CN100408166C - AgTO2Visible light response photocatalysis material of type composite oxide and application thereof - Google Patents
AgTO2Visible light response photocatalysis material of type composite oxide and application thereof Download PDFInfo
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一.技术领域 1. Technical field
本发明涉及一种光催化材料(亦称光触媒)。尤其是可见光响应的光催化材料,这种光催化材料是Ag和另一种金属(常见化合价为+3)组成的AgTO2型复合氧化物(亦称多元金属氧化物)半导体材料及其应用。The invention relates to a photocatalytic material (also known as photocatalyst). Especially visible light-responsive photocatalytic materials, which are AgTO 2 composite oxide (also known as multi-element metal oxide) semiconductor materials composed of Ag and another metal (common valence is +3) and their applications.
二.技术背景2. Technical background
20世纪,经济的飞速增长和工业化大生产的腾飞带来了负面效应——地球生态环境日益恶劣,石油、煤等矿石能源短缺。二噁烷等环境荷尔蒙问题自不用说,水和大气中的农药及恶臭物质也威胁着人们安全而舒适的生活。21世纪,各国政府已充分意识到环境与能源问题,把环境净化、新能源开发、能源高效利用与节约等问题提升到关系到国家生存与发展的战略高度来对待,因而这方面相关的研究与技术开发备受关注。In the 20th century, the rapid economic growth and the take-off of large-scale industrial production brought negative effects—the earth’s ecological environment is getting worse and worse, and there is a shortage of ore energy such as oil and coal. Needless to say, environmental hormones such as dioxane, pesticides and odorous substances in water and air also threaten people's safe and comfortable life. In the 21st century, governments of various countries have been fully aware of environmental and energy issues, and raised environmental purification, new energy development, energy efficient utilization and conservation to a strategic level that is related to the survival and development of the country. Therefore, related research in this area and Technological development has attracted much attention.
利用光催化技术净化环境是一项全新的“绿色技术”,由于其耗能低,几乎完全靠太阳光能,以及二次污染几乎为零(在环境净化过程中不容易产生其它污染物),越来越受到各国政府的普遍重视,并成为各国学术界和产业界的研究热点。The use of photocatalytic technology to purify the environment is a brand new "green technology". Due to its low energy consumption, it relies almost entirely on solar energy, and the secondary pollution is almost zero (other pollutants are not easily produced during the environmental purification process). It has been paid more and more attention by the governments of various countries, and has become a research hotspot in the academic and industrial circles of various countries.
光催化材料是一种氧化物半导体材料,利用半导体自身的性质,在光照条件下,能发生如下反应:当光催化材料吸收了超过其带隙能量的光子后,生成空穴和电子,这些空穴与电子由催化剂内部运动到表面,因为空穴与电子具有强大的氧化与还原能力,所以可以将其周围的化学物质氧化和还原。在这里,氧化物半导体光催化材料的重要特性是其带隙的大小以及导带和禁带的能级。氧化物半导体价带的空穴具有非常强的氧化能力,可以把水以及多种有机物之类的电子给体氧化,而同时生成的导带电子需要通过还原空气中的氧气而被消耗掉。也就是说,该光催化材料发生反应的前提是其能带结构与反应物(水、有机物和氧气)的氧化电位和还原电位必须匹配。The photocatalytic material is an oxide semiconductor material. Using the properties of the semiconductor itself, the following reaction can occur under light conditions: when the photocatalytic material absorbs photons exceeding its band gap energy, holes and electrons are generated, and these holes The holes and electrons move from the inside of the catalyst to the surface. Because the holes and electrons have strong oxidation and reduction capabilities, they can oxidize and reduce the chemical substances around them. Here, the important characteristics of oxide semiconductor photocatalytic materials are the size of their bandgap and the energy levels of conduction and forbidden bands. The holes in the valence band of oxide semiconductors have a very strong oxidation ability, which can oxidize electron donors such as water and various organic substances, while the conduction band electrons generated at the same time need to be consumed by reducing oxygen in the air. That is to say, the prerequisite for the photocatalytic material to react is that its energy band structure must match the oxidation potential and reduction potential of the reactants (water, organic matter and oxygen).
光催化材料在光照射下能有效地去除空气中有害物质和杀菌:将空气中VOCs(挥发性有机化合物,包括醇类气体、醛类气体、挥发性酮类气体、挥发性苯系物等污染气体)、硫化物、氮氧化物直接氧化分解成二氧化碳、水或其它无毒无害物质;能够高效地破坏各种细菌的细胞膜,凝固各种病毒的蛋白质,达到杀菌的目的。在国外现已广泛应用于家庭、办公楼、会议室、室内公共场所、医院病房、幼儿院、学校、微机房以及汽车、火车、轮船、飞机交通工具等环境。目前以化学性质稳定的二氧化钛(TiO2)为主要研究对象,其广泛的工业应用受到极大制约,主要存在的问题包括:1.量子产率低,总反应速率较慢,难以处理量大且浓度高的工业废气和废水;2.太阳能利用率低,由于二氧化钛的带隙是3.2eV,只有在比400nm短的紫外线的照射下才能显现活性,所以其只能吸收利用太阳光中的紫外线部分,不能吸收可见光,因而只能在室外或者有紫外灯的地方工作。射入地表的太阳光,在可见光波长为500nm附近达到最大辐射强度,波长400~750nm的可见光范围的能量是全部太阳光能量的43%。而波长400nm以下的紫外线中的能量约4%。如果能够使材料吸收的波长范围扩大,有效地利用可见光,那么光催化材料的效率将显著提高。因此开发具有高量子产率,能被太阳光谱中的可见光激发的高效半导体光催化材料,是解决当前光催化技术中难题的关键。Photocatalytic materials can effectively remove harmful substances and sterilize the air under light irradiation: VOCs (volatile organic compounds in the air, including alcohol gases, aldehyde gases, volatile ketone gases, volatile benzene series, etc. Gas), sulfide, nitrogen oxides are directly oxidized and decomposed into carbon dioxide, water or other non-toxic and harmless substances; it can efficiently destroy the cell membranes of various bacteria, coagulate the proteins of various viruses, and achieve the purpose of sterilization. In foreign countries, it has been widely used in homes, office buildings, conference rooms, indoor public places, hospital wards, kindergartens, schools, computer rooms, and automobiles, trains, ships, and aircraft vehicles. At present, titanium dioxide (TiO 2 ) with stable chemical properties is the main research object, and its wide industrial application is greatly restricted. The main problems include: 1. The quantum yield is low, the overall reaction rate is slow, and it is difficult to process large quantities and High concentration of industrial waste gas and wastewater; 2. Low utilization rate of solar energy. Since the band gap of titanium dioxide is 3.2eV, it can only show activity under the irradiation of ultraviolet rays shorter than 400nm, so it can only absorb and utilize the ultraviolet part of sunlight , cannot absorb visible light, so it can only work outdoors or in places with ultraviolet lamps. The sunlight entering the earth's surface reaches the maximum radiation intensity near the visible wavelength of 500nm, and the energy in the range of visible light with a wavelength of 400-750nm is 43% of the total solar energy. The energy in ultraviolet light with a wavelength below 400nm is about 4%. If the wavelength range absorbed by the material can be expanded to effectively utilize visible light, the efficiency of photocatalytic materials will be significantly improved. Therefore, the development of high-efficiency semiconductor photocatalytic materials with high quantum yields that can be excited by visible light in the solar spectrum is the key to solving the current problems in photocatalytic technology.
