CN1321742C - Visible light response photocatalyst and application thereof - Google Patents
Visible light response photocatalyst and application thereof Download PDFInfo
- Publication number
- CN1321742C CN1321742C CNB2003101062806A CN200310106280A CN1321742C CN 1321742 C CN1321742 C CN 1321742C CN B2003101062806 A CNB2003101062806 A CN B2003101062806A CN 200310106280 A CN200310106280 A CN 200310106280A CN 1321742 C CN1321742 C CN 1321742C
- Authority
- CN
- China
- Prior art keywords
- visible light
- photocatalyst
- catalyst
- light
- photocatalysts
- 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
Links
Landscapes
- Catalysts (AREA)
Abstract
Description
一、技术领域:1. Technical field:
本发明涉及紫外和可见光响应的光催化剂及其应用,尤其是涉及可以高效地吸收太阳光中的紫外线以及可见光的铟系复合氧化物半导体所组成的高活性的光催化剂,以及利用它分解有害化学物质和制造氢的应用。The invention relates to photocatalysts responsive to ultraviolet and visible light and their applications, in particular to highly active photocatalysts composed of indium compound oxide semiconductors that can efficiently absorb ultraviolet and visible light in sunlight, and to use it to decompose harmful chemicals Matter and applications for making hydrogen.
二、技术背景2. Technical Background
目前,因化石资源的制约以及它的大量消费引起的深刻的环境和能源问题,如地球变暖、环境恶化等等,直接影响了人类的生存和生活质量的改善,人类迫切需要开发绿色、安全的新能源。作为新能源的来源,核能发电虽然已投入使用,但却出现了安全性和废物处理等方面的问题。At present, due to the constraints of fossil resources and the profound environmental and energy problems caused by their massive consumption, such as global warming and environmental degradation, etc., which directly affect the survival of human beings and the improvement of quality of life, human beings urgently need to develop green, safe and of new energy. As a source of new energy, although nuclear power generation has been put into use, there have been problems in safety and waste disposal.
解决问题的途径之一是利用太阳能。在一年间,到达地球表面的太阳能是巨大的,它相当于人类年消耗能量的10,000倍之多。从事可见光半导体光催化剂研究的目的之一是模拟植物的光合作用,发展人工光合成技术,从而利用取之不竭的太阳光和水,直接制造作为绿色燃料的氢和氧。水的分解反应如(1)所示,是能量蓄积型的反应,考虑到光是产生氧的必要的明反应条件,光合成的反应与之相同,也是这样的分解反应:One of the ways to solve the problem is to use solar energy. In one year, the amount of solar energy reaching the earth's surface is enormous, which is equivalent to 10,000 times the annual energy consumption of human beings. One of the purposes of research on visible light semiconductor photocatalysts is to simulate the photosynthesis of plants and develop artificial photosynthesis technology, so as to use the inexhaustible sunlight and water to directly produce hydrogen and oxygen as green fuels. The decomposition reaction of water, as shown in (1), is an energy accumulation type reaction. Considering that light is a necessary light reaction condition for oxygen generation, the photosynthetic reaction is the same as it, and it is also such a decomposition reaction:
H2O=H2+1/2O2 式(1)H 2 O=H 2 +1/2O 2 formula (1)
光催化剂在吸收了高于其带隙能量的光子后,生成了空穴和电子。这些空穴和电子分别进行氧化反应和还原反应,产生氧和氢。考虑到光催化剂的实用性,利用太阳光作为光源是不可缺少的。照射向地表的太阳光中波长在500nm附近可见光的强度最大,波长为400nm-750nm的可见光区的能量大约是太阳光总能量的43%。另一方面,在波长为440nm以下的紫外线则不足5%。所以,为了高效地利用太阳光谱,人们希望寻找在可见光下具有催化剂活性的光催化剂。Photocatalysts generate holes and electrons after absorbing photons with energies above their bandgap. These holes and electrons undergo oxidation and reduction reactions, respectively, to produce oxygen and hydrogen. Considering the practicability of photocatalysts, utilizing sunlight as a light source is indispensable. Among the sunlight irradiated to the surface, the intensity of visible light with a wavelength near 500nm is the highest, and the energy in the visible light region with a wavelength of 400nm-750nm is about 43% of the total energy of sunlight. On the other hand, ultraviolet rays with a wavelength of 440 nm or less are less than 5%. Therefore, in order to efficiently utilize the solar spectrum, people hope to find photocatalysts with catalytic activity under visible light.
