sample to 250 mL of water and stir for 120 minutes. After washing and drying, an iron-doped bismuth oxysulfide photocatalyst is obtained, labeled 1.7% Fe/BiOS.

实施例2Example 2

一种铁掺杂铋氧硫光催化剂的制备方法,步骤如下:A preparation method of iron-doped bismuth oxygen-sulfur photocatalyst, the steps are as follows:

1)称取0.5g的Bi2O2S晶体、0.125g的Fe(NO3)3·9H2O加入球磨罐中,于工作强度为800rpm的球磨机中研磨20min,得到球磨后的样品;1) Weigh 0.5g of Bi 2 O 2 S crystals and 0.125g of Fe(NO 3 ) 3 ·9H 2 O into a ball mill tank, and grind for 20 minutes in a ball mill with a working intensity of 800 rpm to obtain a ball-milled sample;

2)室温下,将球磨后的样品加入250mL水中搅拌120min,水洗干燥后即获得铁掺杂铋氧硫光催化剂,标记3.3%Fe/BiOS。2) At room temperature, add the ball-milled sample to 250 mL of water and stir for 120 minutes. After washing and drying, an iron-doped bismuth oxysulfide photocatalyst is obtained, labeled 3.3% Fe/BiOS.

实施例3Example 3

一种铁掺杂铋氧硫光催化剂的制备方法,步骤如下:A preparation method of iron-doped bismuth oxygen-sulfur photocatalyst, the steps are as follows:

1)称取0.5g的Bi2O2S晶体、0.2412g的Fe(NO3)3·9H2O加入球磨罐中,于工作强度为800rpm的球磨机中研磨20min,得到球磨后的样品;1) Weigh 0.5g of Bi 2 O 2 S crystals and 0.2412g of Fe(NO 3 ) 3 ·9H 2 O into a ball mill tank, and grind them in a ball mill with a working intensity of 800 rpm for 20 minutes to obtain a ball-milled sample;

2)室温下,将球磨后的样品加入250mL水中搅拌120min,水洗干燥后即获得铁掺杂铋氧硫光催化剂,标记5.6%Fe/BiOS。2) At room temperature, add the ball-milled sample to 250 mL of water and stir for 120 minutes. After washing and drying, an iron-doped bismuth oxysulfide photocatalyst is obtained, labeled 5.6% Fe/BiOS.

对照组1Control group 1

一种铁掺杂铋氧硫光催化剂的制备方法,步骤如下:A preparation method of iron-doped bismuth oxygen-sulfur photocatalyst, the steps are as follows:

Bi2O2S晶体的制备:将1.9403g的Bi(NO3)3·5H2O加入到60mL去离子水中搅拌均匀,再向其中加入0.1522g的SC(NH2)2继续搅拌10min,然后将12g的LiOH·H2O缓慢加入到上述混合溶液中,并持续搅拌60min形成棕黑色混合溶液;将上述搅拌后的均匀混合溶液转移到80mL的PPL内衬的高压反应釜中。将高压反应釜放于鼓风干燥箱中加热至200℃,并在此温度下维持72h。当高压反应釜冷却到室温后,将剩余的样品收集并用去离子水洗数遍。最后,将洗完后的样品放在60℃的真空干燥箱中干燥12h。将干燥后的样品收集起来,得到Bi2O2S样品(标记为BiOS)。Preparation of Bi 2 O 2 S crystals: Add 1.9403g of Bi(NO 3 ) 3 ·5H 2 O to 60 mL of deionized water and stir evenly, then add 0.1522g of SC(NH 2 ) 2 and continue stirring for 10 min, then Slowly add 12 g of LiOH·H 2 O to the above mixed solution, and continue stirring for 60 minutes to form a brown-black mixed solution; transfer the above stirred uniform mixed solution to an 80 mL PPL-lined high-pressure reaction kettle. Place the high-pressure reaction kettle in a blast drying oven, heat it to 200°C, and maintain it at this temperature for 72 hours. After the high-pressure reactor cooled to room temperature, the remaining samples were collected and washed several times with deionized water. Finally, the washed samples were dried in a vacuum drying oven at 60°C for 12 h. The dried samples were collected to obtain a Bi 2 O 2 S sample (labeled BiOS).