三.发明内容 3. Contents of the invention
本发明目的是:开发出一系列光催化材料,其既能吸收太阳光中的紫外光,又能吸收可见光的新型光催化材料,并且能高效地发生光催化反应。通过对该催化剂进行光照,其能够分解有害物质,从而提供有害物质的净化处理方法。提出本发明的研究小组,一直致力于环境污染治理的研究,提出了有关利用光催化材料的控制治理污染的各种方案,开发了多项发明。The purpose of the present invention is to develop a series of photocatalytic materials, which can not only absorb ultraviolet light in sunlight, but also absorb visible light, and can efficiently generate photocatalytic reactions. By illuminating the catalyst, it can decompose harmful substances, thereby providing a method for purifying and treating harmful substances. The research group that proposed the present invention has been devoting itself to the research of environmental pollution control, proposed various schemes for the control and control of pollution using photocatalytic materials, and developed a number of inventions.
本发明的技术解决方案是:Technical solution of the present invention is:
1.通式为AgTO2型复合氧化物可见光响应光催化材料,式中T表示Al,Ga,In,Cr,Fe,Co,Ni元素,即包含半导体材料AgAiO2、AgGaO2、AgInO2、AgCrO2、AgFeO2、AgCoO2、AgNiO2。1. The general formula is AgTO 2 composite oxide visible light responsive photocatalytic material, where T represents Al, Ga, In, Cr, Fe, Co, Ni elements, including semiconductor materials AgAiO 2 , AgGaO 2 , AgInO 2 , AgCrO 2. AgFeO 2 , AgCoO 2 , AgNiO 2 .
2.AgTO2型复合氧化物可见光响应光催化材料的合成方法。采用Ag和金属T的氧化物、氢氧化物、各种无机盐及有机盐类为原料,按照Ag与金属T摩尔比1∶1配比,根据如下制备方法,采用不同的工艺条件,制备出正交晶系或六方晶系的AgTO2:2. Synthesis method of AgTO 2 type composite oxide visible light responsive photocatalytic material. Using oxides, hydroxides, various inorganic salts and organic salts of Ag and metal T as raw materials, according to the molar ratio of Ag and metal T 1:1, according to the following preparation method, using different process conditions, prepared Orthorhombic or hexagonal AgTO 2 :
(1)离子交换法:先要合成出对应的前驱体样品LiTO2、NaTO2、KTO2(T=Al,Ga,In,Cr,Fe,Co,Ni),建议采用Li2CO3与T2O3(T=Al,Ga,In,Cr,Fe,Co,Ni)进行反应制备LiTO2,反应温度为500-1200℃(根据前驱体材料不同采用不同烧结温度),烧结12小时,然后将LiTO2、AgNO3、KNO3按一定比例混合并研磨(干法研磨),研磨完成后,将混合好的样品转移至坩埚中,在电炉中,以270℃-400℃(根据材料不同采用不同烧结温度)烧结12小时可得到样品,用蒸馏水清洗掉可溶性物质可得AgTO2样品,干燥样品备用。(1) Ion exchange method: firstly, the corresponding precursor samples LiTO 2 , NaTO 2 , KTO 2 (T=Al, Ga, In, Cr, Fe, Co, Ni) should be synthesized. Li 2 CO 3 and T 2 O 3 (T=Al, Ga, In, Cr, Fe, Co, Ni) was reacted to prepare LiTO 2 at a reaction temperature of 500-1200°C (different sintering temperatures were used depending on the precursor material), sintered for 12 hours, and then Mix and grind LiTO 2 , AgNO 3 , and KNO 3 in a certain proportion (dry grinding). After the grinding is completed, transfer the mixed sample to a crucible. Different sintering temperatures) sintered for 12 hours to obtain samples, washed away the soluble matter with distilled water to obtain AgTO 2 samples, and dried the samples for later use.
(2)水热合成法:采用Ag和金属T(+3价)的氧化物、氢氧化物为原料,按照Ag与金属T摩尔比1∶1配比放入特富龙的高压釜内胆中,加入一定量NaOH作添加剂,再加入一定量的水,将高压釜内胆装入高压釜内,旋紧高压釜的盖,在120℃-200℃的环境下保温5-20小时,取出样品后干燥备用。(2) Hydrothermal synthesis method: use oxides and hydroxides of Ag and metal T (+3 valence) as raw materials, and put them into the Teflon autoclave liner according to the molar ratio of Ag and metal T in a ratio of 1:1 Add a certain amount of NaOH as an additive, then add a certain amount of water, put the autoclave liner into the autoclave, tighten the lid of the autoclave, keep it warm for 5-20 hours at 120°C-200°C, take it out The samples were then dried for later use.
(3)溶胶-凝胶合成法:以Ag和金属T(+3价)的可溶性盐(包括溶于水或溶于有机溶剂)为原料,按照Ag与金属T摩尔比1∶1配比原料,水或有机物为溶剂,加入适当的络合剂,在烘箱中将溶胶烘干变为凝胶,凝胶放入电炉,在300℃保温3小时,再在还原性气氛下,以400℃-1200℃(根据材料不同采用不同烧结温度)温度下烧结3-10小时,烧结温度和时间不同可以制备不同粒径的纳米的AgTO2样品。(3) Sol-gel synthesis method: using soluble salts of Ag and metal T (+3 valence) (including soluble in water or soluble in organic solvents) as raw materials, according to the molar ratio of Ag and metal T 1:1 ratio of raw materials , water or organic matter as a solvent, add an appropriate complexing agent, dry the sol in an oven to become a gel, put the gel in an electric furnace, keep it at 300°C for 3 hours, and then in a reducing atmosphere, heat it at 400°C- Sintering at 1200°C (different sintering temperature according to different materials) for 3-10 hours, different sintering temperature and time can prepare nano AgTO 2 samples with different particle sizes.
(4)共沉淀法:以Ag和金属T(+3价)的可溶性盐(包括溶于水或溶于有机溶剂)为原料,按照Ag与金属T摩尔比1∶1配比原料,水或有机物为溶剂,调节pH值大于10可使Ag+和金属T的离子沉淀,过滤出沉淀,在电炉中,还原性气氛下,以400℃-1200℃(根据材料不同采用不同烧结温度)烧结3-12小时,烧结温度和时间不同可以制备不同粒径的纳米AgTO2样品。(4) Co-precipitation method: using soluble salts of Ag and metal T (+3 valence) (including soluble in water or organic solvents) as raw materials, according to the molar ratio of Ag and metal T 1:1 ratio of raw materials, water or The organic matter is a solvent, adjusting the pH value to be greater than 10 can cause Ag + and metal T ions to precipitate, filter out the precipitate, and sinter at 400°C-1200°C (different sintering temperatures are used according to different materials) in an electric furnace under a reducing atmosphere for 3 -12 hours, different sintering temperature and time can prepare nano-AgTO 2 samples with different particle sizes.
