[go: up one dir, main page]
More Web Proxy on the site http://driver.im/

CN111659411B - Preparation and application of rare earth cerium doped iron molybdate photocatalyst - Google Patents

Preparation and application of rare earth cerium doped iron molybdate photocatalyst Download PDF

Info

Publication number
CN111659411B
CN111659411B CN202010664065.1A CN202010664065A CN111659411B CN 111659411 B CN111659411 B CN 111659411B CN 202010664065 A CN202010664065 A CN 202010664065A CN 111659411 B CN111659411 B CN 111659411B
Authority
CN
China
Prior art keywords
rare earth
photocatalyst
iron molybdate
doped iron
moo
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN202010664065.1A
Other languages
Chinese (zh)
Other versions
CN111659411A (en
Inventor
莫尊理
贾倩倩
裴贺兵
姜洋洋
张红娟
郭瑞斌
刘妮娟
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Northwest Normal University
Original Assignee
Northwest Normal University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Northwest Normal University filed Critical Northwest Normal University
Priority to CN202010664065.1A priority Critical patent/CN111659411B/en
Publication of CN111659411A publication Critical patent/CN111659411A/en
Application granted granted Critical
Publication of CN111659411B publication Critical patent/CN111659411B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/85Chromium, molybdenum or tungsten
    • B01J23/88Molybdenum
    • B01J23/887Molybdenum containing in addition other metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/8871Rare earth metals or actinides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/50Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
    • B01J35/51Spheres
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/61Surface area
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/40Organic compounds containing sulfur
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Catalysts (AREA)

Abstract

The invention provides a preparation method and application of rare earth cerium doped iron molybdate photocatalyst, which is prepared by mixing Fe (NO)3)・9H2Dissolving O in deionized water, adding Ce (NO) at room temperature3)3To obtain Fe (NO)3)・9H2O and Ce (NO)3)3The mixed solution of (1); will be (NH)4)6Mo7O24・4H2O is dissolved in deionized water and added dropwise to Fe (NO)3)・9H2O and Ce (NO)3)3Stirring the mixed solution, adding ammonia water to adjust the pH value to 3-4, reacting for 12-13 h at 180-185 ℃, centrifugally washing and drying to obtain the rare earth cerium doped iron molybdate photocatalyst Ce-Fe2(MoO4)3. The cerium-doped iron molybdate prepared by the invention is in a uniform nano spherical structure and has a larger specific surface area; meanwhile, the doping of the rare earth element can effectively reduce the photoproduction electron-hole recombination rate of the photocatalyst, can improve the specific surface area of the photocatalyst to a certain extent, is beneficial to improving the photocatalytic efficiency, and ensures that the Ce-Fe photocatalyst is prepared by adding the rare earth element into the photocatalyst2(MoO4)3Has wide application prospect in the field of photocatalytic dye wastewater treatment.

Description

一种稀土铈掺杂钼酸铁光催化剂的制备及应用Preparation and application of a rare earth cerium doped iron molybdate photocatalyst

技术领域technical field

本发明涉及一种稀土铈掺杂钼酸铁光催化剂(Ce-Fe2(MoO4)3)的制备方法,尤其涉及一种纳米球状结构铈掺杂钼酸铁(Ce-Fe2(MoO4)3)的制备方法,制备的稀土铈掺杂钼酸铁光催化剂用于染料废水中有机污染物的光催化降解,属于材料制备领域及光催化应用领域。The invention relates to a preparation method of a rare earth cerium-doped iron molybdate photocatalyst (Ce-Fe 2 (MoO 4 ) 3 ), in particular to a nano-spherical structure cerium-doped iron molybdate (Ce-Fe 2 (MoO 4 ) ) 3 ) preparation method, the prepared rare earth cerium doped iron molybdate photocatalyst is used for photocatalytic degradation of organic pollutants in dye wastewater, belonging to the field of material preparation and the field of photocatalysis application.

