CN109985618A - A photocatalytic material, preparation method and application of H-occupied BiVO4-OVs - Google Patents
A photocatalytic material, preparation method and application of H-occupied BiVO4-OVs Download PDFInfo
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- 239000000463 material Substances 0.000 title claims abstract description 66
- 238000002360 preparation method Methods 0.000 title claims abstract description 10
- 230000001699 photocatalysis Effects 0.000 title claims description 83
- PEDCQBHIVMGVHV-UHFFFAOYSA-N Glycerine Chemical compound OCC(O)CO PEDCQBHIVMGVHV-UHFFFAOYSA-N 0.000 claims abstract description 54
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 40
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims abstract description 36
- 239000008367 deionised water Substances 0.000 claims abstract description 36
- 229910021641 deionized water Inorganic materials 0.000 claims abstract description 36
- 238000000034 method Methods 0.000 claims abstract description 25
- 238000001354 calcination Methods 0.000 claims abstract description 7
- 229910002915 BiVO4 Inorganic materials 0.000 claims abstract description 4
- 239000003344 environmental pollutant Substances 0.000 claims description 35
- 231100000719 pollutant Toxicity 0.000 claims description 35
- 239000002243 precursor Substances 0.000 claims description 34
- 238000003756 stirring Methods 0.000 claims description 33
- 238000004729 solvothermal method Methods 0.000 claims description 19
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 17
- 239000001301 oxygen Substances 0.000 claims description 17
- 229910052760 oxygen Inorganic materials 0.000 claims description 17
- 238000006722 reduction reaction Methods 0.000 claims 3
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims 2
- 239000001257 hydrogen Substances 0.000 claims 2
- 229910052739 hydrogen Inorganic materials 0.000 claims 2
- 239000006185 dispersion Substances 0.000 claims 1
- 125000004435 hydrogen atom Chemical group [H]* 0.000 claims 1
- 238000013033 photocatalytic degradation reaction Methods 0.000 claims 1
- 239000000047 product Substances 0.000 abstract description 95
- 230000015556 catabolic process Effects 0.000 abstract description 21
- 238000006731 degradation reaction Methods 0.000 abstract description 21
- 230000003197 catalytic effect Effects 0.000 abstract description 4
- 229910001868 water Inorganic materials 0.000 abstract description 4
- 230000007062 hydrolysis Effects 0.000 abstract description 3
- 238000006460 hydrolysis reaction Methods 0.000 abstract description 3
- 238000006555 catalytic reaction Methods 0.000 abstract 2
- 229910019501 NaVO3 Inorganic materials 0.000 abstract 1
- 239000007795 chemical reaction product Substances 0.000 abstract 1
- 238000001035 drying Methods 0.000 abstract 1
- 230000003287 optical effect Effects 0.000 abstract 1
- CMZUMMUJMWNLFH-UHFFFAOYSA-N sodium metavanadate Chemical compound [Na+].[O-][V](=O)=O CMZUMMUJMWNLFH-UHFFFAOYSA-N 0.000 abstract 1
- 239000002904 solvent Substances 0.000 abstract 1
- 238000005406 washing Methods 0.000 abstract 1
- 239000003054 catalyst Substances 0.000 description 50
- 238000002835 absorbance Methods 0.000 description 34
- 238000001179 sorption measurement Methods 0.000 description 32
- 239000011941 photocatalyst Substances 0.000 description 18
- PYWVYCXTNDRMGF-UHFFFAOYSA-N rhodamine B Chemical compound [Cl-].C=12C=CC(=[N+](CC)CC)C=C2OC2=CC(N(CC)CC)=CC=C2C=1C1=CC=CC=C1C(O)=O PYWVYCXTNDRMGF-UHFFFAOYSA-N 0.000 description 17
- 229940043267 rhodamine b Drugs 0.000 description 17
- 238000006243 chemical reaction Methods 0.000 description 16
- 238000005286 illumination Methods 0.000 description 16
- 239000006228 supernatant Substances 0.000 description 16
- 238000012546 transfer Methods 0.000 description 16
- 238000001132 ultrasonic dispersion Methods 0.000 description 16
- 238000011056 performance test Methods 0.000 description 14
- 238000002441 X-ray diffraction Methods 0.000 description 8