对于2所述的(1)-(4)的方法,建议采用(1)离子交换法,因为金属元素T多数存在多种化合价,利用离子交换法可以控制金属元素T化合价在前驱体样品中为+3价,也保证了在AgTO2中为+3价,使得其晶体结构可控,减少晶体内部的缺陷。For the method of (1)-(4) described in 2, it is recommended to use (1) ion exchange method, because most of the metal elements T have multiple valences, and the ion exchange method can be used to control the metal element T valence in the precursor sample. The +3 valence also ensures the +3 valence in AgTO 2 , making its crystal structure controllable and reducing defects inside the crystal.
3.AgTO2型复合氧化物可见光响应光催化材料的掺杂改性方法。可以在AgTO2中掺入一定量的金属实现如稳定性、耐光性等性质的改性。这些金属包括:碱金属、碱土金属、过渡族金属、Ge、Sn、Pb、Sb、Bi。采用上述金属的氧化物、氢氧化物、各种无机盐及有机盐类为原料,可以实现掺杂改性,掺杂量为0.1%-10%(质量分数)。制备工艺如下:3. Doping modification method of visible light-responsive photocatalytic material of AgTO 2 type composite oxide. A certain amount of metal can be doped in AgTO 2 to realize the modification of properties such as stability and light resistance. These metals include: alkali metals, alkaline earth metals, transition metals, Ge, Sn, Pb, Sb, Bi. The above-mentioned metal oxides, hydroxides, various inorganic salts and organic salts are used as raw materials to realize doping modification, and the doping amount is 0.1%-10% (mass fraction). The preparation process is as follows:
对于2中所述的方法(1)-(4)分三组按下列方法实现:For method (1)-(4) described in 2, divide into three groups and realize by the following methods:
(1)对于离子交换法,在制备前驱体样品时就进行掺杂,加入含掺杂金属的氧化物、氢氧化物或者金属单质到Li2CO3与T2O3(T=Al,Ga,In,Cr,Fe,Co,Ni)的混合物中,进行前驱体制备,然后按2中(1)所述的制备工艺实施即可。(1) For the ion exchange method, doping is carried out when the precursor sample is prepared, and oxides, hydroxides or simple metals containing doped metals are added to Li 2 CO 3 and T 2 O 3 (T=Al, Ga , In, Cr, Fe, Co, Ni) mixture, the precursor preparation is carried out, and then the preparation process described in (1) in 2 can be implemented.
(2)对于水热合成法,按照掺杂量加入含掺杂金属的氧化物、氢氧化物或者金属单质到原料中,按2中(2)所述的制备工艺实施即可。(2) For the hydrothermal synthesis method, add oxides, hydroxides or simple metals containing doped metals to the raw materials according to the doping amount, and implement according to the preparation process described in (2) in 2.
(3)对于溶胶-凝胶合成法、共沉淀法,按照掺杂量加入含掺杂金属的可溶性盐(包括溶于水或溶于有机溶剂)到原料中,按2中(3)(4)所述的制备工艺实施即可。(3) For the sol-gel synthesis method and the co-precipitation method, add soluble salts containing doping metals (including soluble in water or soluble in organic solvents) to the raw materials according to the doping amount, according to 2 in (3) (4) ) The preparation process described in can be implemented.
4.纳米AgTO2,AgTO2掺杂改性材料的制备。4. Preparation of nano AgTO 2 , AgTO 2 doped modified materials.
按2,3所述制备的样品粒径范围通常是100nm-2000nm,当需要将材料分散到涂料、油漆中,或者涂覆、印刷在不同的材料表面上制备成各种薄膜或表面层,如玻璃、钢板、塑料、橡胶、纸张、木材、铝板、陶瓷、陶器、布料,以及建筑物的外表面和内表面,通常需要制备纳米的AgTO2、AgTO2掺杂改性材料。有多种物理或化学的方法,但采用球磨粉碎的方法最佳。一般将样品球磨半小时到50小时,超过50小时可能导致材料晶体结构的改变及性能的下降。最终可以得到粒径为10nm-100nm的粉体,这也是粒子的最佳粒径范围。The particle size range of the samples prepared as described in 2 and 3 is usually 100nm-2000nm. When it is necessary to disperse the material into the paint, paint, or coat and print on the surface of different materials to prepare various films or surface layers, such as Glass, steel plate, plastic, rubber, paper, wood, aluminum plate, ceramics, pottery, cloth, as well as the exterior and interior surfaces of buildings usually require the preparation of nanometer AgTO 2 and AgTO 2 doped modified materials. There are many physical or chemical methods, but the method of ball milling is the best. Generally, the sample is ball milled for half an hour to 50 hours, and more than 50 hours may lead to changes in the crystal structure of the material and a decrease in performance. Finally, a powder with a particle size of 10nm-100nm can be obtained, which is also the optimal particle size range of the particles.
5.AgTO2型复合氧化物可见光响应光催化材料的复合材料的制备。5. Preparation of composite materials of AgTO 2 type composite oxide visible light responsive photocatalytic materials.
(1)以2,3,4制备出的AgTO2或掺杂改性材料为主体材料,可以在其表面担载(生长)以下纳米金属颗粒:Ti、Zr、Hf、V、Nb、Ta、Cr、Mo、W、Ru、Co、Ni、Pd、Pt、Cu、Ag、Au、Zn、Cd、Al、Ga、In、Ge、Sn、Pb、Sb、Bi,制备出AgTO2或AgTO2掺杂改性材料为主体材料的复合材料M/AgTO2或者M/(AgTO2掺杂改性材料)(M=金属),可进一步提高催化效率,以含有上述金属元素的可溶性盐类为原料,担载量为1%-10%(质量分数)。具体方法如下:(1) Using AgTO 2 or doped modified materials prepared by 2, 3, 4 as the main material, the following nano-metal particles can be supported (growth) on its surface: Ti, Zr, Hf, V, Nb, Ta, Cr, Mo, W, Ru, Co, Ni, Pd, Pt, Cu, Ag, Au, Zn, Cd, Al, Ga, In, Ge, Sn, Pb, Sb, Bi, prepared AgTO 2 or AgTO 2 doped The composite material M/AgTO 2 or M/(AgTO 2 doped modified material) (M=metal) with hetero-modified material as the main material can further improve the catalytic efficiency, using soluble salts containing the above-mentioned metal elements as raw materials, The loading amount is 1%-10% (mass fraction). The specific method is as follows:
以AgTO2或者AgTO2的掺杂改性材料为主体材料,以Ti、Zr、Hf、V、Nb、Ta、Cr、Mo、W、Ru、Co、Ni、Pd、Pt、Cu、Ag、Au、Zn、Cd、Al、Ga、In、Ge、Sn、Pb、Sb、Bi的可溶性盐类为担载材料的原料,先将这些可溶性盐类溶解配置成一定浓度的溶液,根据担载量(一般按质量分数)量取一定体积的溶液与主体材料一起研磨,研磨后放置到烘箱中烘干,然后将粉末放置到管式炉中采用合适的气氛处理一定时间,可以得到M/AgTO2、M/(AgTO2掺杂改性材料)复合材料(M=金属)。With AgTO 2 or AgTO 2 doped modified material as the main material, with Ti, Zr, Hf, V, Nb, Ta, Cr, Mo, W, Ru, Co, Ni, Pd, Pt, Cu, Ag, Au , Zn, Cd, Al, Ga, In, Ge, Sn, Pb, Sb, Bi soluble salts are the raw materials of the loading materials, these soluble salts are first dissolved and configured into a solution of a certain concentration, according to the loading ( Generally, a certain volume of solution is measured according to the mass fraction) and ground together with the main material. After grinding, it is placed in an oven for drying, and then the powder is placed in a tube furnace and treated with a suitable atmosphere for a certain period of time. M/AgTO 2 , M/(AgTO 2 doped modified material) composite (M=metal).
