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CN106955699B - A kind of high-efficiency solar energy nitrogen fixation photocatalytic material and preparation method thereof - Google Patents

A kind of high-efficiency solar energy nitrogen fixation photocatalytic material and preparation method thereof Download PDF

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CN106955699B
CN106955699B CN201610015669.7A CN201610015669A CN106955699B CN 106955699 B CN106955699 B CN 106955699B CN 201610015669 A CN201610015669 A CN 201610015669A CN 106955699 B CN106955699 B CN 106955699B
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王文中
孙松美
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Jiangsu Institute Of Advanced Inorganic Materials
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Abstract

本发明涉及一种高效太阳能固氮光催化材料及其制备方法,所述光催化材料的化学组成为Bi2O3‑x/nBiaMOb,其中,x=0~1,n=0~1,a=0~2,b=0~6,M为V、Mo、W中至少一种。本发明的光催化材料包括铋基氧化物Bi2O3‑x(x=0~1)或其与BiaMOb(M=V,Mo,W)光催化材料的复合材料,本发明的光催化材料不仅具有极高的光催化固氮活性,还具有极高的稳定性。该材料中Bi2O3‑x(x=0~1)可以吸附并活化空气中的氮气,促进氮氮三键断裂,在水中生成氨。

The invention relates to a high-efficiency solar nitrogen-fixing photocatalytic material and a preparation method thereof. The chemical composition of the photocatalytic material is Bi 2 O 3‑x / nBia MO b , wherein x=0~1, n=0~1 , a=0~2, b=0~6, M is at least one of V, Mo, and W. The photocatalytic material of the present invention includes bismuth-based oxide Bi 2 O 3-x (x=0~1) or its composite material with Bi a MO b (M=V, Mo, W) photocatalytic material. Photocatalytic materials not only have extremely high photocatalytic nitrogen fixation activity, but also have extremely high stability. Bi 2 O 3-x (x=0~1) in the material can adsorb and activate nitrogen in the air, promote the cleavage of nitrogen-nitrogen triple bonds, and generate ammonia in water.

Description

一种高效太阳能固氮光催化材料及其制备方法A kind of high-efficiency solar energy nitrogen fixation photocatalytic material and preparation method thereof

技术领域technical field

本发明涉及一种高效太阳能固氮光催化材料及其制备方法,属于光催化材料技术领域。The invention relates to a high-efficiency solar energy nitrogen-fixing photocatalytic material and a preparation method thereof, and belongs to the technical field of photocatalytic materials.

背景技术Background technique

氨为植物特别是粮食作物提供氮元素,在工业界的用途广泛,是当今世界上除硫酸外产量最大的化工产品,目前最大的用量在于化肥。传统的固氮途径主要有生物固氮、化学固氮。生物固氮能在比较温和的条件下进行,但是仅能发生在少数的植物和微生物中,难以进行大规模的生产应用。化学固氮有效的解决了生物固氮的不足,但是整个过程能耗大,大量的使用不仅造成了土壤板结,硝酸盐随水渗漏,造成环境较严重污染。目前,整个世界都面临着能源、粮食和环境问题,探究新的固氮产氨的方法已成科学界的热门问题。Ammonia provides nitrogen for plants, especially food crops, and is widely used in industry. It is the largest chemical product in the world except sulfuric acid, and the largest amount is currently in chemical fertilizers. The traditional nitrogen fixation methods mainly include biological nitrogen fixation and chemical nitrogen fixation. Biological nitrogen fixation can be carried out under relatively mild conditions, but it can only occur in a few plants and microorganisms, making it difficult for large-scale production applications. Chemical nitrogen fixation effectively solves the shortage of biological nitrogen fixation, but the whole process consumes a lot of energy, and a large amount of use not only causes soil compaction, but also nitrate leakage with water, causing serious environmental pollution. At present, the whole world is facing energy, food and environmental problems, and exploring new methods of nitrogen fixation and ammonia production has become a hot issue in the scientific community.

氨合成反应的关键在于N2的活化。如果将光能引入这一反应体系中,则有可能实现这一反应。光催化固氮是利用半导体光催化剂对光的响应,通过把氮气转化成氨、将光能转化成化学能的一种新技术,因其节约能源、绿色环保已成为光催化领域重要的科学和技术问题。The key to the ammonia synthesis reaction is the activation of N2 . If light energy is introduced into this reaction system, it is possible to realize this reaction. Photocatalytic nitrogen fixation is a new technology that utilizes the response of semiconductor photocatalyst to light by converting nitrogen into ammonia and light energy into chemical energy. It has become an important science and technology in the field of photocatalysis because of its energy saving and green environmental protection. question.