- 238000010521 absorption reaction Methods 0.000 description 8
- 230000031700 light absorption Effects 0.000 description 7
- 238000000137 annealing Methods 0.000 description 4
- 230000007547 defect Effects 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 238000005215 recombination Methods 0.000 description 4
- 230000006798 recombination Effects 0.000 description 4
- 230000003595 spectral effect Effects 0.000 description 4
- 238000001237 Raman spectrum Methods 0.000 description 3
- 238000001878 scanning electron micrograph Methods 0.000 description 3
- 230000009286 beneficial effect Effects 0.000 description 2
- 230000004298 light response Effects 0.000 description 2
- 238000006479 redox reaction Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 238000001069 Raman spectroscopy Methods 0.000 description 1
- 229910052797 bismuth Inorganic materials 0.000 description 1
- JCXGWMGPZLAOME-UHFFFAOYSA-N bismuth atom Chemical compound [Bi] JCXGWMGPZLAOME-UHFFFAOYSA-N 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 230000005264 electron capture Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 230000005284 excitation Effects 0.000 description 1
- 230000002349 favourable effect Effects 0.000 description 1
- 238000013032 photocatalytic reaction Methods 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 238000001392 ultraviolet--visible--near infrared spectroscopy Methods 0.000 description 1
- LSGOVYNHVSXFFJ-UHFFFAOYSA-N vanadate(3-) Chemical compound [O-][V]([O-])([O-])=O LSGOVYNHVSXFFJ-UHFFFAOYSA-N 0.000 description 1
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- B01J35/30—Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
- B01J35/39—Photocatalytic properties
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- C02F1/30—Treatment of water, waste water, or sewage by irradiation
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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Abstract
Description
技术领域technical field
本发明涉及光催化材料技术领域,特别涉及一种制备H占据含氧空位的BiVO4(BiVO4-OVs)光催化材料的方法及其应用。The invention relates to the technical field of photocatalytic materials, in particular to a method for preparing a BiVO 4 (BiVO 4 -OVs) photocatalytic material in which H occupies an oxygen-containing vacancy and its application.
背景技术Background technique
随着环境污染和能源短缺问题逐渐加剧,光催化技术因其通过太阳光作为能量输入,具有清洁环保、成本低廉、能量巨大等优势,在光解水制氢和降解污染物等方面影响巨大,引起了科学家们的广泛关注,具有良好的发展前景。然而,光催化技术仍然受限于两个影响因素,即光谱响应范围窄和量子效率低,因此,如何拓宽光谱吸收,提高太阳能利用率,抑制光生电子-空穴的快速复合,成为当前研究的核心与关键。With the gradual increase of environmental pollution and energy shortage, photocatalytic technology has the advantages of cleanness, environmental protection, low cost and huge energy due to the use of sunlight as energy input. It has attracted extensive attention of scientists and has good prospects for development. However, photocatalytic technology is still limited by two influencing factors, namely narrow spectral response range and low quantum efficiency. Therefore, how to broaden spectral absorption, improve solar energy utilization, and suppress the rapid recombination of photogenerated electrons and holes has become the current research topic. core and key.
钒酸铋(BiVO4)的禁带宽度为2.3-2.4eV,其价带位置足够高,可实现空穴对有机物的降解。导带位置有利于光生电子的还原,可在可见光下分解水和降解污染物,边缘非常接近H2演化电位,具有起始电位低、光电流密度高等优点,被认为是最有前途的光电化学(PEC)水分解光阳极材料之一。但由于载流子的扩散长度短,光生电子和空穴容易复合,使光电催化性能降低,成为限制BiVO4广泛应用的重要因素。The forbidden band width of bismuth vanadate (BiVO 4 ) is 2.3-2.4 eV, and its valence band position is high enough to realize the degradation of organics by holes. The conduction band position is favorable for the reduction of photogenerated electrons, which can split water and degrade pollutants under visible light, and the edge is very close to the H evolution potential. (PEC) one of the water-splitting photoanode materials. However, due to the short diffusion length of carriers, the photogenerated electrons and holes are easily recombined, which reduces the photoelectric catalytic performance and becomes an important factor limiting the wide application of BiVO4 .