(2)以2,3,4制备出的AgTO2或掺杂改性材料为主体材料,可以在其表面担载(生长)如下纳米金属氧化物颗粒:过渡族金属氧化物、Al2O3、Ga2O3、In2O3、GeO2、SnO2、PbO、PbO2、Sb2O3、Sb2O5、Bi2O3、Bi2O4,制备出MxOy/AgTO2或者MxOy/(AgTO2掺杂改性材料)复合材料(M=金属),可进一步提高催化效率,以含有上述氧化物的金属元素的可溶性盐类为原料,担载量为1%-10%(质量分数)。具体方法如下:(2) Using AgTO 2 or doped modified materials prepared by 2, 3, 4 as the main material, the following nano-metal oxide particles can be supported (grown) on its surface: transition group metal oxides, Al 2 O 3 , Ga 2 O 3 , In 2 O 3 , GeO 2 , SnO 2 , PbO, PbO 2 , Sb 2 O 3 , Sb 2 O 5 , Bi 2 O 3 , Bi 2 O 4 , prepared M x O y /AgTO 2 or M x O y / (AgTO 2 doped modified material) composite material (M = metal), which can further improve the catalytic efficiency, using soluble salts of metal elements containing the above oxides as raw materials, with a loading capacity of 1 %-10% (mass fraction). The specific method is as follows:
以AgTO2或者AgTO2的掺杂改性材料为主体材料,以过渡族金属、Al、Ga、In、Ge、Sn、Pb、Sb、Bi的可溶性盐类为担载材料的原料,先将这些可溶性盐类溶解配置成一定浓度的溶液,根据担载量(一般按质量分数)量取一定体积的溶液与主体材料一起研磨,研磨后放置到烘箱中烘干,然后将粉末放置到管式炉中采用合适的气氛处理一定时间,得到MxOy/AgTO2、MxOy/(AgTO2掺杂改性材料)复合材料(M=金属)。Using AgTO 2 or AgTO 2 doped modified materials as the main material, and soluble salts of transition metals, Al, Ga, In, Ge, Sn, Pb, Sb, Bi as the raw materials of the loading materials, these Soluble salts are dissolved and configured into a solution with a certain concentration. Measure a certain volume of the solution according to the loading capacity (generally by mass fraction) and grind it with the main material. After grinding, put it in an oven for drying, and then put the powder into a tube furnace Treat in a suitable atmosphere for a certain period of time to obtain M x O y /AgTO 2 , M x O y /(AgTO 2 doped modified material) composite materials (M = metal).
6.AgTO2、AgTO2掺杂改性材料、M/AgTO2、M/(AgTO2掺杂改性材料)、MxOy/AgTO2、MxOy/(AgTO2掺杂改性材料)薄膜的制备方法。6. AgTO 2 , AgTO 2 doped modified material, M/AgTO 2 , M/(AgTO 2 doped modified material), M x O y /AgTO 2 , M x O y /(AgTO 2 doped modified material material) film preparation method.
将粉体材料制备成薄膜材料可以节省原料的用量以及扩展材料的应用范围。对于AgTO2、AgTO2掺杂改性材料、M/AgTO2、M/(AgTO2掺杂改性材料)、MxOy/AgTO2、MxOy/(AgTO2掺杂改性材料)的薄膜的制备,方法如下:The preparation of powder materials into film materials can save the amount of raw materials and expand the application range of materials. For AgTO 2 , AgTO 2 doped modified material, M/AgTO 2 , M/(AgTO 2 doped modified material), M x O y /AgTO 2 , M x O y /(AgTO 2 doped modified material ) of the thin film, the method is as follows:
(1)以2,3,4,5制备出的粉末,加入溶剂、粘合剂等制成浆状物,直接用刮刀法(Doctor Blade Method)将浆状物涂覆在基片上,在400℃烧结2-5小时可制作出薄膜。(1) The powder prepared by 2, 3, 4, 5 is added with solvent, binder, etc. to make a slurry, and the slurry is directly coated on the substrate by the Doctor Blade Method, and the Sintering at ℃ for 2-5 hours can produce a thin film.
(2)2,3,4,5制备出的粉末也可利用物理的方法(蒸发镀膜、溅射镀膜等等)可以制备出AgTO2、AgTO2掺杂改性材料、M/AgTO2、M/(AgTO2掺杂改性材料)、MxOy/AgTO2、MxOy/(AgTO2掺杂改性材料)的薄膜。(2) The powders prepared by 2, 3, 4, and 5 can also be prepared by physical methods (evaporation coating, sputtering coating, etc.) to prepare AgTO 2 , AgTO 2 doped modified materials, M/AgTO 2 , M /(AgTO 2 doped modified material), M x O y /AgTO 2 , M x O y /(AgTO 2 doped modified material) thin film.
(3)还可以用化学的方法,如溶胶-凝胶法,来制备AgTO2或AgTO2掺杂改性材料的薄膜,然后再在薄膜表面担载(生长)金属或金属氧化物的纳米颗粒。(3) It is also possible to use chemical methods, such as the sol-gel method, to prepare AgTO 2 or AgTO 2 doped modified material films, and then support (grow) metal or metal oxide nanoparticles on the film surface .
7.将上述2,3,4,5的复合氧化物半导体光催化材料分散到涂料、油漆中,添加量为0.2%-2%(质量分数),或者加入不同的分散剂和溶剂内,涂覆或印刷在不同的材料表面上制备成各种薄膜或表面层,如玻璃、钢板、塑料、橡胶、纸张、木材、铝板、陶瓷、陶器、布料表面,涂覆量为100mg/m2,使这些材料成为环保产品。7. Disperse the composite oxide semiconductor photocatalyst materials of the above 2, 3, 4, 5 into coatings and paints, the addition amount is 0.2%-2% (mass fraction), or add different dispersants and solvents, coat Coated or printed on the surface of different materials to prepare various films or surface layers, such as glass, steel plate, plastic, rubber, paper, wood, aluminum plate, ceramics, pottery, cloth surface, the coating amount is 100mg/m 2 , so that These materials become environmentally friendly products.