光催化固氮技术的核心问题是合适光催化剂的设计、开发与研制。目前的研究主要集中于Fe掺杂的TiO2基系列光催化剂。但就TiO2而言,存在几个关键的技术难题,如TiO2的带隙为3.2eV,仅能被紫外光(只占太阳能的3.8%)激发,此外TiO2光生载流子的复合率高,量子效率低(不到4%),太阳能的利用率低,在可见光范围内几乎没有光响应;用于光催化固氮时,只能产生1-10μmol/L的氨氮。The core problem of photocatalytic nitrogen fixation technology is the design, development and development of suitable photocatalysts. Current research mainly focuses on Fe-doped TiO2 -based series of photocatalysts. But for TiO2 , there are several key technical difficulties, such as the band gap of TiO2 is 3.2eV, which can only be excited by ultraviolet light (only 3.8% of the solar energy), in addition, the recombination rate of photogenerated carriers of TiO2 High, low quantum efficiency (less than 4%), low utilization of solar energy, almost no light response in the visible light range; when used for photocatalytic nitrogen fixation, only 1-10 μmol/L of ammonia nitrogen can be produced.

研发新型高效光催化材料,是利用太阳能实现光催化固氮的关键,也是光催化进一步走向实用化的必然趋势和发展方向。光催化固氮的关键问题在于N≡N三键的活化。绝大多数光催化材料本身不具有活化N2的能力,因此,要从根本上实现光催化材料的太阳能固氮,必须使其与可以活化N2的其他材料复合。这种材料可以是贵金属或是富含电子的金属氧化物。考虑到贵金属的成本问题,富电子的金属氧化物成为助催化剂的首选。Bi元素在形成金属氧化物时,其Bi原子上含有的孤对电子往往不参与成建,使其成为富电子化合物。因此,可以考虑在光催化材料制备过程中引入Bi离子,使其同时生成一部分Bi的金属氧化物负载在光催化材料的表面,起到活化N2的作用。制备这种Bi基氧化物与光催化材料的复合材料,可以极大提高光催化材料在太阳能作用下的固氮效率,既具有较高的科学价值又具有对缓解能源危机、防治环境污染的实际意义。The development of new and efficient photocatalytic materials is the key to using solar energy to achieve photocatalytic nitrogen fixation, and it is also an inevitable trend and development direction for photocatalysis to be further practical. The key problem for photocatalytic nitrogen fixation is the activation of N≡N triple bonds. The vast majority of photocatalytic materials themselves do not have the ability to activate N2 , therefore, to fundamentally realize the solar nitrogen fixation of photocatalytic materials, it must be combined with other materials that can activate N2 . This material can be a noble metal or an electron-rich metal oxide. Considering the cost of noble metals, electron-rich metal oxides are the first choice for cocatalysts. When the Bi element forms metal oxides, the lone pair electrons contained in the Bi atoms often do not participate in the formation, making it an electron-rich compound. Therefore, it can be considered to introduce Bi ions during the preparation of photocatalytic materials, so that a part of Bi metal oxides are simultaneously generated and supported on the surface of photocatalytic materials to activate N2 . The preparation of this composite of Bi-based oxides and photocatalytic materials can greatly improve the nitrogen fixation efficiency of photocatalytic materials under the action of solar energy, which has high scientific value and practical significance for alleviating the energy crisis and preventing environmental pollution. .

发明内容SUMMARY OF THE INVENTION

针对现有光催化固氮技术存在的上述问题,本发明的目的是提供一种高效太阳能固氮光催化材料,同时提供一种简单、快捷、可控性高的制备所述光催化材料的方法。In view of the above problems existing in the existing photocatalytic nitrogen fixation technology, the purpose of the present invention is to provide a high-efficiency solar nitrogen-fixing photocatalytic material, and at the same time provide a simple, fast and highly controllable method for preparing the photocatalytic material.

在此,本发明提供一种高效太阳能固氮光催化材料,所述光催化材料的化学组成为Bi2O3-x/nBiaMOb,其中,x=0~1,n=0~1,a=0~2,b=0~6,M为V、Mo、W中至少一种。优选x、n≠0。Herein, the present invention provides a high-efficiency solar nitrogen-fixing photocatalytic material, the chemical composition of the photocatalytic material is Bi 2 O 3-x / nBia MO b , wherein x=0~1, n=0~1, a=0 to 2, b=0 to 6, and M is at least one of V, Mo, and W. Preferably x, n≠0.

本发明的光催化材料包括铋基氧化物Bi2O3-x(x=0~1)或其与BiaMOb(M=V,Mo,W)光催化材料的复合材料,本发明的光催化材料不仅具有极高的光催化固氮活性,还具有极高的稳定性。该材料中Bi2O3-x(x=0~1)可以吸附并活化空气中的氮气,促进氮氮三键断裂,在水中生成氨。该材料对太阳能光催化固氮具有显著的光催化活性,在24小时模拟太阳光照下,在纯水中可产生1~10mg/L的氨氮,是目前国内外报道的太阳能条件下纯水中光催化固氮达到的最高效率。在相同条件下Fe掺杂的TiO2只能产生0.03mg/L的氨氮。Bi2O3-x(x=0~1)复合光催化材料显示了在自然条件下高效固氮的优势,具有应用前景。The photocatalytic material of the present invention includes bismuth-based oxide Bi 2 O 3-x (x=0~1) or its composite material with Bi a MO b (M=V, Mo, W) photocatalytic material. Photocatalytic materials not only have extremely high photocatalytic nitrogen fixation activity, but also have extremely high stability. Bi 2 O 3-x (x=0-1) in the material can adsorb and activate nitrogen in the air, promote the cleavage of nitrogen-nitrogen triple bonds, and generate ammonia in water. The material has significant photocatalytic activity for solar photocatalytic nitrogen fixation. Under 24 hours of simulated sunlight, 1-10 mg/L of ammonia nitrogen can be generated in pure water. The highest efficiency achieved for nitrogen fixation. Fe-doped TiO 2 can only produce 0.03 mg/L of ammonia nitrogen under the same conditions. Bi 2 O 3-x (x=0~1) composite photocatalytic material shows the advantages of efficient nitrogen fixation under natural conditions and has application prospects.