发明内容SUMMARY OF THE INVENTION
为了克服上述现有技术的不足,本发明的目的在于提供一种制备H占据BiVO4-OVs光催化材料的方法及其应用,H占据BiVO4-OVs光催化材料带隙缩小,光吸收提高,吸光范围增宽,具有优异的光催化性能。In order to overcome the above-mentioned deficiencies of the prior art, the purpose of the present invention is to provide a method for preparing a H-occupied BiVO 4 -OVs photocatalytic material and its application . The light absorption range is widened, and it has excellent photocatalytic performance.
为了实现上述目的,本发明采用的技术方案是:In order to achieve the above object, the technical scheme adopted in the present invention is:
一种制备H占据BiVO4-OVs光催化材料的方法,包括以下步骤:A method for preparing H-occupied BiVO 4 -OVs photocatalytic material, comprising the following steps:
步骤一:step one:
将一定摩尔量的Bi(NO3)3·5 H2O溶解在甘油中得到前驱体溶液A;Dissolving a certain molar amount of Bi(NO 3 ) 3 ·5 H 2 O in glycerol to obtain precursor solution A;
步骤二:Step 2:
将一定摩尔量NaVO3·2 H2O溶解在去离子水中得到前驱体溶液B;The precursor solution B was obtained by dissolving a certain molar amount of NaVO 3 ·2 H 2 O in deionized water;
步骤三:Step 3:
将溶液A加入溶液B并剧烈搅拌,得到溶液C;Add solution A to solution B and stir vigorously to obtain solution C;
步骤四:Step 4:
将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;The solution C was transferred to a polytetrafluoroethylene-lined autoclave and kept at 180 °C for 8 h to obtain the synthetic product D;
步骤五:Step 5:
将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
步骤六:Step 6:
产物E在马弗炉内300 ℃煅烧5 h得到产物F;Product E was calcined in a muffle furnace at 300 °C for 5 h to obtain product F;
步骤七:Step seven:
产物F在Ar/H2气氛中在350 ℃温度下退火10 h得到H占据BiVO4-OVs光催化材料。The product F was annealed at 350 °C for 10 h in Ar/H 2 atmosphere to obtain H-occupied BiVO 4 -OVs photocatalytic materials.
所述步骤四中溶剂热的温度范围为120 ℃~200 ℃。The temperature range of solvothermal in the fourth step is 120°C to 200°C.
所述步骤四中溶剂热的反应时间范围为6~12 h。In the fourth step, the solvothermal reaction time ranges from 6 to 12 h.
所述步骤六中煅烧温度范围为250 ℃~450 ℃。In the step 6, the calcination temperature ranges from 250°C to 450°C.
所述煅烧时间范围为5 h~24 h。The calcination time ranges from 5 h to 24 h.
所述步骤七中退火温度范围为300 ℃~400 ℃。In the seventh step, the annealing temperature ranges from 300°C to 400°C.
所述步骤七中退火时间范围为5h~12 h。In the seventh step, the annealing time ranges from 5 h to 12 h.
所述步骤七中Ar/H2比例范围为95 %:5 %~70 %:30 %。In the seventh step, the ratio of Ar/H 2 ranges from 95%: 5% to 70%: 30%.
