CN115636440B - In+ doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheet and preparation method thereof - Google Patents
In+ doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheet and preparation method thereof Download PDFInfo
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Abstract
本发明公开了一种In+掺杂(001)晶面暴露含氧空位BiOCl纳米片可见光光催化剂及其制备方法。它以硝酸铋、硝酸铟和氯化钾为前躯体(铟元素与铋元素的物质的量比为1:100~5:100,以体积比为1:8~1:3的乙二醇和水的混合溶液为溶剂,在160oC~180oC反应10~30小时得到In3+掺杂(001)晶面暴露BiOCl纳米片,所得样品经紫外光照1~4小时得到In+掺杂(001)晶面暴露含氧空位BiOCl纳米片,其尺寸小于200 nm,厚度为15~25 nm。使用本发明方法制备的(001)晶面暴露BiOCl纳米片中In+与氧空位共存,铟元素取代了铋元素的位置,在可见光下能高效降解杀虫剂五氯酚钠。本发明工艺简单,成本低,环境友好,产率高,适合大规模生产,符合实际生产需要,有较大的应用潜力。
The invention discloses an In + doped (001) crystal plane exposed oxygen vacancy-containing BiOCl nanosheet visible light photocatalyst and a preparation method thereof. The method uses bismuth nitrate, indium nitrate and potassium chloride as precursors (the molar ratio of indium element to bismuth element is 1:100-5:100), and a mixed solution of ethylene glycol and water with a volume ratio of 1:8-1:3 is used as a solvent. The method reacts at 160 ° C-180 ° C for 10-30 hours to obtain In 3+ doped (001) crystal surface exposed BiOCl nanosheets. The obtained sample is irradiated with ultraviolet light for 1-4 hours to obtain In + doped (001) crystal surface exposed oxygen vacancy BiOCl nanosheets, the size of which is less than 200 nm and the thickness is 15-25 nm. In the (001) crystal surface exposed BiOCl nanosheets prepared by the method of the invention, In + and oxygen vacancies coexist, and the indium element replaces the position of the bismuth element, and the insecticide sodium pentachlorophenol can be efficiently degraded under visible light. The method of the invention has simple process, low cost, environmental friendliness, high yield, is suitable for large-scale production, meets actual production needs, and has great application potential.
Description
技术领域Technical Field
本发明属于光催化材料制备技术领域,具体涉及In+掺杂(001)晶面暴露含氧空位BiOCl纳米片及其制备方法。The invention belongs to the technical field of photocatalytic material preparation, and in particular relates to In + doped (001) crystal plane exposed oxygen vacancy-containing BiOCl nanosheets and a preparation method thereof.
背景技术Background technique
BiOCl因具有独特的层状结构而备受关注,因其禁带宽度大,氧化还原能力强、光催化活性高等优点而被应用在液相和气相污染物处理领域。但其宽禁带特征降低了对太阳光的利用率,使其应用收到限制。近年来研究发现金属离子掺杂能够调控BiOCl能带结构提高其可见光催化性能。BiOCl has attracted much attention due to its unique layered structure. It is used in the treatment of liquid and gas phase pollutants due to its wide bandgap, strong redox ability, and high photocatalytic activity. However, its wide bandgap reduces the utilization rate of sunlight, limiting its application. In recent years, studies have found that metal ion doping can regulate the band structure of BiOCl and improve its visible light photocatalytic performance.
如分别采用水解法[Applied Surface Science 258(2011)247-253],溶剂热法[Phys.Chem.Chem.Phys.16(2014)21349-21355],水热法[AppliedCatalysis B:Environmental 221(2018)320-328]和燃烧法[Separationand Purification Technology162(2016)114-119]制备了锰、钨、钴和铁掺杂的BiOCl并研究了其可见光催化活性。其它如碱金属和稀土金属掺杂的BiOCl[中国发明专利CN107597150A]也被广泛研究。Jingfa Li等计算发现铟掺杂BiOCl能使其导带电位更负[Chemical Physics Letter 705 (2018) 31-37],提高导带电子还原效率,但是其禁带宽度增大,不利于可见光效率提高,因此关于铟掺杂BiOCl可见光催化剂至今没有报道。For example, BiOCl doped with manganese, tungsten, cobalt and iron was prepared by hydrolysis method [Applied Surface Science 258 (2011) 247-253], solvothermal method [Phys. Chem. Chem. Phys. 16 (2014) 21349-21355], hydrothermal method [Applied Catalysis B: Environmental 221 (2018) 320-328] and combustion method [Separation and Purification Technology 162 (2016) 114-119] and its visible light catalytic activity was studied. Other BiOCl doped with alkali metals and rare earth metals [Chinese invention patent CN107597150A] has also been widely studied. Jingfa Li et al. calculated that indium-doped BiOCl can make its conduction band potential more negative [Chemical Physics Letter 705 (2018) 31-37], thereby improving the conduction band electron reduction efficiency. However, the increased bandgap width is not conducive to improving the visible light efficiency. Therefore, there has been no report on indium-doped BiOCl visible light catalysts so far.