本发明中,所述光催化材料中Bi2O3-x颗粒的直径为1~1000纳米,优选1~100纳米,BiaMOb颗粒的直径为1~1000纳米,优选1~100纳米。颗粒尺寸增大到100纳米以后随着颗粒比表面积降低,催化活性大幅降低。In the present invention, the diameter of Bi 2 O 3-x particles in the photocatalytic material is 1-1000 nm, preferably 1-100 nm, and the diameter of Bi a MO b particles is 1-1000 nm, preferably 1-100 nm. After the particle size increased to 100 nm, the catalytic activity decreased significantly with the decrease of the specific surface area of the particles.

本发明还提供一种所述高效太阳能固氮光催化材料的制备方法,所述制备方法包括:将铋盐与油酸钠溶于水中,搅拌,制成乳液状前驱体溶液A;将M盐分散在水中,超声得到溶液B;将适量的溶液A与溶液B混合,于80~180℃合成2小时以上,洗涤、干燥后得到所述高效太阳能固氮光催化材料。“将适量的溶液A与溶液B混合”,所述“适量”是指使所述混合后的溶液制备的光催化材料Bi2O3-x/nBiaMOb中的n=0~1。The present invention also provides a preparation method of the high-efficiency solar nitrogen-fixing photocatalytic material, the preparation method comprising: dissolving bismuth salt and sodium oleate in water, stirring to prepare an emulsion-like precursor solution A; dispersing the M salt In water, ultrasonically obtain solution B; mix an appropriate amount of solution A and solution B, synthesize at 80-180° C. for more than 2 hours, wash and dry to obtain the high-efficiency solar nitrogen-fixing photocatalytic material. "Mix an appropriate amount of solution A and solution B", the "appropriate amount" refers to n=0-1 in the photocatalytic material Bi 2 O 3-x / nBia MO b prepared from the mixed solution.

本发明通过以油酸钠作为表面活性剂,将铋盐分散在去离子水中获得乳液状前驱体溶液A,将M盐(M=V,Mo,W)分散在去离子水中获得溶液B。当仅将前驱体溶液A于80~180℃合成2小时以上,洗涤、干燥后则可得到Bi2O3-x(x=0~1)光催化材料,此时制备的高效太阳能固氮光催化材料Bi2O3-x/nBiaMOb中n的取值为0。当将适量的溶液A与适量的溶液B混合,于80~180℃合成2小时以上,洗涤、干燥后则可制备得到n=0~1的光催化材料Bi2O3-x/nBiaMOb。本发明的制备方法无需特殊设备和苛刻条件,工艺简单,可控性强,容易实现规模化生产,具有实用性。The present invention uses sodium oleate as surfactant, disperses bismuth salt in deionized water to obtain emulsion precursor solution A, and disperses M salt (M=V, Mo, W) in deionized water to obtain solution B. When only the precursor solution A was synthesized at 80~180℃ for more than 2 hours, and after washing and drying, Bi 2 O 3-x (x=0~1) photocatalytic material could be obtained. At this time, the high-efficiency solar nitrogen fixation photocatalytic material was prepared. The value of n in the material Bi 2 O 3-x / nBia MO b is 0. When an appropriate amount of solution A is mixed with an appropriate amount of solution B, the photocatalytic material Bi 2 O 3-x / nBia MO with n=0 to 1 can be prepared after synthesizing at 80-180 ℃ for more than 2 hours, washing and drying. b . The preparation method of the invention does not need special equipment and harsh conditions, has simple process, strong controllability, is easy to realize large-scale production, and has practicability.

较佳地,所述铋盐为硝酸铋、氯化铋、铋离子络合物等铋盐中至少一种。Preferably, the bismuth salt is at least one of bismuth salts such as bismuth nitrate, bismuth chloride, and bismuth ion complexes.

较佳地,溶液A中Bi的摩尔浓度为0.001~0.2mol/L,浓度过高会使反应产物颗粒过大。Preferably, the molar concentration of Bi in solution A is 0.001-0.2 mol/L, and if the concentration is too high, the particles of the reaction product will be too large.

较佳地,溶液A中油酸钠的摩尔浓度为0.001~1mol/L,油酸浓度过低不能充分络合铋离子,过高会使反应液体碱性及还原性增加,不利于产物生成。Preferably, the molar concentration of sodium oleate in solution A is 0.001-1 mol/L, and the oleic acid concentration is too low to fully complex bismuth ions, and too high will increase the alkalinity and reducibility of the reaction liquid, which is not conducive to product formation.