8.将上述2,3,4,5,6制备的粉体材料或者薄膜材料放入特制的环境净化器内使用,按需要确定添加量,实现环境净化。8. Put the powder material or film material prepared in 2, 3, 4, 5, and 6 above into a special environmental purifier for use, and determine the amount of addition as required to achieve environmental purification.
本发明的特点是:The features of the present invention are:
1.催化的高效性。一方面,表现在高的可见光光响应性上:本发明开发了与以往开发的光催化材料完全不同的新型光催化材料,由于光催化材料受光激发的空穴与电子需要从催化剂内部传输到表面才能被运用,因而需要消耗掉一些能量在空穴与电子的传输上,所以一些窄带隙材料(能带带隙小于1.6eV)不能表现出高的光催化活性,即使它们能吸收长波长的光,这部分光的能量只能提供传输空穴与电子,而不能提供发生光催化反应的能量,而本发明开发的AgTO2型复合氧化物新型光催化材料,其能带带隙均位于1.6eV-2.8eV的范围内,多数能强烈地吸收可见光,部分材料光吸收的波长范围几乎覆盖整个可见光部分。同时,由于其特殊的晶体结构,使其在传输空穴和电子上消耗的能量很低。这两方面的原因决定了该材料高的可见光光响应性,表现出高的催化活性。1. High catalytic efficiency. On the one hand, it is manifested in high visible light photoresponsiveness: the present invention has developed a new type of photocatalytic material that is completely different from the photocatalytic materials developed in the past, because the holes and electrons excited by the photocatalytic material need to be transported from the inside of the catalyst to the surface To be used, some energy needs to be consumed in the transport of holes and electrons, so some narrow bandgap materials (bandgap less than 1.6eV) cannot show high photocatalytic activity, even if they can absorb long-wavelength light , the energy of this part of light can only provide the energy for transporting holes and electrons, but cannot provide the energy for the photocatalytic reaction, and the AgTO 2 type composite oxide new photocatalytic material developed by the present invention has an energy band gap of 1.6eV In the range of -2.8eV, most of them can strongly absorb visible light, and the wavelength range of light absorption of some materials almost covers the entire visible light part. At the same time, due to its special crystal structure, the energy consumed in transporting holes and electrons is very low. These two reasons determine the high visible light photoresponsiveness of the material and show high catalytic activity.
2.制备方法的多样性。一个材料能否实用,其合成方法具有一定影响,多样化制备的可行性,决定该材料可以从不同的原料出发而制备,因而生产可以不受地域差异的影响,可以选择更廉价的原料以降低成本。本发明开发的AgTO2型复合氧化物新型光催化材料,可以使用多种方法制备,如离子交换法、水热合成法、溶胶-凝胶合成法、共沉淀法等。原料根据制备方法的不同,可以采用Ag和另一种金属的氧化物、氢氧化物、各种无机盐及有机盐类为原料。2. Diversity of preparation methods. Whether a material is practical or not depends on its synthetic method. The feasibility of diversified preparation determines that the material can be prepared from different raw materials, so the production can not be affected by regional differences, and cheaper raw materials can be selected to reduce the production cost. cost. The AgTO 2 composite oxide novel photocatalytic material developed by the present invention can be prepared by various methods, such as ion exchange method, hydrothermal synthesis method, sol-gel synthesis method, co-precipitation method and the like. According to the different preparation methods, the raw materials can be Ag and another metal oxide, hydroxide, various inorganic salts and organic salts as raw materials.
3.对有机污染物普遍适用性。可以光催化降解有害有机色素:偶氮染料、硝基染料、硫化染料、蒽醌染料等。可以光催化降解挥发性有害有机气体:烷烃类、烯烃类、炔烃类、醇类、醛类、酮类、苯及其同系物、多环芳香烃、卤代烃等。3. Universal applicability to organic pollutants. It can photocatalytically degrade harmful organic pigments: azo dyes, nitro dyes, sulfur dyes, anthraquinone dyes, etc. It can photocatalytically degrade volatile harmful organic gases: alkanes, alkenes, alkynes, alcohols, aldehydes, ketones, benzene and its homologues, polycyclic aromatic hydrocarbons, halogenated hydrocarbons, etc.
本发明是关于能高效吸收太阳光中包含的紫外光和可见光的新型光催化材料AgTO2型复合氧化物及其复合材料的制备与应用。通过对该催化剂或以其为主体材料的复合材料的光照,将空气中存在的VOCs、硫化物、氮氧化物或者是水中的有害有机物直接氧化分解成二氧化碳、水或其它无毒无害物质,从而提供有害物质的无害化处理方法。The invention relates to the preparation and application of a novel photocatalytic material AgTO 2 type composite oxide capable of efficiently absorbing ultraviolet light and visible light contained in sunlight and a composite material thereof. By illuminating the catalyst or the composite material with it as the main material, the VOCs, sulfides, nitrogen oxides in the air or harmful organic substances in the water are directly oxidized and decomposed into carbon dioxide, water or other non-toxic and harmless substances, Thereby, a harmless treatment method for harmful substances is provided.
本发明的AgTO2型复合氧化物半导体光催化材料(T=Al,Ga,In,Cr,Fe,Co,Ni),如上所述,在宽的光谱内具有高的催化活性,使用的条件不苛刻,可以耐久使用,并且可以通过对AgTO2进行掺杂改性增长材料的使用寿命,更进一步,可以生产出M/AgTO2,M/(AgTO2掺杂改性材料),MxOy/AgTO2,MxOy/(AgTO2掺杂改性材料)复合材料(M=金属)以及对应的薄膜材料,向市场提供适应工业或生活不同需要的多样化产品,因而商业化前景广阔。The AgTO 2 -type compound oxide semiconductor photocatalytic material (T=Al, Ga, In, Cr, Fe, Co, Ni) of the present invention, as mentioned above, has high catalytic activity in a wide spectrum, and the conditions of use are different. Harsh, can be used durablely, and the service life of the material can be increased by doping and modifying AgTO 2. Further, M/AgTO 2 , M/(AgTO 2 doped modified material), M x O y can be produced /AgTO 2 , M x O y /(AgTO 2 doped modified material) composite material (M=metal) and corresponding thin film materials, provide the market with diversified products that meet different needs of industry or life, so the commercialization prospect is broad .