发明内容Summary of the invention
为解决上述问题本发明采用乙二醇和水混合体系溶剂热法制备In3+掺杂(001)晶面暴露BiOCl纳米片,并在室温下经过紫外光照得到In+掺杂(001)晶面暴露的含氧空位BiOCl纳米片可见光光催化剂。本发明所制备的In+掺杂(001)晶面暴露的含氧空位BiOCl纳米片在可见光下能高效降解高浓度杀虫剂五氯酚钠,经过半个小时可见光照,能将20毫克/升的五氯酚钠几乎完全降解,降解速率分别达未掺杂铟的(001)晶面暴露含氧空位BiOCl纳米片的6.8倍和In3+掺杂(001)晶面暴露BiOCl纳米片的27.4倍。本发明工艺简单,成本低,而且环境友好,便于进一步扩大生产。In order to solve the above problems, the present invention adopts a solvothermal method of a mixed system of ethylene glycol and water to prepare In 3+ doped (001) crystal surface exposed BiOCl nanosheets, and obtains In + doped (001) crystal surface exposed oxygen vacancy BiOCl nanosheet visible light photocatalyst through ultraviolet irradiation at room temperature. The In + doped (001) crystal surface exposed oxygen vacancy BiOCl nanosheet prepared by the present invention can efficiently degrade high concentration of insecticide sodium pentachlorophenol under visible light. After half an hour of visible light irradiation, 20 mg/L of sodium pentachlorophenol can be almost completely degraded, and the degradation rate is 6.8 times that of undoped indium (001) crystal surface exposed oxygen vacancy BiOCl nanosheet and 27.4 times that of In 3+ doped (001) crystal surface exposed BiOCl nanosheet. The present invention has simple process, low cost, and is environmentally friendly, which is convenient for further expansion of production.
为实现上述目的,本发明所述的In+掺杂(001)晶面暴露含氧空位BiOCl纳米片的制备方法采用以下技术手段,包括以下步骤:To achieve the above object, the preparation method of the In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets of the present invention adopts the following technical means, including the following steps:
In+掺杂(001)晶面暴露含氧空位BiOCl纳米片的制备方法,Preparation method of In + doped (001) crystal plane exposed oxygen vacancies containing BiOCl nanosheets,
1)硝酸铋、硝酸铟和氯化钾加入水和乙二醇的混合溶液中,在磁力搅拌下形成悬浊液,其中水和乙二醇体积比为1:8~1:3;1) Bismuth nitrate, indium nitrate and potassium chloride are added to a mixed solution of water and ethylene glycol to form a suspension under magnetic stirring, wherein the volume ratio of water to ethylene glycol is 1:8 to 1:3;
2)将步骤1)得到悬浊液置于聚四氟乙烯反应釜中,在160oC~180oC的氛围中静置10~30小时,形成沉淀;2) placing the suspension obtained in step 1) in a polytetrafluoroethylene reactor and allowing it to stand in an atmosphere of 160 ° C to 180 ° C for 10 to 30 hours to form a precipitate;
3)将步骤2)得到的沉淀洗涤干燥得到In3+掺杂(001)晶面暴露BiOCl纳米片;3) washing and drying the precipitate obtained in step 2) to obtain In 3+ doped (001) crystal surface exposed BiOCl nanosheets;
4)将步骤3)得到的样品经紫外光照得到In+掺杂(001)晶面暴露含氧空位BiOCl纳米片。4) The sample obtained in step 3) is irradiated with ultraviolet light to obtain In + doped (001) crystal plane exposed oxygen vacancies containing BiOCl nanosheets.
作为本发明In+掺杂(001)晶面暴露含氧空位BiOCl纳米片的进一步改进:所述步骤1)中铟元素与铋元素的物质的量比为1:100~5:100,总体积为40 mL,硝酸铋和硝酸铟物质的量之和与氯化钾的物质的量相等。As a further improvement of the In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets of the present invention: in the step 1), the molar ratio of indium element to bismuth element is 1:100 to 5:100, the total volume is 40 mL, and the sum of the moles of bismuth nitrate and indium nitrate is equal to the mole of potassium chloride.
作为本发明In+掺杂(001)晶面暴露含氧空位BiOCl纳米片的进一步改进:所述步骤4)中紫外光照在室温下进行,样品距离光源10 cm以内并持续在300瓦汞灯发射紫外光下光照1~4小时,所述汞灯紫外光波长范围为350 nm~450 nm,波长峰值为365 nm。As a further improvement of the In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets of the present invention: the ultraviolet irradiation in the step 4) is carried out at room temperature, the sample is within 10 cm from the light source and continuously irradiated with ultraviolet light emitted by a 300-watt mercury lamp for 1 to 4 hours, and the ultraviolet light wavelength range of the mercury lamp is 350 nm to 450 nm, and the peak wavelength is 365 nm.