较佳地,制成乳液状前驱体溶液A的搅拌时间为1~3小时。Preferably, the stirring time for preparing the emulsion-like precursor solution A is 1-3 hours.

较佳地,所述M盐为偏钒酸铵、钒酸铵、五氧化二钒、钨酸钠、钼酸钠、氯化钨、磷钨酸、磷钼酸等其中至少一种。Preferably, the M salt is at least one of ammonium metavanadate, ammonium vanadate, vanadium pentoxide, sodium tungstate, sodium molybdate, tungsten chloride, phosphotungstic acid, phosphomolybdic acid and the like.

较佳地,溶液B中M盐的摩尔浓度为0.001~0.1mol/L。Preferably, the molar concentration of M salt in solution B is 0.001-0.1 mol/L.

较佳地,合成时间为2~48小时。Preferably, the synthesis time is 2 to 48 hours.

附图说明Description of drawings

图1是实施例1中以BiO与BiVO4为例获得的BiO/BiVO4复合光催化材料的XRD衍射图谱; 1 is the XRD diffraction pattern of the BiO/BiVO composite photocatalytic material obtained by taking BiO and BiVO as an example in Example 1 ;

图2是实施例1以BiO与BiVO4为例获得的BiO/BiVO4复合光催化材料的透射电镜照片;Fig. 2 is the transmission electron microscope photograph of BiO/BiVO 4 composite photocatalytic material obtained by taking BiO and BiVO 4 as examples in Example 1;

图3是实施例1获得BiO/BiVO4与实施例2获得BiO及实施例4获得BiVO4等材料与Fe掺杂TiO2在模拟太阳光下光催化固氮效率的对比图;Figure 3 is a comparison diagram of the photocatalytic nitrogen fixation efficiency of materials such as BiO/BiVO 4 obtained in Example 1, BiO obtained in Example 2 and BiVO 4 obtained in Example 4 and Fe-doped TiO 2 under simulated sunlight;

图4是实施例2中获得BiO的XRD图谱;Fig. 4 obtains the XRD pattern of BiO in embodiment 2;

图5是实施例4中获得BiVO4的XRD图谱。FIG. 5 is the XRD pattern of BiVO 4 obtained in Example 4. FIG.

具体实施方式Detailed ways

以下结合附图和下述实施方式进一步说明本发明,应理解,下述实施方式仅用于说明本发明,而非限制本发明。The present invention will be further described below with reference to the accompanying drawings and the following embodiments. It should be understood that the following embodiments are only used to illustrate the present invention, but not to limit the present invention.

本发明的目的是,提供一种高效太阳能固氮光催化材料,同时提供一种制备所述光催化材料的方法。本发明的光催化材料化学组成为Bi2O3-x/nBiaMOb,包括以Bi2O3-x(x=0~1)为主要催化活性物种的光催化材料及其与BiaMOb复合的光催化材料。当n=0时,所述光催化材料为铋基氧化物Bi2O3-x(x=0~1),当n≠0时,所述光催化材料为Bi2O3-x与BiaMOb(M=V,Mo,W)光催化材料的复合材料。The purpose of the present invention is to provide a high-efficiency solar nitrogen-fixing photocatalytic material and a method for preparing the photocatalytic material. The chemical composition of the photocatalytic material of the present invention is Bi 2 O 3-x /nBia MO b , including the photocatalytic material with Bi 2 O 3 -x (x=0-1) as the main catalytic active species and its combination with Bi a Photocatalytic materials of MO b composites. When n=0, the photocatalytic material is Bi-based oxide Bi 2 O 3-x (x=0~1), and when n≠0, the photocatalytic material is Bi 2 O 3-x and Bi a MO b (M=V, Mo, W) composite of photocatalytic materials.