背景技术Background technique

钼酸铁(Fe2(MoO4)3)具有响应紫外可见光、比表面能高、可选择性、外露活性强等优异性能。更值得人们所关注的是,在钼酸铁中钼酸本身就具有催化性能,而且铁也具有催化性能,因此,二者之间可达到协同催化的效果,使得钼酸铁的催化性能更强。由于Fe2(MoO4)3具有催化、光学和磁性等优异性质,这使得钼酸铁在催化剂、磁性材料和光学纤维等领域的应用前景比较广阔。Iron molybdate (Fe 2 (MoO 4 ) 3 ) has excellent properties such as response to ultraviolet and visible light, high specific surface energy, selectivity, and strong exposure activity. What is more worthy of attention is that in iron molybdate, molybdate itself has catalytic properties, and iron also has catalytic properties. Therefore, a synergistic catalytic effect can be achieved between the two, making iron molybdate stronger catalytic performance. . Due to the excellent properties of Fe 2 (MoO 4 ) 3 such as catalysis, optics and magnetism, Fe 2 (MoO 4 ) 3 has broad application prospects in the fields of catalysts, magnetic materials and optical fibers.

我国稀土资源储量丰富,其中铈元素的丰量最高、最为廉价,同时铈元素因具有独特的4f1,5d1,6S2 电子排布结构,故而可以+4 价,亦可以+3价形式稳定存在,价态不同会影响原子的配位结构,铈元素这种独特的价态配置为其材料性能的提升大有助益。材料的形貌,尺寸,比表面积和氧空位共同影响其光催化性能,其中氧缺陷与铈离子的电子结构有关,不同价态铈离子的转变过程中,伴随着O2的存储和释放,释放的同时形成氧空位可直接参与反应,故而表现出氧化还原性能,同时铈元素的掺杂能够有效的降低光催化剂的光生电子-空穴复合率,所以铈元素掺杂到钼酸铁中能够显著的提升其光催化性能。China is rich in rare earth resources, among which cerium is the most abundant and cheapest element. At the same time, cerium has a unique 4f 1 , 5d 1 , 6S 2 electronic arrangement structure, so it can be stable in the form of +4 or +3. The existence of different valence states will affect the coordination structure of atoms, and the unique valence state configuration of cerium element is of great help to the improvement of its material properties. The morphology, size, specific surface area and oxygen vacancies of the material together affect its photocatalytic performance, in which oxygen vacancies are related to the electronic structure of cerium ions, and the transition process of cerium ions in different valence states is accompanied by the storage and release of O2 , the release At the same time, the formation of oxygen vacancies can directly participate in the reaction, so it exhibits redox performance. At the same time, the doping of cerium can effectively reduce the photo-generated electron-hole recombination rate of the photocatalyst, so the doping of cerium into iron molybdate can significantly to enhance its photocatalytic performance.

发明内容SUMMARY OF THE INVENTION

本发明的目的是提供一种稀土铈掺杂钼酸铁光催化剂的制备方法及应用。The purpose of the present invention is to provide a preparation method and application of a rare earth cerium doped iron molybdate photocatalyst.

一、稀土铈掺杂钼酸铁光催化剂(Ce-Fe2(MoO4)3)的制备1. Preparation of rare earth cerium-doped iron molybdate photocatalyst (Ce-Fe 2 (MoO 4 ) 3 )

本发明稀土铈掺杂钼酸铁光催化剂的制备方法,是将Fe(NO3)・9H2O溶解于去离子水中,室温下加入Ce(NO3)3,得到Fe(NO3)・9H2O和Ce(NO3)3的混合溶液;将(NH4)6Mo7O24・4H2O溶解于去离子水中并将其滴加到Fe(NO3)・9H2O和Ce(NO3)3混合溶液中,25℃水浴下持续搅拌4~6h,加入氨水调节pH至3~4,于180~185℃下反应12~13h,离心洗涤,80~85℃下干燥,即得稀土铈掺杂钼酸铁光催化剂Ce-Fe2(MoO4)3。其中,Ce(NO3)3和Fe(NO3)・9H2O的摩尔比为0.01~0.06:1;Fe(NO3)・9H2O和(NH4)6Mo7O24・4H2O的摩尔比为1:0.2~1:0.25。The preparation method of the rare earth cerium doped iron molybdate photocatalyst of the present invention is that Fe(NO 3 )·9H 2 O is dissolved in deionized water, and Ce(NO 3 ) 3 is added at room temperature to obtain Fe(NO 3 )·9H Mixed solution of 2 O and Ce(NO 3 ) 3 ; (NH 4 ) 6 Mo 7 O 24 ·4H 2 O was dissolved in deionized water and added dropwise to Fe(NO 3 )·9H 2 O and Ce( NO 3 ) 3 mixed solution, continue stirring for 4~6h in a water bath at 25°C, add ammonia water to adjust the pH to 3~4, react at 180~185°C for 12~13h, wash by centrifugation, and dry at 80~85°C to obtain Rare earth cerium doped iron molybdate photocatalyst Ce-Fe 2 (MoO 4 ) 3 . Among them, the molar ratio of Ce(NO 3 ) 3 and Fe(NO 3 )·9H 2 O is 0.01~0.06:1; Fe(NO 3 )·9H 2 O and (NH 4 ) 6 Mo 7 O 24 ·4H 2 The molar ratio of O is 1:0.2~1:0.25.