In+掺杂(001)晶面暴露含氧空位BiOCl纳米片,其特征在于:In3+掺杂(001)晶面暴露BiOCl纳米片经紫外光照形成In+掺杂(001)晶面暴露含氧空位的BiOCl纳米片,尺寸小于200 nm,厚度为15~25 nm。The invention discloses an In + doped (001) crystal plane exposed BiOCl nanosheet containing oxygen vacancies, characterized in that the In3 + doped (001) crystal plane exposed BiOCl nanosheet is irradiated with ultraviolet light to form an In + doped (001) crystal plane exposed BiOCl nanosheet containing oxygen vacancies, the size of which is less than 200 nm and the thickness is 15 to 25 nm.
所述In+掺杂(001)晶面暴露含氧空位BiOCl纳米片作为可见光光催化剂。The In + doped (001) crystal plane exposed oxygen vacancies in the BiOCl nanosheets as visible light photocatalysts.
有益效果Beneficial Effects
与现有技术相比,本发明具有以下有益效果:Compared with the prior art, the present invention has the following beneficial effects:
第一,本发明制备的In+掺杂(001)晶面暴露含氧空位BiOCl纳米片,其尺寸小于200 nm,厚度为15~25 nm,为类似方法制备的P掺杂BiOCl纳米片尺寸的一半左右。增大了比表面积,有利于提高其光催化活性。本发明所制备的In+掺杂(001)晶面暴露含氧空位BiOCl纳米片中铟元素取代了晶格中铋元素,在可见光下半个小时能将20毫克/升的五氯酚钠几乎完全降解,降解速率达未掺杂铟的(001)晶面暴露含氧空位BiOCl纳米片的6.8倍,是In3+掺杂(001)晶面暴露BiOCl纳米片的27.4倍。First, the In + doped (001) crystal surface exposed oxygen vacancies BiOCl nanosheets prepared by the present invention have a size of less than 200 nm and a thickness of 15 to 25 nm, which is about half the size of P doped BiOCl nanosheets prepared by similar methods. The specific surface area is increased, which is beneficial to improving its photocatalytic activity. In the In + doped (001) crystal surface exposed oxygen vacancies BiOCl nanosheets prepared by the present invention, the indium element replaces the bismuth element in the lattice, and 20 mg/L of sodium pentachlorophenol can be almost completely degraded in half an hour under visible light, and the degradation rate is 6.8 times that of the undoped indium (001) crystal surface exposed oxygen vacancies BiOCl nanosheets, and 27.4 times that of the In 3 + doped (001) crystal surface exposed BiOCl nanosheets.
第二,本发明所述的In+掺杂(001)晶面暴露含氧空位BiOCl纳米片制备中,水和乙二醇体积比设定为1:8~1:3,经大量实验得出若乙二醇体积比高于此范围容易生成BiOCl分等级球状结构,而低于此范围得到BiOCl片尺寸会明显增大,将降低样品比表面积和光催化活性。此外,乙二醇的存在也避免了In(OH)3沉淀的生成,保证了铟以离子形式掺杂入BiOCl中。同时当铟元素与铋元素物质的量比高于5:100时容易生成杂质。Second, in the preparation of the In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets described in the present invention, the volume ratio of water to ethylene glycol is set to 1:8 to 1:3. After a large number of experiments, it is found that if the volume ratio of ethylene glycol is higher than this range, it is easy to generate a graded spherical structure of BiOCl, while if it is lower than this range, the size of the BiOCl sheet will be significantly increased, which will reduce the specific surface area and photocatalytic activity of the sample. In addition, the presence of ethylene glycol also avoids the formation of In(OH) 3 precipitation, ensuring that indium is doped into BiOCl in the form of ions. At the same time, when the molar ratio of indium element to bismuth element is higher than 5:100, impurities are easily generated.
第三,本发明制备的In+掺杂(001)晶面暴露含氧空位BiOCl纳米片,实现铟掺杂BiOCl的可见光光催化活性,其降解杀虫剂五氯酚钠等高浓度水体污染物的效率大大提高,为环境水污染治理提供了新的光催化材料。Third, the In + doped (001) crystal planes prepared by the present invention expose oxygen vacancies in the BiOCl nanosheets, realizing the visible light photocatalytic activity of indium doped BiOCl, and greatly improving the efficiency of degrading high-concentration water pollutants such as the pesticide sodium pentachlorophenol, providing a new photocatalytic material for environmental water pollution control.
第四,本发明所述的紫外光照1~4小时使BiOCl产生氧空位,同时激发了BiOCl本征能带促进了光生电子的产生,这使In3+还原为In+,In+的存在进一步提高了可见光催化反应中电子和空穴的分离效率,提高了可见光催化活性。Fourthly, the ultraviolet irradiation for 1 to 4 hours described in the present invention generates oxygen vacancies in BiOCl and simultaneously excites the intrinsic energy band of BiOCl to promote the generation of photogenerated electrons, which reduces In 3+ to In + . The presence of In + further improves the separation efficiency of electrons and holes in the visible light catalytic reaction and improves the visible light catalytic activity.