H占据BiVO4-OVs光催化材料应用于光催化技术,如污染物降解、光分解水等。以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B(RhB)溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。H-occupied BiVO 4 -OVs photocatalytic materials are applied in photocatalytic technologies, such as pollutant degradation, photo-splitting of water, etc. A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B (RhB) solution, add 20 ml of catalyst and carry out ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
本发明的有益效果:Beneficial effects of the present invention:
采用溶剂热-后期退火方法,制备出H占据BiVO4-OVs光催化材料。该复合材料中氧空位可以吸收近红外光,增加活性位点并且将氧分子转化成活性物质参与氧化还原反应;在BiVO4的导带下方形成缺陷态,使其禁带宽度减小,提高催化剂光吸收范围;同时,作为光生电子捕获中心,在长波长的激发下能够有效分离电子-空穴对并将其转移至催化剂表面,抑制光生电子和空穴的复合,提高光催化效率。在BiVO4-OVs中引入H2,被H占据O空位的价带作为缺陷能级或浅施主能级,带隙宽度减少,光吸收范围增大,吸光度显著提高。作为光催化材料具有电荷分离率高、光吸收范围广、光催化活性高、降解速率快、水解能力强的优势。H-occupied BiVO 4 -OVs photocatalytic materials were prepared by a solvothermal-post-annealing method. Oxygen vacancies in the composite material can absorb near-infrared light, increase active sites and convert oxygen molecules into active species to participate in redox reactions; defect states are formed under the conduction band of BiVO 4 to reduce the forbidden band width and improve the catalyst. At the same time, as a photogenerated electron capture center, it can effectively separate electron-hole pairs and transfer them to the catalyst surface under long-wavelength excitation, inhibit the recombination of photogenerated electrons and holes, and improve the photocatalytic efficiency. When H 2 is introduced into BiVO 4 -OVs, the valence band of O vacancies occupied by H acts as a defect level or shallow donor level, the band gap width is reduced, the light absorption range is enlarged, and the absorbance is significantly improved. As a photocatalytic material, it has the advantages of high charge separation rate, wide light absorption range, high photocatalytic activity, fast degradation rate and strong hydrolysis ability.
附图说明Description of drawings
图1为H占据BiVO4-OVs光催化材料制备过程示意图;Figure 1 is a schematic diagram of the preparation process of H-occupied BiVO 4 -OVs photocatalytic material;
图2为H占据BiVO4-OVs光催化材料的XRD图像;Figure 2 is the XRD pattern of H occupied BiVO 4 -OVs photocatalytic material;
图3为H占据BiVO4-OVs光催化材料的SEM图像;Figure 3 is the SEM image of H occupied BiVO 4 -OVs photocatalytic material;
图4为H占据BiVO4-OVs光催化材料的拉曼光谱图像;Figure 4 is a Raman spectrum image of H occupied BiVO 4 -OVs photocatalytic material;
图5为H占据BiVO4-OVs光催化材料的紫外可见近红外吸收图像。Figure 5 shows the UV-Vis-NIR absorption images of H-occupied BiVO 4 -OVs photocatalytic material.
具体实施方式Detailed ways
下面结合附图对本发明作进一步详细说明。The present invention will be further described in detail below in conjunction with the accompanying drawings.
实施例1Example 1
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,120 ℃保持6 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 120 °C for 6 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内300 ℃煅烧5 h得到产物F;(6) Product E was calcined in a muffle furnace at 300 °C for 5 h to obtain product F;
(7)产物F在Ar/H2气氛中在350 ℃, Ar/H2( Vol: 95%: 5%)气氛下退火10 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 350 ℃, Ar/H 2 (Vol: 95%: 5%) atmosphere for 10 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料光催化性能测试方法如下:The photocatalytic performance test method of the obtained H-occupied BiVO 4 -OVs photocatalytic material is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例2Example 2
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内300 ℃煅烧5 h得到产物F;(6) Product E was calcined in a muffle furnace at 300 °C for 5 h to obtain product F;
(7)产物F在Ar/H2气氛中在350 ℃, Ar/H2( Vol: 95%: 5%)气氛下退火10 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 350 ℃, Ar/H 2 (Vol: 95%: 5%) atmosphere for 10 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料,记作OVH-BiVO4,其光催化性能测试方法如下:The obtained H-occupied BiVO 4 -OVs photocatalytic material is denoted as OV H -BiVO 4 , and its photocatalytic performance test method is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例3Example 3
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持10 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 10 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内300 ℃煅烧5 h得到产物F;(6) Product E was calcined in a muffle furnace at 300 °C for 5 h to obtain product F;
(7)产物F在Ar/H2气氛中在350 ℃,Ar/H2( Vol: 95%: 5%)气氛下退火10 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 350 ℃, Ar/H 2 (Vol: 95%: 5%) atmosphere for 10 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料光催化性能测试方法如下:The photocatalytic performance test method of the obtained H-occupied BiVO 4 -OVs photocatalytic material is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例4Example 4
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,200 ℃保持12 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 200 °C for 12 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内300 ℃煅烧5 h得到产物F;(6) Product E was calcined in a muffle furnace at 300 °C for 5 h to obtain product F;