图1为本发明实施例1-3制备的铁掺杂铋氧硫光催化剂和对照组制备的催化剂的X射线衍射图。从图中可以看出,实施例1制备的1.7%Fe/BiOS的XRD衍射峰位置与Bi2O2S(PDF#34-1493)标准峰位置对应,表明掺杂后的光催化剂中Bi2O2S物相未发生改变,且未生成其他杂质;实施例2制备的3.3%Fe/BiOS的XRD衍射峰位置与Bi2O2S(PDF#34-1493)标准峰位置对应,表明掺杂后的光催化剂中Bi2O2S物相未发生改变,且未生成其他杂质;实施例3制备的5.6%Fe/BiOS的XRD衍射峰位置与Bi2O2S(PDF#34-1493)标准峰位置对应,表明掺杂后的光催化剂中Bi2O2S物相未发生改变,且未生成其他杂质。Figure 1 is the X-ray diffraction pattern of the iron-doped bismuth oxysulfur photocatalyst prepared in Examples 1-3 of the present invention and the catalyst prepared in the control group. It can be seen from the figure that the XRD diffraction peak position of the 1.7% Fe/BiOS prepared in Example 1 corresponds to the standard peak position of Bi 2 O 2 S (PDF #34-1493), indicating that Bi 2 in the doped photocatalyst The physical phase of O 2 S does not change, and no other impurities are generated; the XRD diffraction peak position of the 3.3% Fe/BiOS prepared in Example 2 corresponds to the standard peak position of Bi 2 O 2 S (PDF #34-1493), indicating that doping The Bi 2 O 2 S phase in the doped photocatalyst does not change, and no other impurities are generated; the XRD diffraction peak position of the 5.6% Fe/BiOS prepared in Example 3 is consistent with that of Bi 2 O 2 S (PDF#34-1493 ) corresponds to the standard peak position, indicating that the Bi 2 O 2 S phase in the doped photocatalyst has not changed and no other impurities are generated.

应用例1Application example 1

将实施例1-3制备的铁掺杂铋氧硫光催化剂和对照组1制备的催化剂进行光催化活化过硫酸盐降解四环素性能测试,具体方法如下:The iron-doped bismuth oxysulfur photocatalyst prepared in Examples 1-3 and the catalyst prepared in Control 1 were subjected to photocatalytic activation persulfate degradation tetracycline performance test. The specific method is as follows:

称取0.05g实施例1-3制备的铁掺杂铋氧硫光催化剂和对照组1制备的催化剂加入100mL浓度为30mg/L的四环素溶液中,遮光搅拌0.5h,使催化剂与污染物混合均匀并达到吸附平衡,取5mL溶液至离心管中,并加入1mL甲醇。然后向烧杯中迅速加入0.03g的过硫酸盐(本实验中使用的是过硫酸钾),同时打开氙灯(300W)光照反应30min,每隔5min取5mL溶液至离心管中,并加入1mL甲醇。利用分光光度计在四环素的最大吸收波长357nm处测其吸光度,根据测试结果分析四环素浓度变化,由此计算出光催化剂对四环素的降解效果。Weigh 0.05g of the iron-doped bismuth oxygen-sulfur photocatalyst prepared in Examples 1-3 and the catalyst prepared in Control 1 and add it to 100 mL of a tetracycline solution with a concentration of 30 mg/L. Stir in the dark for 0.5 h to mix the catalyst and pollutants evenly. And to reach adsorption equilibrium, take 5mL of the solution into a centrifuge tube and add 1mL of methanol. Then quickly add 0.03g of persulfate (potassium persulfate was used in this experiment) into the beaker, and turn on the xenon lamp (300W) to illuminate the reaction for 30 minutes. Take 5mL of the solution into the centrifuge tube every 5min, and add 1mL of methanol. Use a spectrophotometer to measure the absorbance of tetracycline at its maximum absorption wavelength of 357 nm. Analyze the changes in tetracycline concentration based on the test results to calculate the degradation effect of the photocatalyst on tetracycline.