第五,整个工艺过程简单易控制,耗能少,产率高,成本低,符合实际生产需要。Fifth, the entire process is simple and easy to control, consumes less energy, has high yield, and low cost, which meets actual production needs.
第六,本发明原料廉价易得,反应条件温和,耗能少,对设备要求低,In+与氧空位共存于(001)晶面暴露BiOCl纳米片中大大提高可见光下电子空穴的分离效率,能快速降解高浓度水体污染物,具有很好的应用前景。Sixth, the raw materials of the present invention are cheap and easy to obtain, the reaction conditions are mild, the energy consumption is low, and the equipment requirements are low. The coexistence of In + and oxygen vacancies in the (001) crystal surface exposed BiOCl nanosheets greatly improves the separation efficiency of electrons and holes under visible light, can quickly degrade high-concentration water pollutants, and has good application prospects.
附图说明BRIEF DESCRIPTION OF THE DRAWINGS
图1是实施例2所制备In3+掺杂(001)晶面暴露BiOCl纳米片、实施例4所制备In+掺杂(001)晶面暴露含氧空位BiOCl纳米片和实施例1所制备(001)晶面暴露含氧空位BiOCl纳米片样品的XRD衍射图。FIG1 is an XRD diffraction pattern of the In 3+ doped (001) crystal plane exposed BiOCl nanosheets prepared in Example 2, the In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets prepared in Example 4, and the (001) crystal plane exposed oxygen vacancies BiOCl nanosheet samples prepared in Example 1.
图2是实施例2和实施例4所得样品的XPS全谱图及In 3d的高分辨能谱图。FIG. 2 is the full XPS spectrum of the samples obtained in Example 2 and Example 4 and the high-resolution energy spectrum of In 3d.
图3是实施例2 (3a, 3b, 3c)和实施例4(3d, 3e, 3f)所得样品的TEM、SAED和HRTEM图。FIG3 is TEM, SAED and HRTEM images of the samples obtained in Example 2 (3a, 3b, 3c) and Example 4 (3d, 3e, 3f).
图4是实施例4所得样品的EPR谱图。FIG. 4 is an EPR spectrum of the sample obtained in Example 4.
图5是实施例2所制备In3+掺杂(001)晶面暴露BiOCl纳米片和实施例4所制备In+掺杂(001)晶面暴露含氧空位BiOCl纳米片的紫外可见吸收光谱图。FIG5 is a graph of the UV-visible absorption spectra of the In 3+ doped (001) crystal plane exposed BiOCl nanosheets prepared in Example 2 and the In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets prepared in Example 4.
图6是实施例4所得In+掺杂(001)晶面暴露含氧空位BiOCl纳米片,实施例2所制备In3+掺杂(001)晶面暴露BiOCl纳米片和实施例1所制备(001)晶面暴露含氧空位BiOCl纳米片在可见光下降解杀虫剂五氯酚钠的效果比较图。FIG6 is a comparison of the degradation effects of the pesticide sodium pentachlorophenol under visible light by the In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets obtained in Example 4, the In3 + doped (001) crystal plane exposed BiOCl nanosheets prepared in Example 2, and the (001) crystal plane exposed oxygen vacancies BiOCl nanosheets prepared in Example 1.
图7为实施例3,4,5和6中所制备In+掺杂(001)晶面暴露含氧空位BiOCl纳米片样品的光催化活性对比图。FIG. 7 is a comparison of the photocatalytic activities of the In + -doped (001) crystal plane-exposed oxygen vacancies-containing BiOCl nanosheet samples prepared in Examples 3, 4, 5 and 6.
具体实施方式Detailed ways
下面结合附图和具体实施例对本发明作进一步说明,本实施例以本发明技术方案为前提,给出了详细的实施方式。The present invention is further described below in conjunction with the accompanying drawings and specific embodiments. This embodiment is based on the technical solution of the present invention and provides a detailed implementation method.
本发明公开了In+掺杂(001)晶面暴露BiOCl纳米片及其制备方法以及In+掺杂(001)晶面暴露BiOCl纳米片作为光催化剂以高效降解杀虫剂五氯酚钠等高浓度水体污染物的应用,以为环境水污染治理提供了新的光催化材料。The invention discloses an In + doped (001) crystal surface exposed BiOCl nanosheet and a preparation method thereof, and an application of the In + doped (001) crystal surface exposed BiOCl nanosheet as a photocatalyst to efficiently degrade high-concentration water pollutants such as the pesticide sodium pentachlorophenol, thereby providing a new photocatalytic material for environmental water pollution control.
本发明申请中实施例1、实施例2分别制备(001)晶面暴露含氧空位BiOCl纳米片和In3+掺杂(001)晶面暴露BiOCl纳米片,以作为本发明专利申请所要保护的In+掺杂(001)晶面暴露BiOCl纳米片的实验对照组使用。In the present application, Example 1 and Example 2 respectively prepare BiOCl nanosheets with (001) crystal plane exposed oxygen vacancies and In 3+ doped (001) crystal plane exposed BiOCl nanosheets, which are used as experimental control groups for In + doped (001) crystal plane exposed BiOCl nanosheets to be protected by the present patent application.