二、稀土铈掺杂钼酸铁(Ce-Fe2(MoO4)3)的形貌2. Morphology of rare earth cerium doped iron molybdate (Ce-Fe 2 (MoO 4 ) 3 )

1、扫描电镜分析1. Scanning electron microscope analysis

图1为本发明制备的稀土铈掺杂钼酸铁(Ce-Fe2(MoO4)3)Ce掺杂量为2%和钼酸铁(Fe2(MoO4)3)的扫描电镜图。从图1A中可以看到,稀土铈掺杂钼酸铁(Ce-Fe2(MoO4)3)呈均匀纳米颗粒状,具有较大比表面积、其粒径可达110-220nm。由图1B可以看出,钼酸铁(Fe2(MoO4)3)为纳米片组装的微米花。FIG. 1 is a scanning electron microscope image of rare earth cerium-doped iron molybdate (Ce-Fe 2 (MoO 4 ) 3 ) with a Ce doping content of 2% and iron molybdate (Fe 2 (MoO 4 ) 3 ) prepared by the present invention. It can be seen from FIG. 1A that the rare earth cerium doped iron molybdate (Ce-Fe 2 (MoO 4 ) 3 ) is in the form of uniform nanoparticles, with a large specific surface area and a particle size of 110-220 nm. It can be seen from Fig. 1B that iron molybdate (Fe 2 (MoO 4 ) 3 ) is a microflower assembled by nanosheets.

2、XRD分析2. XRD analysis

图2为本发明制备的纯钼酸铁、稀土铈掺杂钼酸铁(Ce-Fe2(MoO4)3):1%-Ce、稀土铈掺杂钼酸铁(Ce-Fe2(MoO4)3):2%-Ce的XRD图,由图可知所有衍射峰均于标准卡片PDF#35-0183衍射峰相一致,表明样品合成成功。掺杂稀土元素铈之后并没有额外的衍射峰出现,这表明Fe2(MoO4)3在引入稀土离子之后晶体结构没有发生变化。引入稀土元素掺杂之后的Fe2(MoO4)3的XRD 峰相较于没有稀土元素掺杂的Fe2(MoO4)3,其部分峰位发生位移,这可能是因为稀土元素离子的掺入,取代了催化剂晶体中Fe3+的位置,引起Fe2(MoO4)3晶格变形。Figure 2 shows pure iron molybdate, rare earth cerium doped iron molybdate (Ce-Fe 2 (MoO 4 ) 3 ): 1%-Ce, rare earth cerium doped iron molybdate (Ce-Fe 2 (MoO ) prepared by the present invention 4 ) 3 ): XRD pattern of 2%-Ce, it can be seen from the figure that all diffraction peaks are consistent with the diffraction peaks of standard card PDF#35-0183, indicating that the sample was successfully synthesized. No additional diffraction peaks appeared after doping rare earth element cerium, which indicated that the crystal structure of Fe 2 (MoO 4 ) 3 did not change after the introduction of rare earth ions. Compared with Fe 2 (MoO 4 ) 3 without rare earth element doping, the XRD peaks of Fe 2 (MoO 4 ) 3 after introducing rare earth element doping are partially shifted, which may be due to the doping of rare earth element ions. The Fe 3+ was substituted into the catalyst crystal, resulting in the deformation of Fe 2 (MoO 4 ) 3 lattice.