(7)产物F在Ar/H2气氛中在350 ℃, Ar/H2( Vol: 95%: 5%)气氛下退火10 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 350 ℃, Ar/H 2 (Vol: 95%: 5%) atmosphere for 10 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料光催化性能测试方法如下:The photocatalytic performance test method of the obtained H-occupied BiVO 4 -OVs photocatalytic material is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例5Example 5
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内250 ℃煅烧5 h得到产物F;(6) Product E was calcined in a muffle furnace at 250 °C for 5 h to obtain product F;
(7)产物F在Ar/H2气氛中在350 ℃, Ar/H2( Vol: 95%: 5%)气氛下退火10 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 350 ℃, Ar/H 2 (Vol: 95%: 5%) atmosphere for 10 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料光催化性能测试方法如下:The photocatalytic performance test method of the obtained H-occupied BiVO 4 -OVs photocatalytic material is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例6Example 6
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内300 ℃煅烧5 h得到产物F;(6) Product E was calcined in a muffle furnace at 300 °C for 5 h to obtain product F;
(7)产物F在Ar/H2气氛中在350 ℃, Ar/H2( Vol: 95%: 5%)气氛下退火10 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 350 ℃, Ar/H 2 (Vol: 95%: 5%) atmosphere for 10 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料光催化性能测试方法如下:The photocatalytic performance test method of the obtained H-occupied BiVO 4 -OVs photocatalytic material is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例7Example 7
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内350 ℃煅烧10 h得到产物F;(6) Product E was calcined in a muffle furnace at 350 °C for 10 h to obtain product F;
(7)产物F在Ar/H2气氛中在350 ℃, Ar/H2( Vol: 95%: 5%)气氛下退火10 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 350 ℃, Ar/H 2 (Vol: 95%: 5%) atmosphere for 10 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料光催化性能测试方法如下:The photocatalytic performance test method of the obtained H-occupied BiVO 4 -OVs photocatalytic material is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例8Example 8
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内450 ℃煅烧12 h得到产物F;(6) Product E was calcined in a muffle furnace at 450 °C for 12 h to obtain product F;
(7)产物F在Ar/H2气氛中在350 ℃, Ar/H2( Vol: 95%: 5%)气氛下退火10 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 350 ℃, Ar/H 2 (Vol: 95%: 5%) atmosphere for 10 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料光催化性能测试方法如下:The photocatalytic performance test method of the obtained H-occupied BiVO 4 -OVs photocatalytic material is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例9Example 9
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内300 ℃煅烧5 h得到产物F;(6) Product E was calcined in a muffle furnace at 300 °C for 5 h to obtain product F;
(7)产物F在Ar/H2气氛中在300 ℃, Ar/H2( Vol: 95%: 5%)气氛下退火5 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 300 ℃, Ar/H 2 (Vol: 95%: 5%) atmosphere for 5 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料光催化性能测试方法如下:The photocatalytic performance test method of the obtained H-occupied BiVO 4 -OVs photocatalytic material is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例10Example 10
(1)将2.0 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 2.0 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内300 ℃煅烧5 h得到产物F;(6) Product E was calcined in a muffle furnace at 300 °C for 5 h to obtain product F;
(7)产物F在Ar/H2气氛中在350 ℃, Ar/H2( Vol: 95%: 5%)气氛下退火10 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 350 ℃, Ar/H 2 (Vol: 95%: 5%) atmosphere for 10 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料光催化性能测试方法如下:The photocatalytic performance test method of the obtained H-occupied BiVO 4 -OVs photocatalytic material is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例11Example 11
(1)将1.2mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 1.2 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内300 ℃煅烧5 h得到产物F;(6) Product E was calcined in a muffle furnace at 300 °C for 5 h to obtain product F;
(7)产物F在Ar/H2气氛中在400 ℃, Ar/H2( Vol: 90%: 10%)气氛下退火12 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 400 ℃, Ar/H 2 (Vol: 90%: 10%) atmosphere for 12 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料光催化性能测试方法如下:The photocatalytic performance test method of the obtained H-occupied BiVO 4 -OVs photocatalytic material is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例12Example 12
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内300 ℃煅烧5 h得到产物F;(6) Product E was calcined in a muffle furnace at 300 °C for 5 h to obtain product F;
(7)产物F在Ar/H2气氛中在350 ℃, Ar/H2( Vol: 80%: 20%)气氛下退火10 h得到H占据BiVO4-OVs光催化材料。(7) The product F was annealed in Ar/H 2 atmosphere at 350 ℃, Ar/H 2 (Vol: 80%: 20%) atmosphere for 10 h to obtain H-occupied BiVO 4 -OVs photocatalytic material.