但是,以往的半导体光催化剂虽然在具有高能量的紫外线照射下可以产生氢和氧,但利用可见光响应的半导体光催化剂实现制造氢的例子非常有限,而且活性也很低。而充分利用可见光是高效利用太阳光的基本前提。However, although conventional semiconductor photocatalysts can generate hydrogen and oxygen under high-energy ultraviolet irradiation, there are very limited examples of hydrogen production using visible light-responsive semiconductor photocatalysts, and their activity is also low. Making full use of visible light is the basic premise for efficient use of sunlight.
近几年,应用光催化剂分解有害化学物质的研究已经引起了人们的重视。虽然已经出现了利用二氧化钛对水中和大气中的农药和恶臭物质等有机物进行分解和涂在固体表面进行自清洁等应用,但是二氧化钛几乎不能利用可见光。如果有可资利用的可见光光催化剂,那么可以大大提高上述应用的效率。氧化物半导体中价带的空穴具有非常强的氧化能力,可以氧化水及大多数有机物等电子给体,从而释放氧。而导带电子具有还原能力,可以将水还原生成氢。也就是说,导带能级比氧的氧化电位高,而价带能级比氢的还原电位低是实现水分解的必不可少的条件。能分解水产生氢和氧的光催化剂具有强的氧化和还原能力,因此可以期待在上述领域中得到应用。In recent years, research on the application of photocatalysts to decompose harmful chemicals has attracted attention. Although titanium dioxide has been used to decompose organic substances such as pesticides and odorous substances in water and the atmosphere, and to apply it on solid surfaces for self-cleaning, titanium dioxide can hardly use visible light. If visible-light photocatalysts are available, the efficiency of the above applications can be greatly improved. The holes in the valence band in oxide semiconductors have a very strong oxidation ability, which can oxidize electron donors such as water and most organic substances, thereby releasing oxygen. The conduction band electrons have the ability to reduce water to generate hydrogen. That is to say, the conduction band energy level is higher than the oxidation potential of oxygen, and the valence band energy level is lower than the reduction potential of hydrogen, which is an indispensable condition for water splitting. Photocatalysts capable of splitting water to generate hydrogen and oxygen have strong oxidizing and reducing abilities, and thus can be expected to be used in the above-mentioned fields.
三、发明内容3. Contents of the invention
本发明的目的是:提供高效吸收太阳光中紫外线和可见光的铟系复合氧化物半导体所构成的高活性的光催化剂以及利用它分解有害化学物质和制造氢的方法。The object of the present invention is to provide a highly active photocatalyst composed of an indium-based composite oxide semiconductor that efficiently absorbs ultraviolet and visible light in sunlight, and a method for decomposing harmful chemical substances and producing hydrogen using it.
本发明的目的是这样实现的:The purpose of the present invention is achieved like this:
1.可见光响应的光催化剂,由铟和A元素,以及2价过渡金属元素M形成的复合氧化半导体:In1-xMXAO4,A元素为Nb,Ta,V中选择的至少一种,所述的2价过渡金属元素M是从Cr,Mn,Fe,Co,Ni,Cu,Zn元素中选择至少一种,0<x<1,这些复合氧化物半导体作为光催化剂。1. A photocatalyst responsive to visible light, a compound oxide semiconductor formed by indium and A elements, and a divalent transition metal element M: In 1-x M X AO 4 , A element is at least one selected from Nb, Ta, V , the divalent transition metal element M is at least one selected from Cr, Mn, Fe, Co, Ni, Cu, Zn elements, 0<x<1, and these composite oxide semiconductors are used as photocatalysts.
2.由铟和元素周期表中A元素构成的氧化物半导体InAO4所表示的氧化物半导体和其中一部分铟被置换为过渡金属M后的化学式In1-xMXAO4所表示的具有wolfranite型晶体结构的复合氧化物半导体,就是请求项1所记录的光催化剂。2. An oxide semiconductor composed of indium and element A in the periodic table represented by InAO 4 and an oxide semiconductor represented by the chemical formula In 1-x M X AO 4 after a part of the indium is substituted with a transition metal M has wolfranite A compound oxide semiconductor with crystal structure of type is the photocatalyst recorded in claim 1.
3.作为可见光响应的氧化物半导体是上述1-3中记录的光催化剂。3. The oxide semiconductor that responds as visible light is the photocatalyst recorded in 1-3 above.