三、稀土铈掺杂钼酸铁(Ce-Fe2(MoO4)3)的催化性能3. Catalytic performance of rare earth cerium doped iron molybdate (Ce-Fe 2 (MoO 4 ) 3 )

图3为所制备样品中Ce3+与Fe3+的物质量之比分别为1%、2%、4%、6%的光催化性能研究图,使用上海兰仪LY-GHX-Xe-300型光催化反应器,此处氙灯光源用北京纽比特科技有限公司HSX-F300氙灯,光源处使用滤光片,滤掉紫外光(λ<400 nm),反应装置循环水恒温并持续搅拌,分别在黑暗条件和可见光照射下进行光催化性能测试。从图中可以发现稀土铈元素的掺杂可有效的提高Fe2(MoO4)3的光催化性能,催化剂材料Ce-Fe2(MoO4)3对亚甲基蓝的降解能力顺序依次为Ce-2%/Fe2(MoO4)3>Ce-1%/Fe2(MoO4)3>Ce-4%/Fe2(MoO4)3>Ce-6%/Fe2(MoO4)3>Fe2(MoO4)3。其中Ce-2%/Fe2(MoO4)3的光催化性能最强,未掺杂铈的催化剂材料的光催化性能最弱。在4h的光催化反应后,Ce-2%/Fe2(MoO4)3对亚甲基蓝溶液的降解率达到95.7%,而未掺杂铈的催化剂材料对亚甲基蓝溶液的降解率仅为63.29%。Figure 3 shows the photocatalytic performance of the prepared samples with the ratios of Ce 3+ and Fe 3+ being 1%, 2%, 4%, and 6%, respectively. Shanghai Lanyi LY-GHX-Xe-300 was used. Type photocatalytic reactor, where the xenon lamp light source is HSX-F300 xenon lamp of Beijing Newbit Technology Co., Ltd., a filter is used at the light source to filter out ultraviolet light (λ<400 nm), the reaction device circulates water at a constant temperature and continuously stirs, respectively. The photocatalytic performance tests were carried out under dark conditions and visible light irradiation. It can be found from the figure that the doping of rare earth cerium element can effectively improve the photocatalytic performance of Fe 2 (MoO 4 ) 3 , and the degradation ability of the catalyst material Ce-Fe 2 (MoO 4 ) 3 to methylene blue is in the order of Ce-2% /Fe 2 (MoO 4 ) 3 >Ce-1%/Fe 2 (MoO 4 ) 3 >Ce-4%/Fe 2 (MoO 4 ) 3 >Ce-6%/Fe 2 (MoO 4 ) 3 >Fe 2 (MoO 4 ) 3 . Among them, Ce-2%/Fe 2 (MoO 4 ) 3 has the strongest photocatalytic performance, and the undoped cerium catalyst material has the weakest photocatalytic performance. After 4 h of photocatalytic reaction, the degradation rate of Ce-2%/Fe 2 (MoO 4 ) 3 to methylene blue solution reached 95.7%, while the degradation rate of undoped cerium catalyst material to methylene blue solution was only 63.29%.

综上所述,本发明制备的铈掺杂钼酸铁呈均匀纳米球状结构,具有较大的比表面积;同时稀土元素的掺杂能够有效的降低光催化剂的光生电子-空穴复合率,且能在一定程度上提高光催化剂的比表面积,有利于光催化效率的提升,这使得这种Ce-Fe2(MoO4)3在光催化染料废水处理领域具有广阔的应用前景。To sum up, the cerium-doped iron molybdate prepared by the present invention has a uniform nano-spherical structure and has a large specific surface area; at the same time, the doping of rare earth elements can effectively reduce the photo-generated electron-hole recombination rate of the photocatalyst, and The specific surface area of the photocatalyst can be increased to a certain extent, which is beneficial to the improvement of the photocatalytic efficiency, which makes the Ce-Fe 2 (MoO 4 ) 3 have broad application prospects in the field of photocatalytic dye wastewater treatment.