所得H占据BiVO4-OVs光催化材料光催化性能测试方法如下:The photocatalytic performance test method of the obtained H-occupied BiVO 4 -OVs photocatalytic material is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken each time were separated from the photocatalyst and the solution by a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例13Example 13
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
所得产物E未经过马弗炉煅烧,未在Ar/H2还原气氛下退火,记作OV'-BiVO4,其光催化性能测试方法如下:The obtained product E is not calcined in a muffle furnace, nor annealed in an Ar/H 2 reducing atmosphere, and is denoted as OV'-BiVO 4 . The photocatalytic performance test method is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例14Example 14
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在马弗炉内300 ℃煅烧5 h得到产物F;(6) Product E was calcined in a muffle furnace at 300 °C for 5 h to obtain product F;
所得产物F未在Ar/H2还原气氛下退火,记作OV-BiVO4,其光催化性能测试方法如下:The obtained product F was not annealed under the Ar/H 2 reducing atmosphere, and was denoted as OV-BiVO 4 , and its photocatalytic performance test method was as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
实施例15Example 15
(1)将0.4 mmol Bi(NO3)3·5 H2O溶解于16 ml甘油得到前驱体溶液A;(1) Dissolve 0.4 mmol Bi(NO 3 ) 3 ·5 H 2 O in 16 ml of glycerol to obtain precursor solution A;
(2)将0.4 mmol NaVO3·2 H2O溶解于16 ml去离子水得到前驱体溶液B;(2) Dissolve 0.4 mmol NaVO 3 ·2 H 2 O in 16 ml deionized water to obtain precursor solution B;
(3)将溶液A加入溶液B并剧烈搅拌,得到溶液C;(3) Add solution A to solution B and stir vigorously to obtain solution C;
(4)将溶液C转移到聚四氟乙烯内衬的高压釜中,180 ℃保持8 h后得到合成产物D;(4) Transfer solution C to a polytetrafluoroethylene-lined autoclave, and keep it at 180 °C for 8 h to obtain synthetic product D;
(5)将溶剂热合成产物D经过10000 rpm离心分离,去离子水和乙醇洗涤,60 ℃烘干4 h后得到产物E;(5) The solvothermal synthesis product D was centrifuged at 10,000 rpm, washed with deionized water and ethanol, and dried at 60 °C for 4 h to obtain product E;
(6)产物E在Ar/H2气氛中在350 ℃, Ar/H2( Vol: 80%: 20%)气氛下退火10 h得到H占据BiVO4-OVs光催化材料。(6) The product E was annealed in Ar/H 2 atmosphere at 350 ℃, Ar/H 2 (Vol: 80%: 20%) atmosphere for 10 h to obtain H-occupied BiVO 4 -OVs photocatalytic materials.