实施例1Example 1
本实施例制备(001)晶面暴露含氧空位BiOCl纳米片的制备方法在于,将硝酸铋和氯化钾(其中硝酸铋和氯化钾物质的量比为1:1)加入水和乙二醇的混合溶液中(乙二醇和水体积比为1:8),在磁力搅拌下形成悬浊液,悬浊液体积为40 mL;在160oC的氛围中静置20小时,形成沉淀,得到的沉淀烘干便可以得到(001)晶面暴露BiOCl纳米片,然后在紫外光(300瓦汞灯)下照射2小时得到(001)晶面暴露含氧空位BiOCl纳米片。The preparation method of the (001) crystal plane exposed oxygen vacancies BiOCl nanosheets in this embodiment is to add bismuth nitrate and potassium chloride (wherein the molar ratio of bismuth nitrate to potassium chloride is 1:1) to a mixed solution of water and ethylene glycol (the volume ratio of ethylene glycol to water is 1:8) to form a suspension under magnetic stirring, and the volume of the suspension is 40 mL; the suspension is allowed to stand for 20 hours in an atmosphere of 160 o C to form a precipitate, and the obtained precipitate is dried to obtain the (001) crystal plane exposed BiOCl nanosheets, and then irradiated under ultraviolet light (300-watt mercury lamp) for 2 hours to obtain the (001) crystal plane exposed oxygen vacancies BiOCl nanosheets.
实施例2Example 2
本实施例中In+掺杂(001)晶面暴露含氧空位BiOCl纳米片的制备方法在于,将硝酸铋、硝酸铟和氯化钾(其中硝酸铋和硝酸铟物质的量比例为1:100)加入水和乙二醇的混合溶液中(乙二醇和水体积比为1:8),在磁力搅拌下形成悬浊液,悬浊液体积为40 mL;在160oC的氛围中静置20小时,形成沉淀,得到的沉淀烘干便可以得到In3+掺杂(001)晶面暴露BiOCl纳米片。In this embodiment, the preparation method of In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets is to add bismuth nitrate, indium nitrate and potassium chloride (wherein the molar ratio of bismuth nitrate to indium nitrate is 1:100) to a mixed solution of water and ethylene glycol (the volume ratio of ethylene glycol to water is 1:8), and form a suspension under magnetic stirring, the volume of the suspension is 40 mL; stand in an atmosphere of 160 o C for 20 hours to form a precipitate, and the obtained precipitate is dried to obtain In3 + doped (001) crystal plane exposed BiOCl nanosheets.
实施例3Example 3
本实施例中In+掺杂(001)晶面暴露含氧空位BiOCl纳米片的制备方法在于,将硝酸铋、硝酸铟和氯化钾,(其中硝酸铋和硝酸铟物质的量比例为1:100,硝酸铋和硝酸铟物质的量之和与氯化钾的物质的量相等)加入水和乙二醇的混合溶液中(乙二醇和水体积比为1:8),在磁力搅拌下形成悬浊液,悬浊也体积为40 mL;在160oC的氛围中静置20小时,形成沉淀,得到的沉淀烘干便可以得到In3+掺杂(001)晶面暴露BiOCl纳米片,然后在紫外光(300瓦汞灯)下照射1小时得到In+掺杂(001)晶面暴露含氧空位BiOCl纳米片,具体来讲,样品紫外照射过程在室温下进行,将样品距离光源10 cm以内,在300瓦汞灯发射紫外光光源下持续光照1小时,即可得到In+掺杂(001)晶面暴露含氧空位BiOCl纳米片。In this embodiment, the preparation method of In + doped (001) crystal surface exposed oxygen vacancies BiOCl nanosheets is as follows: bismuth nitrate, indium nitrate and potassium chloride (wherein the molar ratio of bismuth nitrate to indium nitrate is 1:100, and the sum of the molar ratio of bismuth nitrate and indium nitrate is equal to the molar ratio of potassium chloride) are added to a mixed solution of water and ethylene glycol (the volume ratio of ethylene glycol to water is 1:8), and a suspension is formed under magnetic stirring, and the volume of the suspension is 40 mL; the suspension is allowed to stand for 20 hours in an atmosphere of 160 o C to form a precipitate, and the obtained precipitate is dried to obtain In 3+ doped (001) crystal surface exposed BiOCl nanosheets, and then irradiated under ultraviolet light (300-watt mercury lamp) for 1 hour to obtain In + doped (001) crystal surface exposed oxygen vacancies BiOCl nanosheets. Specifically, the sample ultraviolet irradiation process is carried out at room temperature, and the sample is within 10 cm from the light source and continuously irradiated under the ultraviolet light source emitted by a 300-watt mercury lamp for 1 hour to obtain In 3+ doped (001) crystal surface exposed oxygen vacancies BiOCl nanosheets. + doped (001) planes expose BiOCl nanosheets containing oxygen vacancies.