附图说明Description of drawings

图1为稀土铈掺杂钼酸铁Ce-Fe2(MoO4)3:2%-Ce和钼酸铁的扫描电镜图。FIG. 1 is a scanning electron microscope image of rare earth cerium doped iron molybdate Ce-Fe 2 (MoO 4 ) 3 : 2%-Ce and iron molybdate.

图2为本发明所制备样品的XRD图。Fig. 2 is the XRD pattern of the sample prepared by the present invention.

图3为本发明所制备样品光催化降解亚甲基蓝的光催化性能图。FIG. 3 is a photocatalytic performance diagram of the photocatalytic degradation of methylene blue of the sample prepared in the present invention.

具体实施方式Detailed ways

下面通过具体实例对本发明一种稀土铈掺杂钼酸铁(Ce-Fe2(MoO4)3)的制备和性能作进一步说明。The preparation and properties of a rare earth cerium-doped iron molybdate (Ce-Fe 2 (MoO 4 ) 3 ) of the present invention will be further described below through specific examples.

实施例1Example 1

将1.0 mmol Fe(NO3)・9H2O溶解于20mL去离子水中,然后在室温下加入0.01mmolCe(NO3)3,得到Fe(NO3)・9H2O和Ce(NO3)3的混合溶液;将0.22 mmol (NH4)6Mo7O24・4H2O溶解于20mL去离子水中,在磁力搅拌下将其逐滴滴加到Fe(NO3)・9H2O和Ce(NO3)3的混合溶液中,25℃恒温水浴持续搅拌6h,加入氨水调节pH至4;最后转移至含有50mL聚四氟乙烯内胆的高压反应釜中,于180℃下反应12h,待反应结束后用去离子水离心洗涤三次,再用无水乙醇离心洗涤两次,然后在80℃下干燥,得到稀土铈掺杂钼酸铁Ce-Fe2(MoO4)3光催化剂:1%-Ce。Dissolve 1.0 mmol Fe(NO 3 )·9H 2 O in 20 mL of deionized water, and then add 0.01 mmol Ce(NO 3 ) 3 at room temperature to obtain a mixture of Fe(NO 3 )·9H 2 O and Ce(NO 3 ) 3 mixed solution; 0.22 mmol (NH 4 ) 6 Mo 7 O 24 ·4H 2 O was dissolved in 20 mL of deionized water, and added dropwise to Fe(NO 3 )·9H 2 O and Ce(NO ) under magnetic stirring 3 ) In the mixed solution of 3 , keep stirring in a constant temperature water bath at 25°C for 6h, add ammonia water to adjust the pH to 4; finally transfer to a high pressure reaction kettle containing 50mL polytetrafluoroethylene liner, react at 180°C for 12h, and wait for the reaction to end After centrifugation and washing with deionized water three times, centrifugation and washing with absolute ethanol for two times, and then drying at 80 °C, a rare earth cerium-doped iron molybdate Ce-Fe 2 (MoO 4 ) 3 photocatalyst was obtained: 1%-Ce .

催化性能:在亚甲基蓝溶液中加入上述制备材料,在4h的光催化反应后,溶液中亚甲基蓝的降解率达到92.85%。Catalytic performance: The above prepared materials were added to the methylene blue solution. After 4 h of photocatalytic reaction, the degradation rate of methylene blue in the solution reached 92.85%.