本发明采用液相法,以油酸钠作为表面活性剂,将铋盐分散在去离子水中获得乳液状前驱体溶液A,将M盐(M=V,Mo,W)溶于水中得前驱体溶液B,加热前驱体溶液或其与M盐的混合溶液,制备得到本发明的高效太阳能固氮光催化材料。关于溶液A的制备,优选先将作为表面活性剂油酸钠溶于去离子水,这样可以使得油酸分子充分溶解形成胶束,再加入铋盐使其分散均匀。当仅加热前驱体溶液A时可得到Bi2O3-x(x=0~1)光催化材料,此时制备的高效太阳能固氮光催化材料Bi2O3-x/nBiaMOb中n的取值为0。当将适量的溶液A与适量的溶液B混合后加热则可制备得到n=0~1且n不为0的光催化材料Bi2O3-x/nBiaMOb;所述“适量”是指使所述混合后的溶液制备的光催化材料Bi2O3-x/nBiaMOb中的n=0~1且n不为0;另,关于溶液A与溶液B的混合液,其中铋盐与M盐(M=V,Mo,W)的摩尔比优选为1:1~1:2;当铋盐的量太多会导致没有固氮催化活性的Bi2O3生成、太少会产生M盐的分相。The present invention adopts the liquid phase method, uses sodium oleate as surfactant, disperses bismuth salt in deionized water to obtain emulsion precursor solution A, and dissolves M salt (M=V, Mo, W) in water to obtain precursor In solution B, the precursor solution or the mixed solution thereof with M salt is heated to prepare the high-efficiency solar nitrogen-fixing photocatalytic material of the present invention. Regarding the preparation of solution A, it is preferable to dissolve sodium oleate as a surfactant in deionized water first, so that the oleic acid molecules can be fully dissolved to form micelles, and then bismuth salt is added to make it evenly dispersed. When only the precursor solution A is heated, Bi 2 O 3-x (x=0~1) photocatalytic material can be obtained, and the high-efficiency solar nitrogen-fixing photocatalytic material Bi 2 O 3-x / nBia MO b is prepared at this time. The value of is 0. When an appropriate amount of solution A and an appropriate amount of solution B are mixed and heated, the photocatalytic material Bi 2 O 3-x / nBia MO b with n=0~1 and n is not 0 can be prepared; the “appropriate amount” is Refers to the photocatalytic material Bi 2 O 3-x / nBia MO b prepared from the mixed solution, where n=0~1 and n is not 0; The molar ratio of salt to M salt (M=V, Mo, W) is preferably 1:1 to 1:2; when the amount of bismuth salt is too large, Bi 2 O 3 without nitrogen fixation catalytic activity will be generated, and too little will produce Phase separation of M salts.

本发明中,配置乳液状前驱体溶液包括将铋盐与油酸钠溶于水中,搅拌,制成乳液状前驱体溶液的步骤。所述铋盐包括但不限于硝酸铋、氯化铋、铋的络合物等。所述乳液状前驱体溶液中含Bi的摩尔浓度优选0.001~0.2mol/L,油酸钠的摩尔浓度优选0.001~1mol/L,超过浓度范围,反应物浓度过大会出现产物颗粒过大,催化性能降低等问题。油酸钠浓度过大会导致反应液酸碱性及还原性改变不利于产物生成。具体的,作为一个示例,例如将硝酸铋或氯化铋与油酸钠按一定比例溶解于去离子水中,搅拌1~3小时使形成乳液状前驱体溶液。关于铋盐与油酸钠的混合比例,两者摩尔比可以为1:3~1:6之间,既保证Bi离子充分络合,油酸钠浓度也不过高。In the present invention, the preparation of the emulsion precursor solution includes the steps of dissolving bismuth salt and sodium oleate in water and stirring to prepare the emulsion precursor solution. The bismuth salts include, but are not limited to, bismuth nitrate, bismuth chloride, bismuth complexes, and the like. The molar concentration of Bi in the emulsion precursor solution is preferably 0.001 to 0.2 mol/L, and the molar concentration of sodium oleate is preferably 0.001 to 1 mol/L. If the concentration exceeds the concentration range, the reactant concentration will be too large, and the product particles will be too large, and the catalytic effect will be too large. performance degradation, etc. Excessive concentration of sodium oleate will lead to changes in the acidity, alkalinity and reducibility of the reaction solution, which is not conducive to the formation of products. Specifically, as an example, for example, bismuth nitrate or bismuth chloride and sodium oleate are dissolved in deionized water in a certain proportion, and stirred for 1 to 3 hours to form an emulsion-like precursor solution. Regarding the mixing ratio of bismuth salt and sodium oleate, the molar ratio of the two can be between 1:3 and 1:6, which ensures that Bi ions are fully complexed and the concentration of sodium oleate is not too high.

本发明中,M盐(M=V,Mo,W)包括但不限于为偏钒酸铵、钒酸铵、五氧化二钒、钨酸钠、钼酸钠、氯化钨、磷钨酸、磷钼酸等。将M盐溶于水后搅拌0.5~2小时,并超声分散均匀,M盐溶于水的摩尔浓度优选0.001~0.1mol/L。In the present invention, M salt (M=V, Mo, W) includes but is not limited to ammonium metavanadate, ammonium vanadate, vanadium pentoxide, sodium tungstate, sodium molybdate, tungsten chloride, phosphotungstic acid, Phosphomolybdic acid, etc. After dissolving the M salt in water, stir for 0.5 to 2 hours, and ultrasonically disperse it uniformly. The molar concentration of the M salt dissolved in water is preferably 0.001 to 0.1 mol/L.