实施例4Example 4
本实施例中In+掺杂(001)晶面暴露含氧空位BiOCl纳米片的制备方法在于,将硝酸铋、硝酸铟和氯化钾(其中硝酸铋和硝酸铟物质的量比例为1:100,硝酸铋和硝酸铟物质的量之和与氯化钾的物质的量相等),加入水和乙二醇的混合溶液中(乙二醇和水体积比为1:8),在磁力搅拌下形成悬浊液,悬浊液体积为40 mL;在160oC的氛围中静置20小时,形成沉淀,得到的沉淀烘干便可以得到In3+掺杂(001)晶面暴露BiOCl纳米片,然后室温下将样品暴露于紫外光源10cm内,在紫外光(300瓦汞灯)下持续照射2小时得到In+掺杂(001)晶面暴露含氧空位BiOCl纳米片。In this embodiment, the preparation method of In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets is as follows: bismuth nitrate, indium nitrate and potassium chloride (wherein the molar ratio of bismuth nitrate to indium nitrate is 1:100, and the sum of the molar ratio of bismuth nitrate and indium nitrate is equal to the molar ratio of potassium chloride) are added to a mixed solution of water and ethylene glycol (the volume ratio of ethylene glycol to water is 1:8), and a suspension is formed under magnetic stirring, and the volume of the suspension is 40 mL; the suspension is allowed to stand for 20 hours in an atmosphere of 160 o C to form a precipitate, and the obtained precipitate is dried to obtain In 3+ doped (001) crystal plane exposed BiOCl nanosheets, and then the sample is exposed to an ultraviolet light source within 10 cm at room temperature, and continuously irradiated under ultraviolet light (300-watt mercury lamp) for 2 hours to obtain In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets.
实施例5Example 5
本实施例中In+掺杂(001)晶面暴露含氧空位BiOCl纳米片的制备方法在于,将硝酸铋、硝酸铟和氯化钾(其中硝酸铋和硝酸铟物质的量比例为5:100,硝酸铋和硝酸铟物质的量之和与氯化钾的物质的量相等)加入水和乙二醇的混合溶液中(乙二醇和水体积比为1:5),在磁力搅拌下形成悬浊液,悬浊液体积为40 mL;在160oC的氛围中静置20小时,形成沉淀,得到的沉淀烘干便可以得到In3+掺杂(001)晶面暴露BiOCl纳米片,然后室温下将样品暴露于紫外光源10 cm内,在紫外光(300瓦汞灯)下光照4小时得到In+掺杂(001)晶面暴露BiOCl纳米片。In this embodiment, the preparation method of In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets is to add bismuth nitrate, indium nitrate and potassium chloride (wherein the molar ratio of bismuth nitrate and indium nitrate is 5:100, and the sum of the molar amounts of bismuth nitrate and indium nitrate is equal to the molar amount of potassium chloride) to a mixed solution of water and ethylene glycol (the volume ratio of ethylene glycol to water is 1:5), and form a suspension under magnetic stirring, and the volume of the suspension is 40 mL; the suspension is allowed to stand for 20 hours in an atmosphere of 160 o C to form a precipitate, and the obtained precipitate is dried to obtain In 3+ doped (001) crystal plane exposed BiOCl nanosheets, and then the sample is exposed to an ultraviolet light source within 10 cm at room temperature, and illuminated under ultraviolet light (300-watt mercury lamp) for 4 hours to obtain In + doped (001) crystal plane exposed BiOCl nanosheets.
实施例6Example 6
本实施例中In+掺杂(001)晶面暴露含氧空位BiOCl纳米片的制备方法在于,将硝酸铋、硝酸铟和氯化钾(其中硝酸铋和硝酸铟物质的量比例为5:100,硝酸铋和硝酸铟物质的量之和与氯化钾的物质的量相等),加入水和乙二醇的混合溶液中(乙二醇和水体积比为1:3),在磁力搅拌下形成悬浊液,悬浊液体积为40 mL;在180oC的氛围中静置20小时,形成沉淀,得到的沉淀烘干便可以得到In3+掺杂(001)晶面暴露BiOCl纳米片,然后在室温下将样品暴露于紫外光源10 cm内,在紫外光(300瓦汞灯)下照射4小时得到In+掺杂(001)晶面暴露BiOCl纳米片。In this embodiment, the preparation method of In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets is to add bismuth nitrate, indium nitrate and potassium chloride (wherein the molar ratio of bismuth nitrate to indium nitrate is 5:100, and the sum of the molar ratio of bismuth nitrate and indium nitrate is equal to the molar ratio of potassium chloride) to a mixed solution of water and ethylene glycol (the volume ratio of ethylene glycol to water is 1:3), and form a suspension under magnetic stirring, and the volume of the suspension is 40 mL; the suspension is allowed to stand for 20 hours in an atmosphere of 180 o C to form a precipitate, and the obtained precipitate is dried to obtain In 3+ doped (001) crystal plane exposed BiOCl nanosheets, and then the sample is exposed to an ultraviolet light source within 10 cm at room temperature, and irradiated under ultraviolet light (300-watt mercury lamp) for 4 hours to obtain In + doped (001) crystal plane exposed BiOCl nanosheets.