实施例2Example 2

将1.0 mmol Fe(NO3)・9H2O溶解于20mL去离子水中,然后在室温下加入0.02mmolCe(NO3)3,得到Fe(NO3)・9H2O和Ce(NO3)3的混合溶液;将0.22 mmol (NH4)6Mo7O24・4H2O溶解于20mL去离子水中,在磁力搅拌下将其逐滴滴加到Fe(NO3)・9H2O和Ce(NO3)3的混合溶液中,25℃恒温水浴持续搅拌6h,加入氨水调节pH至4;最后转移至含有50mL聚四氟乙烯内胆的高压反应釜中,于180℃下反应12h,待反应结束后用去离子水离心洗涤三次,再用无水乙醇离心洗涤两次,然后在80℃下干燥,得到稀土铈掺杂钼酸铁光催化剂Ce-Fe2(MoO4)3:2%-Ce。Dissolve 1.0 mmol Fe(NO 3 )·9H 2 O in 20 mL of deionized water, and then add 0.02 mmol Ce(NO 3 ) 3 at room temperature to obtain a mixture of Fe(NO 3 )·9H 2 O and Ce(NO 3 ) 3 mixed solution; 0.22 mmol (NH 4 ) 6 Mo 7 O 24 ·4H 2 O was dissolved in 20 mL of deionized water, and added dropwise to Fe(NO 3 )·9H 2 O and Ce(NO ) under magnetic stirring 3 ) In the mixed solution of 3 , keep stirring in a constant temperature water bath at 25°C for 6h, add ammonia water to adjust the pH to 4; finally transfer to a high pressure reaction kettle containing 50mL polytetrafluoroethylene liner, react at 180°C for 12h, and wait for the reaction to end After centrifugation and washing with deionized water for three times, centrifugation and washing with absolute ethanol for two times, and then drying at 80° C., the rare earth cerium doped iron molybdate photocatalyst Ce-Fe 2 (MoO 4 ) 3 : 2%-Ce was obtained .

催化性能:在亚甲基蓝溶液中加入上述制备材料,在4h的光催化反应后,溶液中亚甲基蓝的降解率达到95.7%。Catalytic performance: The above prepared materials were added to the methylene blue solution. After 4 h of photocatalytic reaction, the degradation rate of methylene blue in the solution reached 95.7%.

实施例3Example 3

将1.0 mmol Fe(NO3)・9H2O溶解于20mL去离子水中,然后在室温下加入0.04mmolCe(NO3)3,得到Fe(NO3)・9H2O和Ce(NO3)3的混合溶液;将0.22mmol (NH4)6Mo7O24・4H2O溶解于20mL去离子水中,在磁力搅拌下将其逐滴滴加到Fe(NO3)・9H2O和Ce(NO3)3的混合溶液中,25℃恒温水浴持续搅拌6h,加入氨水调节pH至4;最后转移至含有50mL聚四氟乙烯内胆的高压反应釜中,于180℃下反应12h,待反应结束后用去离子水离心洗涤三次,再用无水乙醇离心洗涤两次,然后在80℃下干燥,得到稀土铈掺杂钼酸铁光催化剂Ce-Fe2(MoO4)3:4%-Ce。Dissolve 1.0 mmol Fe(NO 3 )·9H 2 O in 20 mL of deionized water, and then add 0.04 mmol Ce(NO 3 ) 3 at room temperature to obtain a mixture of Fe(NO 3 )·9H 2 O and Ce(NO 3 ) 3 Mixed solution; 0.22mmol (NH 4 ) 6 Mo 7 O 24 ·4H 2 O was dissolved in 20 mL of deionized water, and added dropwise to Fe(NO 3 )·9H 2 O and Ce(NO ) under magnetic stirring 3 ) In the mixed solution of 3 , keep stirring in a constant temperature water bath at 25°C for 6h, add ammonia water to adjust the pH to 4; finally transfer to a high pressure reaction kettle containing 50mL polytetrafluoroethylene liner, react at 180°C for 12h, and wait for the reaction to end After centrifugation and washing with deionized water for three times, centrifugation and washing with absolute ethanol for two times, and then drying at 80 °C, the rare earth cerium doped iron molybdate photocatalyst Ce-Fe 2 (MoO 4 ) 3 : 4%-Ce was obtained .

催化性能:在亚甲基蓝溶液中加入上述制备材料,在4h的光催化反应后,溶液中亚甲基蓝的降解率达到67.39%。Catalytic performance: The above prepared materials were added to the methylene blue solution. After 4 h of photocatalytic reaction, the degradation rate of methylene blue in the solution reached 67.39%.