四.具体实施方式 4. Specific implementation
实施例1Example 1
离子交换法制备AgTO2:Preparation of AgTO 2 by ion exchange method:
在本发明中,利用离子交换法合成AgTO2(T=Al,Ga,In,Cr,Fe,Co,Ni)时,使用原料如下(全部由国药集团化学试剂有限公司生产):Li2CO3(99.99%)、Al2O3(99.99%)、Ga2O3(99.9%)、In2O3(99.9%)、Cr2O3(99.0%)、Fe2O3(99.0%)、Co2O3(99.0%)、NiO(99.0%)、AgNO3(99.8%)和KNO3(99.0%)。按照化学计量比先制备LiTO2(T=Al,Ga,In,Cr,Fe,Co,Ni):LiAlO2、LiCoO2用Li2CO3与Al2O3或Co2O3在900℃烧结12小时而得;LiGaO2、LiInO2、LiCrO2、LiFeO2用Li2CO3与Ga2O3、In2O3、Cr2O3、Fe2O3分别在750℃烧结12小时而得;LiNiO2用Li2CO3与NiO在650℃烧结12小时而得。得到的前驱体样品与AgNO3、KNO3按摩尔比1∶3∶1配比混合,然后在275℃-400℃之间烧结12小时,烧结完毕后取出样品清洗,剩余沉淀在室温干燥备用。利用如上工艺制备的粉体的粒径为200nm-1000nm,利用可以用球磨粉碎机进行粉碎,以缩小粒子直径,粒径的大小一般为10nm-200nm,而效果最佳的粒径范围是10-100nm。In the present invention, when using the ion exchange method to synthesize AgTO 2 (T=Al, Ga, In, Cr, Fe, Co, Ni), the raw materials used are as follows (all produced by Sinopharm Chemical Reagent Co., Ltd.): Li 2 CO 3 (99.99%), Al 2 O 3 (99.99%), Ga 2 O 3 (99.9%), In 2 O 3 (99.9%), Cr 2 O 3 (99.0%), Fe 2 O 3 (99.0%), Co 2 O 3 (99.0%), NiO (99.0%), AgNO 3 (99.8%) and KNO 3 (99.0%). Prepare LiTO 2 (T=Al, Ga, In, Cr, Fe, Co, Ni) according to the stoichiometric ratio: LiAlO 2 and LiCoO 2 are sintered with Li 2 CO 3 and Al 2 O 3 or Co 2 O 3 at 900°C Obtained in 12 hours; LiGaO 2 , LiInO 2 , LiCrO 2 , and LiFeO 2 are obtained by sintering Li 2 CO 3 with Ga 2 O 3 , In 2 O 3 , Cr 2 O 3 , and Fe 2 O 3 at 750°C for 12 hours, respectively. ; LiNiO 2 obtained by sintering Li 2 CO 3 and NiO at 650 ° C for 12 hours. The obtained precursor sample was mixed with AgNO 3 and KNO 3 in a molar ratio of 1:3:1, and then sintered at 275°C-400°C for 12 hours. After sintering, the sample was taken out for cleaning, and the remaining precipitate was dried at room temperature for later use. The particle size of the powder prepared by the above process is 200nm-1000nm, and it can be crushed with a ball mill to reduce the particle diameter. The particle size is generally 10nm-200nm, and the particle size range with the best effect is 10- 100nm.
实施例2Example 2
以AgTO2或AgTO2掺杂改性材料为主体材料制备M/AgTO2、MxOy/AgTO2、M/(AgTO2掺杂改性材料)、MxOy/(AgTO2掺杂改性材料)复合材料: M /AgTO 2 , M x O y /AgTO 2 , M/(AgTO 2 doped modified material), M x O y / (AgTO 2 doped Modified material) composite material:
取1g实施例1制备的AgTO2粉体若干份,根据担载量量取配制好的AgNO3(1g/100ml),Bi(NO3)3·5H2O(1g/100ml),Ni(NO3)2·6H2O(1g/100ml),Zn(NO3)2·6H2O(1g/100ml),H2PtCl6·6H2O(1g/100ml),RuCl3·3H2O(1g/100ml)等盐溶液,将AgTO2粉体与盐溶液混合研磨半小时,在烘箱中干燥,若要制备M/AgTO2复合材料(M=金属),则将粉末放置到管式炉以300-1200℃(根据上述盐的分解温度不同而使用不同的烧结温度),在空气气氛中烧结3-12小时,再在氢气还原气氛下烧结3-12小时,得到M/AgTO2;若要制备MxOy/AgTO2复合材料(M=金属)则将粉末放置到管式炉以300-1200℃(根据上述盐的分解温度不同而使用不同的烧结温度),在空气气氛中烧结3-12小时,得到MxOy/AgTO2。Take several parts of 1g of the AgTO 2 powder prepared in Example 1, and measure the prepared AgNO 3 (1g/100ml), Bi(NO 3 ) 3 ·5H 2 O (1g/100ml), Ni(NO 3 ) 2 ·6H 2 O(1g/100ml), Zn(NO 3 ) 2 ·6H 2 O(1g/100ml), H 2 PtCl 6 ·6H 2 O(1g/100ml), RuCl 3 ·3H 2 O( 1g/100ml) and other salt solution, mix and grind AgTO 2 powder with the salt solution for half an hour, and dry in an oven. To prepare M/AgTO 2 composite material (M = metal), put the powder in a tube furnace for 300-1200°C (different sintering temperatures are used depending on the decomposition temperature of the above-mentioned salts), sintering in an air atmosphere for 3-12 hours, and then sintering in a hydrogen reducing atmosphere for 3-12 hours to obtain M/AgTO 2 ; To prepare the M x O y /AgTO 2 composite material (M=metal), place the powder in a tube furnace at 300-1200°C (different sintering temperatures are used according to the decomposition temperature of the above-mentioned salts), and sinter in an air atmosphere for 3 -12 hours, M x O y /AgTO 2 is obtained.
对于AgTO2掺杂改性材料,使用上述方法可以制备出M/(AgTO2掺杂改性材料)和MxOy/(AgTO2掺杂改性材料)复合材料。For AgTO 2 doped modified materials, M/(AgTO 2 doped modified materials) and M x O y /(AgTO 2 doped modified materials) composite materials can be prepared using the above method.
实施例3Example 3
AgTO2薄膜的刮刀法(Doctor Blade Method)制备和AgTO2表面涂覆层制备:Preparation of AgTO 2 film by Doctor Blade Method and preparation of AgTO 2 surface coating layer:
在制备AgTO2薄膜时,取少量实施例1制备的AgTO2(T=Al,Ga,In,Cr,Fe,Co,Ni)粉体加入聚乙烯醇及乙酰丙酮各2-4滴,混合制成浆状物,直接用刮刀法(Doctor Blade Method)将浆状物涂覆在基片(20mm×20mm)上,在400℃烧结2-5小时可制作出薄膜,称量基片及有薄膜的基片,可以得到薄膜层的重量,约10mg-30mg。When preparing the AgTO2 thin film, take a small amount of AgTO2 (T=Al, Ga, In, Cr, Fe, Co, Ni) powder prepared in Example 1, add 2-4 drops of polyvinyl alcohol and acetylacetone each, and mix to prepare Make a slurry, directly coat the slurry on the substrate (20mm×20mm) with the doctor blade method, and sinter at 400°C for 2-5 hours to make a film, weigh the substrate and the film The base sheet can obtain the weight of the film layer, about 10mg-30mg.
在制备表面涂覆层时,取100mg的AgTO2(T=Al,Ga,In,Cr,Fe,Co,Ni)粉体,悬浮于100ml水中或有机溶剂中,将该悬浊液分3-5次全部喷溅在建筑材料表面(1m2),每喷溅一次进行30分钟的300-1000℃(根据基底材料不同采用不同温度)退火处理一次,最终可以在建筑材料表面制备出AgTO2表面涂覆层。When preparing the surface coating layer, take 100mg of AgTO 2 (T=Al, Ga, In, Cr, Fe, Co, Ni) powder, suspend in 100ml of water or organic solvent, divide the suspension into 3- Spray on the surface of the building material (1m 2 ) for 5 times, and anneal at 300-1000°C (different temperature according to the base material) for 30 minutes for each splash, and finally the surface of AgTO 2 can be prepared on the surface of the building material coating layer.