本发明合成的光催化材料包括以Bi2O3-x(x=0~1)为主要催化活性物种的光催化材料及其与BiaMOb复合的光催化材料。作为一个示例,合成步骤可以包括:The photocatalytic material synthesized by the invention includes the photocatalytic material with Bi 2 O 3-x (x=0-1) as the main catalytic active species and the photocatalytic material compounded with Bi a MO b . As an example, the synthesis steps may include:

当将乳液状前驱体溶液于80~180℃油浴或水热合成2小时以上,用有机溶剂洗涤,干燥后获得Bi2O3-x(x=0~1)光催化材料;When the emulsion precursor solution is synthesized in an oil bath or hydrothermally at 80~180°C for more than 2 hours, washed with an organic solvent, and dried to obtain Bi 2 O 3-x (x=0~1) photocatalytic material;

当将乳液状前驱体溶液与M盐水溶液混合,于80~180℃油浴或水热合成2小时以上,用有机溶剂洗涤,干燥后获得Bi2O3-x(x=0~1)负载的复合光催化材料;When the emulsion precursor solution is mixed with the M salt solution, it is synthesized in oil bath or hydrothermally at 80~180℃ for more than 2 hours, washed with organic solvent, and dried to obtain Bi 2 O 3-x (x=0~1) loading composite photocatalytic materials;

所述的有机溶剂为正己烷、环己烷、丙酮、酒精等。The organic solvent is n-hexane, cyclohexane, acetone, alcohol and the like.

与现有技术相比,本发明具有如下有益效果:Compared with the prior art, the present invention has the following beneficial effects:

1)由本发明方法获得的Bi2O3-x/nBiaMOb光催化材料,不仅具有极高的光催化固氮活性,还具有极高的稳定性。材料在24小时模拟太阳光照下,在纯水中可产生1~10mg/L的氨氮,是目前国内外报道的太阳能条件下纯水中光催化固氮达到的最高效率。在相同条件下Fe掺杂的TiO2只能产生0.03mg/L的氨氮。Bi2O3-x(x=0~1)复合光催化材料显示了在自然条件下高效固氮的优势,具有应用前景;1) The Bi 2 O 3-x / nBia MO b photocatalytic material obtained by the method of the present invention not only has extremely high photocatalytic nitrogen fixation activity, but also has extremely high stability. The material can generate 1-10 mg/L of ammonia nitrogen in pure water under 24 hours of simulated sunlight illumination, which is the highest efficiency of photocatalytic nitrogen fixation in pure water under solar energy conditions reported at home and abroad. Fe-doped TiO 2 can only produce 0.03 mg/L of ammonia nitrogen under the same conditions. Bi 2 O 3-x (x=0~1) composite photocatalytic material shows the advantages of efficient nitrogen fixation under natural conditions, and has application prospects;

2)Bi2O3-x/nBiaMOb光催化材料的制备方法无需特殊设备和苛刻条件,工艺简单,可控性强,容易实现规模化生产,具有实用性。2 ) The preparation method of the Bi 2 O 3-x /nBia MO b photocatalytic material does not require special equipment and harsh conditions, the process is simple, the controllability is strong, it is easy to realize large-scale production, and has practicability.

下面进一步例举实施例以详细说明本发明。同样应理解,以下实施例只用于对本发明进行进一步说明,不能理解为对本发明保护范围的限制,本领域的技术人员根据本发明的上述内容作出的一些非本质的改进和调整均属于本发明的保护范围。下述示例具体的工艺参数等也仅是合适范围中的一个示例,即本领域技术人员可以通过本文的说明做合适的范围内选择,而并非要限定于下文示例的具体数值。The following further examples are given to illustrate the present invention in detail. It should also be understood that the following examples are only used to further illustrate the present invention, and should not be construed as limiting the protection scope of the present invention. Some non-essential improvements and adjustments made by those skilled in the art according to the above content of the present invention belong to the present invention. scope of protection. The specific process parameters and the like in the following examples are only an example of a suitable range, that is, those skilled in the art can make selections within the suitable range through the description herein, and are not intended to be limited to the specific numerical values exemplified below.

实施例1Example 1

将1.2mmoL油酸钠溶于20mL去离子水中,溶解后加入0.194g Bi(NO3)3·5H2O,磁力搅拌1.5小时形成乳液状前驱体溶液;Dissolve 1.2 mmol of sodium oleate in 20 mL of deionized water, add 0.194 g Bi(NO 3 ) 3 ·5H 2 O after dissolving, and stir magnetically for 1.5 hours to form an emulsion-like precursor solution;

将0.4mmoL偏钒酸铵溶解在20mL去离子水中,搅拌1小时并超声使分散均匀;Dissolve 0.4 mmol of ammonium metavanadate in 20 mL of deionized water, stir for 1 hour and sonicate to make the dispersion uniform;

将两组溶液混合搅拌1小时后转移到50mL的水热釜中,在105℃水热反应16小时,自然冷却至室温;The two groups of solutions were mixed and stirred for 1 hour and then transferred to a 50mL hydrothermal kettle, hydrothermally reacted at 105°C for 16 hours, and naturally cooled to room temperature;

将水热釜中固体样品经正己烷,乙醇等洗涤后使用真空冷冻干燥技术获得粉体即为BiO/BiVO4复合材料。The solid sample in the hydrothermal kettle was washed with n-hexane, ethanol, etc., and then the powder was obtained by vacuum freeze-drying technology, which was the BiO/BiVO 4 composite material.

图1是本实施例获得的BiO/BiVO4复合材料的XRD衍射图谱,经XRD成分分析可知:所获得的复合光催化材料为单斜相BiVO4与少量六方相BiO。Figure 1 is the XRD diffraction pattern of the BiO/BiVO 4 composite material obtained in this example. The XRD component analysis shows that the obtained composite photocatalytic material is monoclinic BiVO 4 and a small amount of hexagonal BiO.