实施例4Example 4

将1.0 mmol Fe(NO3)・9H2O溶解于20mL去离子水中,然后在室温下加入0.06mmolCe(NO3)3,得到Fe(NO3)・9H2O和Ce(NO3)3的混合溶液;将0.22mmol (NH4)6Mo7O24・4H2O溶解于20mL去离子水中,在磁力搅拌下将其逐滴滴加到Fe(NO3)・9H2O和Ce(NO3)3的混合溶液中,25℃恒温水浴持续搅拌6h,加入氨水调节pH至4;最后转移至含有50mL聚四氟乙烯内胆的高压反应釜中,于180℃下反应12h,待反应结束后用去离子水离心洗涤三次,再用无水乙醇离心洗涤两次,然后在80℃下干燥,得到稀土铈掺杂钼酸铁光催化剂Ce-Fe2(MoO4)3:6%-Ce。Dissolve 1.0 mmol Fe(NO 3 )·9H 2 O in 20 mL of deionized water, and then add 0.06 mmol Ce(NO 3 ) 3 at room temperature to obtain a mixture of Fe(NO 3 )·9H 2 O and Ce(NO 3 ) 3 Mixed solution; 0.22mmol (NH 4 ) 6 Mo 7 O 24 ·4H 2 O was dissolved in 20 mL of deionized water, and added dropwise to Fe(NO 3 )·9H 2 O and Ce(NO ) under magnetic stirring 3 ) In the mixed solution of 3 , keep stirring in a constant temperature water bath at 25°C for 6h, add ammonia water to adjust the pH to 4; finally transfer to a high pressure reaction kettle containing 50mL polytetrafluoroethylene liner, react at 180°C for 12h, and wait for the reaction to end After centrifugation and washing with deionized water for three times, centrifugation and washing with absolute ethanol for two times, and then drying at 80 °C, the rare earth cerium doped iron molybdate photocatalyst Ce-Fe 2 (MoO 4 ) 3 : 6%-Ce was obtained .

催化性能:在亚甲基蓝溶液中加入上述制备材料,在4h的光催化反应后,溶液中亚甲基蓝的降解率达到65.65%。Catalytic performance: The above prepared materials were added to the methylene blue solution. After 4 h of photocatalytic reaction, the degradation rate of methylene blue in the solution reached 65.65%.

Claims (5)

1. A process for preparing the rare-earth Ce doped iron molybdate photocatalyst includes such steps as adding Fe (NO)3)・9H2Dissolving O in deionized water, adding Ce (NO) at room temperature3)3To obtain Fe (NO)3)・9H2O and Ce (NO)3)3The mixed solution of (1); will be (NH)4)6Mo7O24・4H2O is dissolved in deionized water and added dropwise to Fe (NO)3)・9H2O and Ce (NO)3)3Stirring the mixed solution, adding ammonia water to adjust the pH value to 3-4, reacting for 12-13 h at 180-185 ℃, centrifugally washing and drying to obtain the rare earth cerium doped iron molybdate photocatalyst Ce-Fe2(MoO4)3(ii) a What is needed isThe above Ce (NO)3)3And Fe (NO)3)・9H2The molar ratio of O is 0.01-0.02: 1.
2. The method of claim 1, wherein the preparation method comprises the following steps: said Fe (NO)3)・9H2O and (NH)4)6Mo7O24・4H2The molar ratio of O is 1: 0.2-1: 0.25.
3. The method for preparing a rare earth cerium doped iron molybdate photocatalyst as claimed in claim 1, wherein the method comprises the following steps: the stirring is carried out for 4-6 h under a water bath at 25 ℃.
4. The method of claim 1, wherein the preparation method comprises the following steps: the drying temperature is 80-85 ℃.
5. The use of the rare earth cerium doped iron molybdate photocatalyst prepared by the preparation method according to any one of claims 1 to 4 for photocatalytic degradation of organic pollutants in dye wastewater, characterized in that: the organic contaminant is methylene blue.
CN202010664065.1A 2020-07-10 2020-07-10 Preparation and application of rare earth cerium doped iron molybdate photocatalyst Expired - Fee Related CN111659411B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202010664065.1A CN111659411B (en) 2020-07-10 2020-07-10 Preparation and application of rare earth cerium doped iron molybdate photocatalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202010664065.1A CN111659411B (en) 2020-07-10 2020-07-10 Preparation and application of rare earth cerium doped iron molybdate photocatalyst

Publications (2)

Publication Number Publication Date
CN111659411A CN111659411A (en) 2020-09-15
CN111659411B true CN111659411B (en) 2022-06-14

Family

ID=72391922

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010664065.1A Expired - Fee Related CN111659411B (en) 2020-07-10 2020-07-10 Preparation and application of rare earth cerium doped iron molybdate photocatalyst