所得产物E未经过马弗炉煅烧,记作OVH'-BiVO4,其光催化性能测试方法如下:The obtained product E is not calcined in a muffle furnace, and is denoted as OV H '-BiVO 4 , and its photocatalytic performance testing method is as follows:
以300 W的Xe灯为光源,用小于800 nm波长的截止滤光片模拟太阳光。量取50 ml罗丹明B溶液,加入20 ml催化剂并进行超声分散。在光照前,在黑暗中吸附搅拌30 min使催化剂与污染物达到吸附平衡。开灯后,每隔固定20 min从反应容器中取4 mL样品。每次取出的样品用10000 r/min的高速离心机将光催化剂与溶液分离,取上层清液,用紫外-可见分光光度计测定Rh B的吸光度,根据吸光度来判断催化剂对污染物溶液的降解效率。A 300 W Xe lamp was used as the light source, and sunlight was simulated with a cut-off filter with wavelengths less than 800 nm. Measure 50 ml of Rhodamine B solution, add 20 ml of catalyst and perform ultrasonic dispersion. Before illumination, adsorption and stirring were carried out in the dark for 30 min to make the catalyst and pollutants reach the adsorption equilibrium. After the light was turned on, 4 mL samples were taken from the reaction vessel every fixed 20 min. The samples taken out each time were separated from the photocatalyst and the solution with a high-speed centrifuge at 10,000 r/min, the supernatant was taken, and the absorbance of Rh B was measured with a UV-Vis spectrophotometer, and the degradation of the catalyst to the pollutant solution was judged according to the absorbance. efficiency.
参见图2,图2为H占据BiVO4-OVs光催化材料的XRD图像。图中:a. 是否经过马弗炉煅烧的未加H的BiVO4的XRD图像,即实施例13与实施例14所制样品的XRD图像; b. 是否经过马弗炉煅烧的加H的BiVO4的XRD图像,即实施例15与实施例2所制样品的XRD图像: c. 未经过马弗炉煅烧的加H前后的BiVO4的XRD图像,即实施例15与实施例13所制样品的XRD图像: d. 经过马弗炉煅烧的加H前后的含有氧空位的BiVO4的XRD图像,即实施例2与实施例14所制样品的XRD图像。Referring to FIG. 2, FIG. 2 is an XRD image of the H-occupied BiVO 4 -OVs photocatalytic material. In the figure: a. Whether or not the XRD pattern of BiVO 4 without H added after being calcined in a muffle furnace, that is, the XRD images of the samples prepared in Example 13 and Example 14; b. XRD patterns of 4 , namely the XRD patterns of the samples prepared in Example 15 and Example 2: c. The XRD patterns of BiVO 4 before and after adding H without muffle furnace calcination, namely the samples prepared in Example 15 and Example 13 XRD patterns of: d. The XRD patterns of BiVO 4 containing oxygen vacancies before and after adding H after muffle furnace calcination, namely the XRD patterns of the samples prepared in Example 2 and Example 14.
参见图3,图3为H占据BiVO4-OVs光催化材料的SEM图像,即实施例2所制得OVH-BiVO4光催化材料的SEM图像;可明显观察到样品形貌明显且尺寸均一,半径尺寸在500~600nm左右,呈桑葚状结构,表面粗糙,为光催化反应提供了更多反应活性位点,有利于光生电子的捕获。Referring to Figure 3, Figure 3 is the SEM image of the BiVO 4 -OVs photocatalytic material occupied by H, that is, the SEM image of the OV H -BiVO 4 photocatalytic material prepared in Example 2; it can be clearly observed that the sample has an obvious morphology and uniform size , with a radius of about 500-600 nm, with a mulberry-like structure and a rough surface, which provides more reactive sites for photocatalytic reactions and is conducive to the capture of photogenerated electrons.
参见图4,图4为H占据BiVO4-OVs光催化材料的拉曼光谱图像,即实施例2、实施例13、实施例14、实施例15所制得H占据BiVO4-OVs光催化材料的拉曼光谱图像;可观察到存在氧空位的OV-BiVO4相较BiVO4峰位一致,峰值降低,可证明氧空位的存在。同时,H占据BiVO4-OVs即OVH-BiVO4相较于OV-BiVO4峰值明显降低,说明H部分或完全占据氧空位。通过拉曼光谱可证明氧空位的存在,也可证明H能够部分或完全占据氧空位。Referring to FIG. 4 , FIG. 4 is a Raman spectrum image of the H-occupied BiVO 4 -OVs photocatalytic material, namely the H-occupied BiVO 4 -OVs photocatalytic materials prepared in Example 2, Example 13, Example 14, and Example 15 The Raman spectrum image of ; it can be observed that the peak position of OV-BiVO 4 with oxygen vacancies is the same as that of BiVO 4 , and the peak is lower, which can prove the existence of oxygen vacancies. At the same time, the peak of H occupied BiVO 4 -OVs, namely OV H -BiVO 4 , was significantly lower than that of OV-BiVO 4 , indicating that H partially or completely occupied oxygen vacancies. The existence of oxygen vacancies can be proved by Raman spectroscopy, and it can also be proved that H can partially or completely occupy the oxygen vacancies.