本发明以上述实施例进行In+掺杂(001)晶面暴露含氧空位BiOCl纳米片的制备并进行数据分析:The present invention uses the above embodiment to prepare In + doped (001) crystal plane exposed oxygen vacancies containing BiOCl nanosheets and conduct data analysis:
如图1对各项BiOCl纳米片样品进行XRD衍射分析,通过数据与标准卡片对比可知,图中两个样品的衍射峰与BiOCl(JCPDS No: 6-249)的标准图谱相吻合,不存在其他杂相。XRD图中掺杂In3+和In+的BiOCl样品衍射峰向高角度方向移动,证明In替代Bi进入了BiOCl晶格。As shown in Figure 1, the XRD diffraction analysis of various BiOCl nanosheet samples is carried out. By comparing the data with the standard card, it can be seen that the diffraction peaks of the two samples in the figure are consistent with the standard spectrum of BiOCl (JCPDS No: 6-249), and there is no other impurity phase. The diffraction peaks of the BiOCl samples doped with In 3+ and In + in the XRD graph move to the high angle direction, proving that In replaces Bi and enters the BiOCl lattice.
从图2全谱中可以看出铟元素的存在,对比In 3d的高分辨能谱图可以发现In+掺杂(001)晶面暴露含氧空位BiOCl纳米片中In 3d结合能比In3+掺杂(001)晶面暴露BiOCl纳米片中低0.4电子福特左右,证实了实施例4制备的样品中铟元素以In+的状态存在。The presence of indium can be seen from the full spectrum in Figure 2. By comparing the high-resolution energy spectrum of In 3d, it can be found that the binding energy of In 3d in the In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets is about 0.4 electron Ford lower than that in the In 3+ doped (001) crystal plane exposed BiOCl nanosheets, confirming that the indium element in the sample prepared in Example 4 exists in the In + state.
图3中,从TEM可以看出所制备的In3+掺杂(001)晶面暴露BiOCl纳米片和In+掺杂(001)晶面暴露含氧空位BiOCl纳米片尺寸均小于200 nm,厚度为20 nm左右。从HRTEM和SAED图片可以看出实施例2和实施例4所制备纳米片的上下两个面均为(001)晶面。In Figure 3, it can be seen from TEM that the size of the prepared In 3+ doped (001) crystal plane exposed BiOCl nanosheets and In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets are both less than 200 nm and the thickness is about 20 nm. From the HRTEM and SAED images, it can be seen that the upper and lower surfaces of the nanosheets prepared in Example 2 and Example 4 are both (001) crystal planes.
从图4的EPR谱图证实了紫外光照后In+掺杂(001)晶面暴露含氧空位BiOCl纳米片中氧空位的存在。The EPR spectrum in Figure 4 confirms the existence of oxygen vacancies in the In + doped (001) crystal plane exposed oxygen vacancies in the BiOCl nanosheets after UV irradiation.
从图5的紫外可见吸收光谱图可以看出,与In3+掺杂(001)晶面暴露BiOCl纳米片相比,虽然In+掺杂(001)晶面暴露含氧空位BiOCl纳米片能带没有明显变化,但其在可见光范围内有较强的杂质能级吸收现象。It can be seen from the UV-visible absorption spectrum of Figure 5 that compared with the In 3+ doped (001) crystal plane exposed BiOCl nanosheets, although the energy band of the In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheets has no obvious change, it has a strong impurity energy level absorption phenomenon in the visible light range.
图6中通过将BiOCl纳米片在可见光下降解杀虫剂五氯酚钠的效果比较图得出,光催化剂活性均通过在可见光下降解杀虫剂五氯酚钠测试,其中用500 W氙灯作为光源,并加上滤波片,将波长小于420 nm的光滤去,从而得到可见光。催化剂的用量为0.05 g,五氯酚钠溶液的浓度为20 mg/L,体积为50 mL。从图中可以看出,经过半小时的可见光照射后,实施例4中In+掺杂(001)晶面暴露含氧空位BiOCl纳米片可以使五氯酚钠几乎完全降解,其降解速率是实施例1中(001)晶面暴露含氧空位BiOCl纳米片的6.8倍,是实施例2中In3+掺杂(001)晶面暴露BiOCl纳米片的27.4倍。Figure 6 shows a comparison of the effects of BiOCl nanosheets on the degradation of sodium pentachlorophenol under visible light. The photocatalyst activity was tested by degrading sodium pentachlorophenol under visible light, where a 500 W xenon lamp was used as the light source, and a filter was added to filter out light with a wavelength less than 420 nm, thereby obtaining visible light. The amount of catalyst used was 0.05 g, the concentration of the sodium pentachlorophenol solution was 20 mg/L, and the volume was 50 mL. It can be seen from the figure that after half an hour of visible light irradiation, the In + doped (001) crystal surface exposed oxygen vacancies BiOCl nanosheets in Example 4 can almost completely degrade sodium pentachlorophenol, and its degradation rate is 6.8 times that of the (001) crystal surface exposed oxygen vacancies BiOCl nanosheets in Example 1, and 27.4 times that of the In 3+ doped (001) crystal surface exposed BiOCl nanosheets in Example 2.