Country Status (1)

Country Link
CN (1) CN111659411B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116550350B (en) * 2023-05-14 2024-12-17 广东九田环保科技有限公司 Environment-friendly formaldehyde purifying agent and preparation method and application thereof

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107213904B (en) * 2017-05-08 2020-07-28 武汉工程大学 A kind of preparation method of monoclinic iron molybdate nanosheets with high activity and exposed crystal planes
CN108295862A (en) * 2018-02-27 2018-07-20 成都新柯力化工科技有限公司 A kind of sheet iron molybdate photochemical catalyst and preparation method for dye wastewater treatment
CN111229242B (en) * 2018-11-29 2022-12-30 中国科学院大连化学物理研究所 Iron-molybdenum-based catalyst for preparing formaldehyde by oxidizing cerium-doped methanol, preparation and application thereof

Also Published As

Publication number Publication date
CN111659411A (en) 2020-09-15

Similar Documents

Publication Publication Date Title
CN107456991B (en) A kind of preparation method of g-C3N4 quantum dot supported bismuth tungstate nanosheet photocatalyst
CN110064424A (en) A kind of BiOX/titanium carbide optic catalytic composite material and preparation method thereof
Vijayaraghavan et al. Influence of secondary oxide phases in enhancing the photocatalytic properties of alkaline earth elements doped LaFeO3 nanocomposites
CN108355669B (en) Magnetic nano onion carbon loaded Bi2WO6Photocatalyst and preparation method and application thereof
CN108993550A (en) A kind of bromine oxygen bismuth photochemical catalyst and preparation method thereof that surface Lacking oxygen is modified
CN110193373A (en) The preparation method and applications of visible light-responded doped yttrium bismuth oxychloride catalyst
CN103611577B (en) A visible light catalyst for efficiently degrading organic dye wastewater and its preparation method
CN105056973B (en) Efficient Bi2S3-BiFeO3 composite visible-light-driven photocatalyst prepared through in-situ growth with chemical corrosion method and application of Bi2S3-BiFeO3 composite visible-light-driven photocatalyst
CN110227461B (en) A magnetic heterogeneous photosynthetic Fenton catalyst and its preparation method and application
CN106745166A (en) A kind of synthetic method of quantum dot cerium oxide/modified oxidized cerium nano material
Han et al. MIL-53 (Fe)@ BiOBr/TCN/Ti photoanode assembled visible light responsive photocatalytic fuel cell to enhance rhodamine B degradation and electricity generation
CN111686770B (en) A kind of metal ion co-doped BiOBr microsphere, preparation method and application thereof
CN111659411B (en) Preparation and application of rare earth cerium doped iron molybdate photocatalyst
CN108704638A (en) A kind of silk ball-shaped Bi2WO6Nano material and its preparation method and application
Cao et al. Preparation of UiO-66-NH2/Bi2. 15WO6 composite with enhanced tetracycline degradation under weak light intensity
CN106582726A (en) A kind of Bi4O5Br2 hollow sphere and its preparation method using microemulsion as template
CN112871183B (en) Preparation method of bismuth/bismuth tungstate/ferroferric oxide composite photocatalyst
Lin et al. High-performance research of the photocatalyst of amorphous iron oxide supported on the novel Bi-based compound in the photo-Fenton system for the removal of dye pollutant
CN117258846B (en) Floating catalyst, preparation method and application thereof
CN115121249B (en) Preparation method and application of magnetic sodium iron silicate/hematite composite photocatalyst
CN110801857A (en) Method for preparing titanium dioxide-nitrogen doped graphene composite photocatalytic material
Xu et al. Preparation of organic porous materials-TiO 2/cu composite with excellent photocatalytic degradation performances toward degradation of organic pollutants in wastewater
CN112808287B (en) Magnetic core-shell bismuth oxide carbonate/sepiolite composite photocatalyst and preparation method thereof
Su et al. Preparation and visible photocatalytic properties of Ag3PO4/PBN/Fe3O4 composites
CN112657555B (en) Monodisperse Fe-O cluster doped Ni-based metal organic framework composite photocatalyst and preparation method and application thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20220614