参见图5,图5为H占据BiVO4-OVs光催化材料的紫外可见近红外吸收图像,即实施例2、实施例13、实施例14、实施例15所制得H占据BiVO4-OVs光催化材料的紫外可见近红外吸收图像;由图中可观察到BiVO4在500 nm可见光以内有明显吸收;OV-BiVO4相较于BiVO4出现红移现象,可见光吸收范围增加,证明氧空位有利于扩大光响应范围;未经马弗炉煅烧、经过H2退火的OVH'-BiVO4在200~2500 nm全光谱范围均有吸收,且吸收率达到0.4以上;经过马弗炉煅烧、经过H2退火的OVH-BiVO4在200~2500 nm全光谱范围吸收率可达0.9以上,具有更宽的光吸收范围和更强的光吸收能力,光催化活性显著提高。Referring to FIG. 5 , FIG. 5 is the UV-visible-near-infrared absorption image of the H-occupied BiVO 4 -OVs photocatalytic material, that is, the H-occupied BiVO 4 -OVs light prepared in Example 2, Example 13, Example 14, and Example 15 Ultraviolet-visible-near-infrared absorption image of the catalytic material; it can be observed that BiVO 4 has obvious absorption within 500 nm visible light; OV-BiVO 4 has a red-shift phenomenon compared with BiVO 4 , and the visible light absorption range increases, which proves that oxygen vacancies have It is beneficial to expand the light response range; OV H '-BiVO 4 without muffle furnace calcination and H 2 annealing has absorption in the full spectral range of 200-2500 nm, and the absorption rate reaches more than 0.4; The H 2 annealed OV H -BiVO 4 has an absorptivity of over 0.9 in the full spectral range of 200-2500 nm, with a wider light absorption range and stronger light absorption capacity, and the photocatalytic activity is significantly improved.
由以上实施例可以看出本发明提供的一种制备H占据BiVO4-OVs光催化剂材料制备方法步骤简单,制备的H占据BiVO4-OVs光催化剂材料光响应范围增大、载流子分离率提高,作为光催化材料具有催化活性高、降解速率快、水解能力强的优势,为太阳能的高效利用提供新思路。It can be seen from the above examples that the preparation method of the H-occupied BiVO 4 -OVs photocatalyst material provided by the present invention has simple steps, and the prepared H-occupied BiVO 4 -OVs photocatalyst material has an increased light response range and a carrier separation rate. As a photocatalytic material, it has the advantages of high catalytic activity, fast degradation rate, and strong hydrolysis ability, providing new ideas for the efficient utilization of solar energy.
H占据BiVO4-OVs技术为解决BiVO4的带隙问题和载流子复合问题提供了机遇,粗糙多孔的BiVO4有助于吸附更多电子进行氧化还原反应,引入氧空位缺陷后,氧空位吸收近红外光,增大吸光范围,活性位点增加。H占据O空位后产生新的缺陷能级或浅施主能级,带隙宽度减少,光吸收范围增大,吸光度有较大改善,光催化活性显著提高。制备H占据BiVO4-OVs光催化材料是解决光催化材料带隙较宽、光响应范围窄、电子-空穴极易复合的有效方法和可靠途径。The H-occupied BiVO 4 -OVs technology provides an opportunity to solve the band gap problem and carrier recombination problem of BiVO 4 , the rough and porous BiVO 4 helps to adsorb more electrons for redox reaction, and after the introduction of oxygen vacancy defects, the oxygen vacancies Absorb near-infrared light, increase the absorption range, and increase the active site. After H occupies the O vacancy, a new defect level or shallow donor level is generated, the band gap width is reduced, the light absorption range is increased, the absorbance is greatly improved, and the photocatalytic activity is significantly improved. The preparation of H-occupied BiVO 4 -OVs photocatalytic materials is an effective and reliable way to solve the problems of wide band gap, narrow photoresponse range and easy electron-hole recombination of photocatalytic materials.
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