对实施例3,4,5和6中所制备In+掺杂(001)晶面暴露含氧空位BiOCl纳米片样品的光催化活性对比(如图7),可以看出实施例3中紫外光照1小时所制备样品的光催化活性最弱,紫外光照2小时以上的样品可见光下光催化降解杀虫剂五氯酚钠的效率相当,在本实施例所给出的乙二醇与水的比例范围、铋元素与铟元素比例范围和溶解热反应温度范围内,这三个条件的变化对催化活性的影响不明显。The photocatalytic activities of the In + doped (001) crystal plane exposed oxygen vacancies BiOCl nanosheet samples prepared in Examples 3, 4, 5 and 6 are compared (as shown in FIG7 ). It can be seen that the photocatalytic activity of the sample prepared by ultraviolet irradiation for 1 hour in Example 3 is the weakest, and the efficiency of photocatalytic degradation of the pesticide sodium pentachlorophenol under visible light of the samples irradiated with ultraviolet light for more than 2 hours is comparable. Within the range of the ratio of ethylene glycol to water, the range of the ratio of bismuth to indium, and the range of the thermal reaction temperature of dissolution given in this example, the changes in these three conditions have no obvious effect on the catalytic activity.
以上所述,仅是本发明的较佳实施例而已,并非对本发明作任何形式上的限制,虽然本发明已以较佳实施例揭露如上,然而并非用以限定本发明,任何熟悉本专业的技术人员,在不脱离本发明技术方案范围内,当可利用上述揭示的技术内容作出些许更动或修饰为等同变化的等效实施例,但凡是未脱离本发明技术方案内容,依据本发明的技术实质对以上实施例所作的任何简单修改、等同变化与修饰,均仍属于本发明技术方案的范围内。The above description is only a preferred embodiment of the present invention and does not limit the present invention in any form. Although the present invention has been disclosed as a preferred embodiment as above, it is not used to limit the present invention. Any technician familiar with this profession can make some changes or modify the technical contents disclosed above into equivalent embodiments without departing from the scope of the technical solution of the present invention. However, any simple modification, equivalent change and modification made to the above embodiments according to the technical essence of the present invention without departing from the content of the technical solution of the present invention still fall within the scope of the technical solution of the present invention.
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Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104069876A (en) * | 2014-06-24 | 2014-10-01 | 华中师范大学 | Ag-BiOCl compound photocatalyst prepared by depositing nanometer silver on [001] crystal face of BiOCl nanometer sheet and method |
WO2015019348A2 (en) * | 2013-08-05 | 2015-02-12 | Yissum Research Development Company Of The Hebrew University Of Jerusalem Ltd. | Photocatalysts based on bismuth oxyhalide, process for their preparation and uses thereof |
CN108383160A (en) * | 2018-04-11 | 2018-08-10 | 湘潭大学 | A kind of preparation method and applications of metallic element doping BiOCl nanometer sheet materials |
CN112119128A (en) * | 2018-05-16 | 2020-12-22 | 默克专利股份有限公司 | Laser additives and their use in polymeric materials |
CN114832841A (en) * | 2022-04-26 | 2022-08-02 | 西安理工大学 | Preparation method of natural light response bismuth oxyhalide photocatalytic material |
-
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Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2015019348A2 (en) * | 2013-08-05 | 2015-02-12 | Yissum Research Development Company Of The Hebrew University Of Jerusalem Ltd. | Photocatalysts based on bismuth oxyhalide, process for their preparation and uses thereof |
CN104069876A (en) * | 2014-06-24 | 2014-10-01 | 华中师范大学 | Ag-BiOCl compound photocatalyst prepared by depositing nanometer silver on [001] crystal face of BiOCl nanometer sheet and method |
CN108383160A (en) * | 2018-04-11 | 2018-08-10 | 湘潭大学 | A kind of preparation method and applications of metallic element doping BiOCl nanometer sheet materials |
CN112119128A (en) * | 2018-05-16 | 2020-12-22 | 默克专利股份有限公司 | Laser additives and their use in polymeric materials |
CN114832841A (en) * | 2022-04-26 | 2022-08-02 | 西安理工大学 | Preparation method of natural light response bismuth oxyhalide photocatalytic material |
Non-Patent Citations (2)
Title |
---|
"Regulation of band edge and specific surface area of BixInyOCl microsphere for excellent photocatalytic performance";Yanguang Zhang et al.;《Journal of Alloys and Compounds》;第第867卷卷;文献号159052 * |
Regulating the relative content of •O2− and •OH for PCPNa degradation on BiOCl plates with controllable exposed crystal faces and surface oxygenvacancies;Suxiang Ge et al;《Separation and Purification Technology》;第228卷卷;文献号115743 * |
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