图2为本发明实施例1-3制备的铁掺杂铋氧硫光催化剂和对照组制备的催化剂光催化活化过硫酸盐降解四环素的效果图。从图2中可以看出,实施例1制备的1.7%Fe/BiOS催化剂在光催化活化过硫酸盐降解四环素的试验中,83%的四环素被降解;实施例2制备的3.3%Fe/BiOS催化剂在光催化活化过硫酸盐降解四环素的试验中,90%的四环素被降解;实施例3制备的5.6%Fe/BiOS催化剂在光催化活化过硫酸盐降解四环素的试验中,86%的四环素被降解;而未加修饰的Bi2O2S在光催化活化过硫酸盐降解四环素的试验中,57%的四环素被降解,由此表明本发明实施例1-3制备的催化剂在光催化活化过硫酸盐降解四环素的性能明显高于未加修饰的Bi2O2S。Figure 2 is a diagram showing the effect of photocatalytic activation of persulfate to degrade tetracycline by the iron-doped bismuth oxysulfur photocatalyst prepared in Examples 1-3 of the present invention and the catalyst prepared by the control group. As can be seen from Figure 2, in the photocatalytic activation test of persulfate degradation of tetracycline using the 1.7% Fe/BiOS catalyst prepared in Example 1, 83% of the tetracycline was degraded; the 3.3% Fe/BiOS catalyst prepared in Example 2 In the test of photocatalytic activation of persulfate to degrade tetracycline, 90% of tetracycline was degraded; in the test of photocatalytic activation of persulfate to degrade tetracycline, 86% of tetracycline was degraded by the 5.6% Fe/BiOS catalyst prepared in Example 3 ; In the test of photocatalytic activation of persulfate to degrade tetracycline by unmodified Bi 2 O 2 S, 57% of the tetracycline was degraded, which shows that the catalyst prepared in Examples 1-3 of the present invention is effective in photocatalytic activation of persulfate. The performance of salt degradation of tetracycline is significantly higher than that of unmodified Bi 2 O 2 S.

图3为本发明实施例2制备的铁掺杂铋氧硫光催化剂的TEM图。从图中可以看出,通过球磨法制备的铁掺杂铋氧硫光催化剂为纳米片状。Figure 3 is a TEM image of the iron-doped bismuth oxysulfur photocatalyst prepared in Example 2 of the present invention. It can be seen from the figure that the iron-doped bismuth oxysulfur photocatalyst prepared by ball milling is in the shape of nanosheets.

图4为本发明实施例2制备的铁掺杂铋氧硫光催化剂光催化反应前后的XRD图。从图中可以看出,光催化反应前后的铁掺杂铋氧硫光催化剂的XRD没有发生明显变化,说明铁掺杂铋氧硫光催化剂具有良好的稳定性。Figure 4 is an XRD pattern before and after the photocatalytic reaction of the iron-doped bismuth oxysulfur photocatalyst prepared in Example 2 of the present invention. It can be seen from the figure that the XRD of the iron-doped bismuth oxysulfide photocatalyst before and after the photocatalytic reaction does not change significantly, indicating that the iron-doped bismuth oxysulfide photocatalyst has good stability.

对比例1Comparative example 1

同实施例2,区别在于,球磨时间为10min。Same as Example 2, except that the ball milling time is 10 minutes.

采用与实施例2相同的方法,将其进行光催化活化过硫酸盐降解四环素性能测试,结果发现,84%的四环素被降解。Using the same method as Example 2, the photocatalytic activation persulfate degradation tetracycline performance test was performed. As a result, it was found that 84% of the tetracycline was degraded.

对比例2Comparative example 2

同实施例2,区别在于,球磨时间为40min。Same as Example 2, except that the ball milling time is 40 minutes.

采用与实施例2相同的方法,将其进行光催化活化过硫酸盐降解四环素性能测试,结果发现,90%的四环素被降解。Using the same method as Example 2, the photocatalytic activation persulfate degradation tetracycline performance test was performed. As a result, it was found that 90% of the tetracycline was degraded.