4.采用化学式In1-xNixTaO4或In1-xNixNbO4所表示的复合氧化物半导体,作为上述1-4记录的光催化剂。4. Use the composite oxide semiconductor represented by the chemical formula In 1-x Ni x TaO 4 or In 1-x Ni x NbO 4 as the photocatalyst recorded in 1-4 above.
5.上述1-5中记录的助催化剂的光催化剂。5. A photocatalyst of the co-catalyst described in 1-5 above.
6.用上述1-6中的光催化剂被含有紫外线和可见光的光线照射分解有害化学物质的方法。6. A method for decomposing harmful chemical substances by irradiating the photocatalyst in the above 1-6 with light rays containing ultraviolet rays and visible light.
7.用上述1-6中的光催化剂被含有紫外线和可见光的光线照射来制造氢的方法。7. A method of producing hydrogen by irradiating the photocatalyst in the above 1-6 with light rays including ultraviolet rays and visible light.
8.用上述1-6中的光催化剂被含有紫外线或者可见光的光线照射完全分解水为氢和氧来制造氢的方法。8. A method for producing hydrogen by completely decomposing water into hydrogen and oxygen by using the photocatalyst in the above 1-6 by irradiation with light containing ultraviolet light or visible light.
在本发明中,所使用的光催化剂是表达式为In1-xMXAO4的氧化物,其中M为2价的金属元素,是从Cr,Mn,Fe,Co,Ni,Cu,Zn等元素中选择的,A为5价的元素,从V、Nb、Ta等元素中选择,化学式中的氧形式上用4个原子,实际上得到的结果由于存在氧空位等缺陷而少于4个。可以认为如果2价的M变得多了,氧的数量就会变得少于4。X是比0大比1小的数字。基本分子式表示为一般式B3-A5-O4,具有wolfranite晶体结构,化合物中x在保持其晶体结构稳定的范围内就可以了。本发明的复合氧化物半导体可以通过一般的固相反应法合成,即按照化学计量比混合各具有各金属成分的氧化物,在空气常压下煅烧而成。对于容易升华的原料,在份量上需要略微多加一点。此外,也可以使用金属醇盐或金属盐为原料的各种溶胶凝胶(sol-gel)法、柠檬酸络合法等多种方法。In the present invention, the photocatalyst used is an oxide with the expression In 1-x M X AO 4 , wherein M is a 2-valent metal element, which is obtained from Cr, Mn, Fe, Co, Ni, Cu, Zn Among other elements, A is a 5-valent element, and it is selected from V, Nb, Ta and other elements. The oxygen in the chemical formula uses 4 atoms in form, and the result actually obtained is less than 4 due to the existence of defects such as oxygen vacancies. indivual. It can be considered that if the number of divalent M increases, the number of oxygen will become less than four. X is a number that is greater than 0 and less than 1. The basic molecular formula is expressed as the general formula B 3- A 5- O 4 , which has a wolfranite crystal structure, and x in the compound only needs to be within the stable range of the crystal structure. The composite oxide semiconductor of the present invention can be synthesized by a general solid-state reaction method, that is, by mixing oxides each having each metal component according to a stoichiometric ratio, and calcining it under normal air pressure. For ingredients that sublime easily, a little more is needed in the serving size. In addition, various methods such as various sol-gel methods and citric acid complex methods using metal alkoxides or metal salts as raw materials can also be used.
为了更加有效地利用光,希望本发明中的光催化剂的形状为微粒子,以获得较大的表面积。In order to utilize light more effectively, it is desirable that the shape of the photocatalyst in the present invention is a fine particle to obtain a larger surface area.
用固相反应法制备的氧化物,其粒子较大而表面积较小,但是可以通过球磨机等粉碎手段使粒子直径变小。一般的粒子大小约为10μm-200μm,最好是50μm以下。此外,还可以将微粒子压制成板状来使用。固相反应的方法可以参见本申请人的相关发明92107282、98111231发明人:忻新泉等。The oxide prepared by the solid state reaction method has larger particles and a smaller surface area, but the particle diameter can be reduced by pulverizing means such as a ball mill. The general particle size is about 10 μm-200 μm, preferably less than 50 μm. In addition, fine particles may be pressed into a plate shape and used. For the method of solid phase reaction, please refer to related inventions 92107282 and 98111231 of the applicant. Inventor: Xin Xinquan et al.