实施例4Example 4
利用AgTO2光催化分解亚甲基蓝(MB):Photocatalytic decomposition of methylene blue (MB) using AgTO2 :
利用200mg实施例1制备的AgAlO2,使其在装有约21.0mg/L的MB水溶液100ml(pH值为7左右)的反应器(直径75mm,高35mm)中悬浮,进行MB的光催化分解反应。一边用磁性棒进行搅拌,一边从外部进行光照。光源采用300W的Xe灯,反应器采用耐热玻璃(Corning公司产品)。为了去除热效果,在反应器与Xe灯之间加一冷却装置使反应器冷却。如果在灯和冷却装置之间插入光学滤波片,可以实现只用波长大于滤波片的光进行照射(如使用420nm滤波片,则只有λ≥420nm的光可以通过)。通过紫外-可见吸收光谱测定仪可以检测出由于MB的光分解而产生的浓度变化。Utilize 200mg of AgAlO 2 prepared in Example 1, suspend it in a reactor (75mm in diameter, 35mm in height) filled with about 21.0mg/L of MB aqueous solution 100ml (pH value is about 7), and carry out photocatalytic decomposition of MB reaction. While stirring with a magnetic bar, light was applied from the outside. A 300W Xe lamp was used as the light source, and heat-resistant glass (product of Corning Company) was used as the reactor. To remove thermal effects, a cooling device was placed between the reactor and the Xe lamp to cool the reactor. If an optical filter is inserted between the lamp and the cooling device, only light with a wavelength longer than the filter can be used for irradiation (for example, if a 420nm filter is used, only light with λ≥420nm can pass through). The concentration change due to the photodecomposition of MB can be detected by UV-Vis absorption spectrometer.
结果,在同时有紫外光和可见光的光线照射的情况下,经过120分钟,MB降解了95%。在波长大于420nm的可见光的照射下,经过120分钟,MB降解了86%;还使用商业用TiO2(P25,Degussa,德国),进行了可见光照射下的对比实验,120分钟,MB只能降解了35%。其结果如表1所示。As a result, MB was degraded by 95% after 120 minutes under simultaneous irradiation with ultraviolet light and visible light. Under the irradiation of visible light with a wavelength greater than 420nm, after 120 minutes, MB was degraded by 86%. Commercial TiO 2 (P25, Degussa, Germany) was also used to conduct a comparative experiment under visible light irradiation. After 120 minutes, MB could only degrade up 35%. The results are shown in Table 1.
对于AgTO2(T=Ga,In,Cr,Fe,Co,Ni),使用同样条件分别进行MB的光催化分解反应,光照一定的时间亦能达到与AgAlO2相同的效果。For AgTO 2 (T=Ga, In, Cr, Fe, Co, Ni), use the same conditions to carry out the photocatalytic decomposition reaction of MB respectively, and light for a certain time can also achieve the same effect as AgAlO 2 .
利用实施例2制备的M/AgTO2、MxOy/AgTO2(T=Al,Ga,In,Cr,Fe,Co,Ni;M=金属)进行实验得到更好的效果,催化效率较AgTO2增加,尤其是担载Pt,Ag,Bi2O3的复合材料效率增加明显。M/AgTO 2 , M x O y /AgTO 2 (T=Al, Ga, In, Cr, Fe, Co, Ni; M=metal) prepared in Example 2 were used to conduct experiments to obtain better results, and the catalytic efficiency was higher than The increase of AgTO 2 , especially the efficiency of the composite material loaded with Pt, Ag, Bi 2 O 3 increases significantly.
实施例5Example 5
利用AgTO2薄膜光催化分解亚甲基蓝(MB):Photocatalytic Decomposition of Methylene Blue (MB) Using AgTO 2 Thin Films:
利用实施例3制备的AgAlO2薄膜,将其置于装有5.0mg/L的MB水溶液10ml(pH值为7左右)的反应器(25mm×25mm×20mm)的底部,用有紫外光和可见光的光线照射和波长大于420nm的可见光的光线照射,经过60分钟,效果同实施例4接近。Utilize the AgAlO film prepared in Example 3, place it at the bottom of a reactor (25mm × 25mm × 20mm) containing 10ml of 5.0mg/L MB aqueous solution (pH value is about 7), use ultraviolet light and visible light The light irradiation of light irradiation and the light irradiation of the visible light of wavelength greater than 420nm, after 60 minutes, the effect is close to embodiment 4.
使用AgTO2(T=Ga,In,Cr,Fe,Co,Ni)的薄膜,再按上述实验条件分别进行MB的光催化分解反应,光照一定的时间亦能达到与AgAlO2薄膜相同的效果。Using AgTO 2 (T=Ga, In, Cr, Fe, Co, Ni) film, and then carrying out the photocatalytic decomposition reaction of MB according to the above experimental conditions, the same effect as that of AgAlO 2 film can be achieved by light for a certain time.
实施例6Example 6
利用AgTO2光催化分解茜素红(AR):Photocatalytic Decomposition of Alizarin Red (AR) Using AgTO 2 :
利用300mg实施例1制备的AgAlO2,使其在约16.0mg/L的AR水溶液100ml(pH值为7-8)中悬浮,进行AR的光催化分解反应。条件同上。300 mg of AgAlO 2 prepared in Example 1 was used to suspend it in 100 ml of an AR aqueous solution (pH value of 7-8) of about 16.0 mg/L to carry out the photocatalytic decomposition reaction of AR. Same conditions as above.
结果,在同时有紫外光和可见光的光线照射的情况下,经过120分钟,AR降解了96%;在波长大于420nm的可见光的照射下,经过120分钟,AR降解了70%。其结果如表1所示。As a result, under the irradiation of ultraviolet light and visible light at the same time, 96% of AR was degraded after 120 minutes; under the irradiation of visible light with a wavelength greater than 420nm, 70% of AR was degraded after 120 minutes. The results are shown in Table 1.
对于AgTO2(T=Ga,In,Cr,Fe,Co,Ni),使用同样条件分别进行AR的光催化分解反应,光照一定的时间亦能达到与AgAlO2相同的效果。For AgTO 2 (T=Ga, In, Cr, Fe, Co, Ni), the photocatalytic decomposition reaction of AR is carried out under the same conditions, and the same effect as that of AgAlO 2 can be achieved by light for a certain time.
利用实施例2制备的M/AgTO2、MxOy/AgTO2(X=Al,Ga,In,Cr,Fe,Co,Ni;M=金属)复合材料进行实验得到更好的效果,催化效率较AgTO2增加,尤其是担载Pt,Ag,Bi2O3的复合材料效率增加明显。Using the M/AgTO 2 , M x O y /AgTO 2 (X=Al, Ga, In, Cr, Fe, Co, Ni; M=metal) composite materials prepared in Example 2 to carry out experiments to obtain better results, catalytic The efficiency is higher than that of AgTO 2 , especially the efficiency of composite materials loaded with Pt, Ag, Bi 2 O 3 is significantly increased.