图2是本实施例获得的BiO/BiVO4复合材料的透射电镜照片,由图2可见:所获得的复合材料中BiVO4是由直径为40-50nm左右的纳米棒组成的结构,BiO是直径为3-4nm左右的纳米棒,并且BiO纳米棒紧密生长在BiVO4上。Fig. 2 is a transmission electron microscope photograph of the BiO/BiVO 4 composite material obtained in this example. It can be seen from Fig. 2 that: in the obtained composite material, BiVO 4 is a structure composed of nanorods with a diameter of about 40-50 nm, and BiO is a diameter of about 40-50 nm. are nanorods around 3-4 nm, and the BiO nanorods are tightly grown on BiVO 4 .

为了研究所制备样品的光催化固氮性能,设计模拟太阳光下材料在纯水体系中将空气中N2还原为NH4 +的实验。实施例中所述的“Fe掺杂TiO2”是参照文献(Appl.Catal.B:Environ.2014,144,468–477)制备而得。In order to study the photocatalytic nitrogen fixation performance of the prepared samples, an experiment was designed to simulate the reduction of N2 in air to NH4 + by the material in pure water system under sunlight. The "Fe-doped TiO 2 " described in the examples was prepared with reference to literature (Appl. Catal. B: Environ. 2014, 144, 468-477).

实验中通过水杨酸分光光度法(HJ 536-2009)测量NH4 +浓度。The NH 4 + concentration was measured by salicylic acid spectrophotometry (HJ 536-2009) in the experiment.

将等量的BiO/BiVO4复合材料和水热法制得的0.5wt%Fe掺杂TiO2纳米材料分别加入200mL纯水中,用稀盐酸调pH为3-4之间,然后置于500W氙灯下照射24小时,检测溶液中NH4 +浓度并记录结果。 The same amount of BiO/BiVO composite and 0.5wt% Fe-doped TiO nanomaterials prepared by hydrothermal method were added into 200 mL of pure water, respectively, and the pH was adjusted between 3-4 with dilute hydrochloric acid, and then placed in a 500W xenon lamp. Under irradiation for 24 hours, the NH 4 + concentration in the solution was measured and the results were recorded.

检测结果表明:光照24小时进行显色,发现BiO/BiVO4复合材料的悬浮液中的氨氮浓度达到3.9mg/L,说明所获得的BiO/BiVO4复合材料具有较高的光催化固氮能力。The detection results showed that the color development was carried out under light for 24 hours, and the ammonia nitrogen concentration in the suspension of BiO/BiVO 4 composite material was found to reach 3.9 mg/L, indicating that the obtained BiO/BiVO 4 composite material had a high photocatalytic nitrogen fixation ability.

图3示出本实施例获得的BiO/BiVO4复合材料与Fe掺杂TiO2纳米材料在模拟太阳光下光催化固氮(氙灯下还原空气中N2的)效率的对比图。由图3可见:所获得的BiO/BiVO4复合材料比Fe掺杂TiO2同样条件下固氮效率大幅提升。Figure 3 shows the comparison of the photocatalytic nitrogen fixation (reduction of N 2 in air under a xenon lamp) efficiency of the BiO/BiVO 4 composite obtained in this example and Fe-doped TiO 2 nanomaterials under simulated sunlight. It can be seen from Figure 3 that the obtained BiO/BiVO 4 composites have a significantly higher nitrogen fixation efficiency than Fe-doped TiO 2 under the same conditions.

实施例2Example 2

将2.2mmoL油酸钠溶于20mL去离子水中,溶解后加入0.194g Bi(NO3)3·5H2O,磁力搅拌1.5小时形成乳液状前驱体溶液,将前驱体溶液加入20mL去离子水后转移到50mL的水热釜中,在105℃水热反应20小时,自然冷却至室温;Dissolve 2.2 mmol of sodium oleate in 20 mL of deionized water, add 0.194 g Bi(NO 3 ) 3 ·5H 2 O after dissolving, and stir magnetically for 1.5 hours to form an emulsion-like precursor solution. Add the precursor solution to 20 mL of deionized water. Transfer to a 50mL hydrothermal kettle, hydrothermally react at 105°C for 20 hours, and naturally cool to room temperature;

将固体样品经乙醇等洗涤后使用真空冷冻干燥技术获得粉体即为BiO材料。The solid sample is washed with ethanol, etc., and then the powder is obtained by vacuum freeze-drying technology, which is the BiO material.

经XRD检测分析得知(见图4):本实施例所获得的材料为BiO材料(量子尺寸化的BiO(quantum sized BiO))。According to XRD detection and analysis (see FIG. 4 ), the material obtained in this example is a BiO material (quantum sized BiO).

本实施例所获得BiO材料比实施例1获得的复合材料相同条件下还原空气中氮气产生NH4 +的效率略低(见图3)。The BiO material obtained in this example is slightly less efficient than the composite material obtained in Example 1 in reducing nitrogen in air to generate NH 4 + (see FIG. 3 ).