可以在本发明的半导体表面修饰常用的助催化剂,如Pt、Pd等贵金属、Ni、Co等过渡金属、NiO及IrO2、NiOx、RuO2等氧化物,作为具有微结构的光催化剂。制备方法可以是浸渍法或电沉积法等。浸渍法就是将半导体氧化物放入该氧化物活性种的氯化物、硝酸盐等化合物的水溶液中浸渍,然后在100-200℃下干燥约2-5小时,在800℃以下(最好是200-500℃之间),在还原性气体及/或氧化气体下煅烧2-5小时。助催化剂用量为0.01-10wt%、最好是0.1-5wt%。Common co-catalysts such as noble metals such as Pt and Pd, transition metals such as Ni and Co, oxides such as NiO and IrO2, NiOx and RuO2 can be modified on the surface of the semiconductor of the present invention as a photocatalyst with a microstructure. The preparation method can be impregnation method or electrodeposition method and the like. The impregnation method is to immerse the semiconductor oxide in an aqueous solution of compounds such as chlorides and nitrates of the active species of the oxide, and then dry it at 100-200°C for about 2-5 hours. -500°C), calcined in reducing gas and/or oxidizing gas for 2-5 hours. The amount of co-catalyst used is 0.01-10wt%, preferably 0.1-5wt%.
此外,进行水的完全分解反应所使用的反应溶液并不仅限于纯水。一般来说,在通常溶解有碳酸盐或碳酸氢盐、碘盐和溴盐的盐水中也可以使水的分解反应发生。In addition, the reaction solution used for the complete decomposition reaction of water is not limited to pure water. In general, water splitting reactions can also be made to occur in brines where carbonates or bicarbonates, iodine salts, and bromide salts are usually dissolved.
在上述水溶液中添加本发明的光催化剂。催化剂的添加量基本上应该是保证入射的光可以被高效吸收的量。对照射面积为25cm2的情况,添加的光催化剂的量为0.05-10g,最好是0.2-3g。像这样通过对添加了光分解用催化剂的水溶液进行光照射,可使水分解并产生氧。例如,可以向纯水中添加本发明的光催化剂,通过照射可见光使水分解,同时生成化学计量比为2∶1的氧和氢。用于照射水的光的光谱必须含有可以被半导体吸收的波长。在本发明中也可以照射太阳光。The photocatalyst of this invention is added to the said aqueous solution. The amount of catalyst added should basically be the amount that ensures that the incident light can be efficiently absorbed. When the irradiation area is 25cm 2 , the amount of photocatalyst added is 0.05-10g, preferably 0.2-3g. By irradiating the aqueous solution to which the photodecomposition catalyst is added in this way, water can be decomposed and oxygen can be generated. For example, the photocatalyst of the present invention can be added to pure water, and the water can be decomposed by irradiating visible light to generate oxygen and hydrogen in a stoichiometric ratio of 2:1. The spectrum of light used to illuminate the water must contain wavelengths that can be absorbed by the semiconductor. In the present invention, sunlight may also be irradiated.
具体反应的方式可以是将催化剂悬浊于包含有机物的水溶液中进行光照射,也可以是把催化剂固定在底座上,液体在其表面慢慢流动,也可以在气化室床中分解恶臭物质的气相反应。The specific reaction method can be to suspend the catalyst in an aqueous solution containing organic matter for light irradiation, or to fix the catalyst on the base, and the liquid flows slowly on its surface, or to decompose the malodorous substance in the gasification chamber bed. gas phase reaction.
本发明的光催化剂不仅可以用于水的完全分解,还可以应用于多种光催化反应。例如,分解复杂的有机物分子时,酒精或农药、染料、中间体、恶臭等污染物质的分子一般起到电子给体的作用,它们被空穴氧化而被分解,与此同时,或者被电子还原产生氢,或者氧被电子还原。具体反应的装置可以是将催化剂悬浊于包含有机物的水溶液中进行光照射,也可以是把催化剂固定在底座上,也可以是分解恶臭物质时的气相反应。The photocatalyst of the present invention can not only be used for the complete decomposition of water, but also can be applied to various photocatalytic reactions. For example, when decomposing complex organic molecules, molecules of pollutants such as alcohol or pesticides, dyes, intermediates, and odors generally act as electron donors, and they are oxidized by holes to be decomposed, and at the same time, or reduced by electrons Hydrogen is produced, or oxygen is reduced by electrons. The device for the specific reaction can be that the catalyst is suspended in an aqueous solution containing organic matter for light irradiation, or that the catalyst can be fixed on a base, or it can be a gas phase reaction when decomposing malodorous substances.