实施例7Example 7
利用AgTO2薄膜光催化分解茜素红(AR):Photocatalytic Decomposition of Alizarin Red (AR) Using AgTO 2 Thin Films:
利用实施例3制备的AgAlO2薄膜,将其置于装有5.0mg/L的AR水溶液10ml(pH值为7左右)的反应器(25mm×25mm×20mm)的底部,用有紫外光和可见光的光线照射和波长大于420nm的可见光的光线照射,经过60分钟,效果同实施例6接近。Utilize the AgAlO2 film prepared in Example 3, place it at the bottom of a reactor (25mm×25mm×20mm) filled with 10ml of 5.0mg/L AR aqueous solution (pH value is about 7), use ultraviolet light and visible light The light irradiation and the light irradiation of the visible light of wavelength greater than 420nm, after 60 minutes, the effect is close to that of embodiment 6.
对于AgTO2(T=Ga,In,Cr,Fe,Co,Ni)的薄膜,再按上述实验条件分别进行AR的光催化分解反应,光照一定的时间亦能达到与AgAlO2薄膜相同的效果。For the thin film of AgTO 2 (T=Ga, In, Cr, Fe, Co, Ni), the photocatalytic decomposition reaction of AR is carried out according to the above experimental conditions, and the same effect as that of the AgAlO 2 thin film can be achieved by light for a certain time.
实施例8Example 8
利用AgTO2进行光催化降解乙醛污染气体:Photocatalytic degradation of acetaldehyde pollution gas using AgTO2 :
将300mg实施例1制备的AgAlO2置于24mm×24mm的载玻片上,然后将载玻片放入带气体循环泵的密闭系统(体积232cc)中,向其中注入一定量的乙醛溶液(40%),形成空气中含浓度为1270ppm的乙醛气体的重度污染空气,用不加滤波片的Xe灯进行照射,并用气体循环泵循环气体。生成的CO2和残留的污染物的浓度用气相色谱仪(GC)检测。300mg of AgAlO prepared in Example 1 was placed on a glass slide of 24mm × 24mm, then the slide glass was put into a closed system (232cc in volume) with a gas circulation pump, and a certain amount of acetaldehyde solution (40 cc) was injected thereinto. %) to form heavily polluted air containing acetaldehyde gas with a concentration of 1270ppm in the air, irradiate with an Xe lamp without a filter, and circulate the gas with a gas circulation pump. The concentrations of generated CO 2 and residual pollutants were detected by gas chromatography (GC).
结果在同时有紫外光和可见光的光线照射的情况下,经过360分钟,1270ppm的乙醛完全降解,840分钟矿化率达到90%。Results Under the condition of irradiation with ultraviolet light and visible light at the same time, after 360 minutes, 1270ppm of acetaldehyde was completely degraded, and the mineralization rate reached 90% in 840 minutes.
矿化是指有机物变为CO2和水等无害物质,矿化率是由实际产生的CO2除以理论上有机物完全分解应产生的CO2而得,通常由于粉末材料有对气体有吸附,所以不可能达到100%。Mineralization refers to the transformation of organic matter into harmless substances such as CO 2 and water. The mineralization rate is obtained by dividing the actual CO 2 produced by the theoretical CO 2 that should be generated by the complete decomposition of organic matter. Usually, the powder material has adsorption on gas , so it is impossible to reach 100%.
对于AgTO2(T=Ga,In,Cr,Fe,Co,Ni),使用同样条件分别进行乙醛的光催化分解反应,光照一定的时间亦能达到与AgAlO2相同的效果。For AgTO 2 (T=Ga, In, Cr, Fe, Co, Ni), the photocatalytic decomposition reaction of acetaldehyde is carried out under the same conditions, and the same effect as that of AgAlO 2 can be achieved by light for a certain time.
利用实施例2制备的M/AgTO2、MxOy/AgTO2(T=Al,Ga,In,Cr,Fe,Co,Ni;M=金属)复合材料进行实验能得到更好的效果,催化效率较AgTO2增加,尤其是担载Pt,Ag,Bi2O3的复合材料效率增加明显。Experiments using the M/AgTO 2 , M x O y /AgTO 2 (T=Al, Ga, In, Cr, Fe, Co, Ni; M=metal) composite materials prepared in Example 2 can obtain better results, The catalytic efficiency is higher than that of AgTO 2 , especially the efficiency of composite materials loaded with Pt, Ag, Bi 2 O 3 is significantly increased.
根据上述结果,本发明的AgTO2型复合氧化物新型光催化材料的应用范围很广。用途如:涂料、油漆添加剂,或者加入不同的分散剂和溶剂内,涂覆或印刷在不同的材料表面上制备成各种薄膜或表面层,如玻璃、钢板、塑料、橡胶、纸张、木材、铝板、陶瓷、陶器、布料,以及建筑物的外表面和内表面,比二氧化钛的效果好。可以进行包括紫外光及可见光照射下,分解、去除有害化学物质。处理高浓度的有机化学废水:如上述实施例,添加量的需处理水量的0.1%-0.3%(质量分数),经光照(紫外光更好)即可以COD去除率达到90%以上;处理高浓度的有机化学废气:如上述实施例,使用量为1.3mg/cc,经光照(紫外光更好),分解率100%,矿化率90%以上。薄膜材料能在原料消耗少的情况下能实现同样效果,复合材料M/AgTO2、MxOy/AgTO2(T=Al,Ga,In,Cr,Fe,Co,Ni;M=金属)比单一的AgTO2性能更好。参见表1.According to the above results, the AgTO 2 type composite oxide novel photocatalytic material of the present invention has a wide range of applications. Uses such as: coatings, paint additives, or added to different dispersants and solvents, coated or printed on the surface of different materials to prepare various films or surface layers, such as glass, steel plate, plastic, rubber, paper, wood, Aluminum panels, ceramics, earthenware, fabrics, and exterior and interior surfaces of buildings, work better than titanium dioxide. It can decompose and remove harmful chemical substances under the irradiation of ultraviolet light and visible light. Treatment of high-concentration organic chemical wastewater: as in the above-mentioned embodiment, the added amount is 0.1%-0.3% (mass fraction) of the amount of water to be treated, and the COD removal rate can reach more than 90% through light (ultraviolet light is better); the treatment is high Concentration of organic chemical waste gas: as in the above examples, the usage amount is 1.3mg/cc, after light (ultraviolet light is better), the decomposition rate is 100%, and the mineralization rate is more than 90%. Thin film materials can achieve the same effect with less raw material consumption, composite materials M/AgTO 2 , M x O y /AgTO 2 (T=Al, Ga, In, Cr, Fe, Co, Ni; M=metal) Better than single AgTO 2 performance. See Table 1.
表1AgAlO2光催化降解有机污染物的结果Table 1 AgAlO photocatalytic degradation results of organic pollutants
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