图5为本发明实施例2、对比例1、对比例2制备的铁掺杂铋氧硫光催化剂光催化活化过硫酸盐降解四环素的效果图。从图中可以看出,经过30min的光催化反应,研磨10min获得的铁掺杂铋氧硫光催化剂光催化活化过硫酸盐降解四环素的效果不如研磨20min获得的铁掺杂铋氧硫光催化剂;而研磨20min和40min获得的铁掺杂铋氧硫光催化剂光催化活化过硫酸盐降解四环素的效果相当。但是考虑到能耗和成本,研磨20min获得铁掺杂铋氧硫光催化剂的方法更合适。Figure 5 is a diagram showing the effect of photocatalytic activation of persulfate to degrade tetracycline by the iron-doped bismuth oxysulfur photocatalyst prepared in Example 2, Comparative Example 1, and Comparative Example 2 of the present invention. It can be seen from the figure that after 30 minutes of photocatalytic reaction, the iron-doped bismuth oxysulfide photocatalyst obtained by grinding for 10 minutes is less effective in photocatalytically activating persulfate for degrading tetracycline than the iron-doped bismuth oxysulfide photocatalyst obtained by grinding for 20 minutes; The iron-doped bismuth oxysulfur photocatalysts obtained by grinding for 20 minutes and 40 minutes have equivalent photocatalytic activation of persulfate for the degradation of tetracycline. However, considering energy consumption and cost, the method of grinding for 20 minutes to obtain the iron-doped bismuth oxygen-sulfur photocatalyst is more suitable.

以上所述仅为本发明的较佳实施例,并不用以限制本发明,凡在本发明的精神和原则之内所作的任何修改、等同替换和改进等,均应包含在本发明的保护范围之内。The above are only preferred embodiments of the present invention and are not intended to limit the present invention. Any modifications, equivalent substitutions and improvements made within the spirit and principles of the present invention shall be included in the protection scope of the present invention. within.

Claims (3)

1.一种用于光催化活化过硫酸盐处理含有四环素废水的铁掺杂铋氧硫光催化剂的制备方法,其特征在于,包括以下步骤:1. A method for preparing an iron-doped bismuth oxysulfur photocatalyst for photocatalytically activated persulfate treatment of wastewater containing tetracycline, which is characterized in that it includes the following steps: 以Bi2O2S晶体和Fe(NO3)3·9H2O为原料,采用高能球磨法,制备铁掺杂铋氧硫光催化剂,其中,Bi2O2S晶体和Fe(NO3)3·9H2O的质量比为0.5:(0.0625-0.2142);Using Bi 2 O 2 S crystal and Fe(NO 3 ) 3 ·9H 2 O as raw materials, an iron-doped bismuth oxysulfur photocatalyst was prepared using high-energy ball milling method, in which Bi 2 O 2 S crystal and Fe(NO 3 ) The mass ratio of 3 ·9H 2 O is 0.5: (0.0625-0.2142); Fe在铁掺杂铋氧硫光催化剂中的掺杂量为1.7-5.6%;The doping amount of Fe in the iron-doped bismuth oxysulfur photocatalyst is 1.7-5.6%; 球磨过程中,球磨工作强度为800rpm,球磨时间为20min;During the ball milling process, the ball milling working intensity is 800rpm and the ball milling time is 20min; 球磨后的样品在室温下加入水中搅拌120min,干燥。The ball-milled sample was added to water at room temperature, stirred for 120 min, and dried. 2.根据权利要求1所述的制备方法,其特征在于,所述Bi2O2S晶体为纳米片状结构。2. The preparation method according to claim 1, characterized in that the Bi 2 O 2 S crystal has a nanosheet structure. 3.一种如权利要求1或2所述的制备方法制备得到的铁掺杂铋氧硫光催化剂在光催化活化过硫酸盐处理含有四环素废水中的应用。3. Application of an iron-doped bismuth oxysulfur photocatalyst prepared by the preparation method of claim 1 or 2 in photocatalytically activated persulfate treatment of wastewater containing tetracycline.
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