实施例3Example 3

将1.2mmoL油酸钠溶于20mL去离子水中,溶解后加入0.194g Bi(NO3)3·5H2O,磁力搅拌1.5小时形成乳液状前驱体溶液;Dissolve 1.2 mmol of sodium oleate in 20 mL of deionized water, add 0.194 g Bi(NO 3 ) 3 ·5H 2 O after dissolving, and stir magnetically for 1.5 hours to form an emulsion-like precursor solution;

将0.1mmoL的钨酸钠溶解在20mL去离子水中,搅拌1小时并超声使分散均匀;Dissolve 0.1 mmol of sodium tungstate in 20 mL of deionized water, stir for 1 hour and sonicate to make the dispersion uniform;

将两组溶液混合搅拌1小时后转移到50mL的水热釜中,在105℃水热反应16小时,自然冷却至室温;The two groups of solutions were mixed and stirred for 1 hour and then transferred to a 50mL hydrothermal kettle, hydrothermally reacted at 105°C for 16 hours, and naturally cooled to room temperature;

将水热釜中固体样品经正己烷,乙醇等洗涤后使用真空冷冻干燥技术获得粉体即为BiO,Bi2O3,Bi2O2.33/Bi2WO6复合材料。The solid sample in the hydrothermal kettle is washed with n-hexane, ethanol, etc., and then vacuum freeze-drying technology is used to obtain powder, which is BiO, Bi 2 O 3 , Bi 2 O 2.33 /Bi 2 WO 6 composite material.

本实施例所获得的Bi2O3-x复合Bi2WO6光催化材料在与实施例1相同条件下获得BiO/BiVO4材料对光催化固氮效率为实施例1的85%。The Bi 2 O 3-x composite Bi 2 WO 6 photocatalytic material obtained in this example is 85% of the photocatalytic nitrogen fixation efficiency of the BiO/BiVO 4 material obtained under the same conditions as in Example 1.

实施例4Example 4

本实施例与实施例1的不同之处仅在于:制备过程中不加入油酸纳;The difference between this example and Example 1 is only: sodium oleate is not added in the preparation process;

其余内容均与实施例1中所述完全相同。The rest are exactly the same as described in Example 1.

本实施例产物经XRD成分分析确定为纯BiVO4相(见图5),说明油酸根离子的存在是形成BiO相的必要条件。The product of this example was determined to be pure BiVO 4 phase by XRD component analysis (see Figure 5), indicating that the existence of oleate ions is a necessary condition for the formation of BiO phase.

产物BiVO4与实施例1获得的BiO/BiVO4相比,相同条件下固氮效率只有复合材料的2%(见图3)。Compared with the BiO/BiVO 4 obtained in Example 1, the nitrogen fixation efficiency of the product BiVO 4 is only 2% of that of the composite material under the same conditions (see Figure 3).

Claims (11)

1. a kind of high-efficiency solar fixed nitrogen catalysis material, which is characterized in that the chemical composition of the catalysis material is BiO/ nBiaMOb, wherein n=0~1 and n are not 0, a=0~2 and a is not 0, b=0~6 and b is not 0, M V, at least one in Mo, W Kind, the diameter of BiO is 3-4 nanometers in the catalysis material.
2. catalysis material according to claim 1, which is characterized in that Bi in the catalysis materialaMObParticle it is straight Diameter is 1~1000 nanometer.
3. catalysis material according to claim 2, which is characterized in that Bi in the catalysis materialaMObParticle it is straight Diameter is 1~100 nanometer.
4. the preparation method of high-efficiency solar fixed nitrogen catalysis material, feature described in a kind of any one of claims 1 to 3 Be, the preparation method include: bismuth salt is soluble in water with enuatrol, stirring, emulsion form precursor solution A is made;By M salt It is dispersed in water, ultrasound obtains solution B;Suitable solution A is mixed with solution B, synthesized 2 hours in 80~180 DEG C or more, it washes Wash, dry after obtain the high-efficiency solar fixed nitrogen catalysis material.
5. the preparation method according to claim 4, which is characterized in that the bismuth salt is bismuth nitrate, bismuth chloride, bismuth ion network Close at least one of object.
6. the preparation method according to claim 4, which is characterized in that in solution A the molar concentration of Bi be 0.001~ 0.2mol/L。
7. the preparation method according to claim 4, which is characterized in that in solution A the molar concentration of enuatrol be 0.001~ 1mol/L。
8. the preparation method according to claim 4, which is characterized in that the mixing time of emulsion form precursor solution A is made It is 1~3 hour.
9. the preparation method according to claim 4, which is characterized in that the M salt is ammonium metavanadate, ammonium vanadate, five oxidations At least one of two vanadium, sodium tungstate, sodium molybdate, tungsten chloride, phosphotungstic acid, phosphomolybdic acid.
10. the preparation method according to claim 4, which is characterized in that in solution B the molar concentration of M salt be 0.001~ 0.1 mol/L。
11. the preparation method according to any one of claim 4 to 10, which is characterized in that generated time is 2~48 small When.
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