发明的效果还包括:关于直接利用太阳能使水完全分解的光催化剂,目前使用的光催化剂只在紫外线下有活性,而不能有效利用占太阳能中占绝大部分的可见光。通过本发明则可以利用可见光将水分解成氢和氧。未来就有可能在人工池里铺满光催化剂,通过无尽的太阳能高效率地大量制造氢气,这为解决能源问题提供了一条有希望的途径。The effect of the invention also includes: Regarding the photocatalyst that directly utilizes solar energy to completely decompose water, currently used photocatalysts are only active under ultraviolet rays, and cannot effectively utilize visible light that accounts for the vast majority of solar energy. Visible light can be used to split water into hydrogen and oxygen through the present invention. In the future, it may be possible to cover artificial pools with photocatalysts to efficiently mass-produce hydrogen from endless solar energy, which provides a promising way to solve energy problems.
四、具体实施方式4. Specific implementation
实施例1Example 1
在本发明的化学式In1-xMxAO4中,使用铟、元素M和A来合成In1-xMxAO4。根据化学计量比,通过固相法合成各种成分的氧化物。本催化剂是利用化学计量比调节(1-x)mol In2O3x=(0-1),x mol NiO(x=0-1)及1 mol Ta2O5(表1)的。例如,x=0.2时,In0.8Ni0.2TaO4分别是称量In2O83.201g、NiO 0.431g、Ta2O56.368g。把这些原料放入矾土坩埚中,在空气中常压下在电炉中经过900℃、24小时的预烧结后,再重复进行3次1200℃、50小时的煅烧。煅烧结束后,把此煅烧物在碾钵中研磨成10μm以下的大小粉末。使用XRD和SEM-EDS研究光反应前后催化剂的化学组成和晶体结构。通过Rietveld解析,此类氧化物具有单斜晶体结构、空间群为P2/C,晶体构型是层状Wolframite结构。具有Wolframite型晶体结构的半导体,其电子比较容易移动。通过紫外光吸收谱测定,可以得到其能隙在2.5Ev以下,因此具有可见光的响应性。In the chemical formula In 1-x M x AO 4 of the present invention, In 1-x M x AO 4 is synthesized using indium, elements M and A. Depending on the stoichiometric ratio, oxides of various compositions were synthesized by a solid-state method. The catalyst is adjusted by stoichiometric ratio (1-x) mol In 2 O 3 x=(0-1), x mol NiO (x=0-1) and 1 mol Ta 2 O 5 (Table 1). For example, when x=0.2, In 0.8 Ni 0.2 TaO 4 weighs 3.201 g of In 2 O 8 , 0.431 g of NiO, and 6.368 g of Ta 2 O 5 . Put these raw materials into an alumina crucible, and after pre-sintering in an electric furnace at 900°C for 24 hours in air under normal pressure, repeat 3 times of calcination at 1200°C for 50 hours. After the calcination, the calcined product is ground into a powder with a size of 10 μm or less in a mortar. The chemical composition and crystal structure of the catalyst before and after the photoreaction were investigated using XRD and SEM-EDS. According to Rietveld's analysis, this kind of oxide has a monoclinic crystal structure, the space group is P2/C, and the crystal configuration is a layered Wolframite structure. Semiconductors with a Wolframite-type crystal structure allow electrons to move relatively easily. Through the measurement of ultraviolet light absorption spectrum, it can be obtained that its energy gap is below 2.5Ev, so it has the responsiveness of visible light.
上述氧化物半导体中掺入1.0wt%NiOx助催化剂的方法是通过Ni(NO3)2水溶液的浸渍、200℃下5小时干燥、500℃下氢还原、再在200℃下氧化来实现的。The method of doping 1.0wt% NiOx co-catalyst into the above oxide semiconductor is achieved by impregnating Ni(NO 3 ) 2 aqueous solution, drying at 200°C for 5 hours, hydrogen reduction at 500°C, and oxidation at 200°C.
把0.5g的NiOx/In1-xNixTaO4悬浊于纯水250ml中,使其发生水的光分解反应。使用封闭循环类催化反应装置,一边进行磁搅拌,一边从外部照射可见光。光源使用300W的氙灯,反应槽使用硼硅酸玻璃制成的器皿。使光通过斩波滤波器(波长>420nm)得到长波长的光,然后照射光催化剂。用气体色谱法进行所产生的氢和氧的检测与定量。Suspend 0.5 g of NiOx/In 1-x Ni x TaO 4 in 250 ml of pure water to cause a photolysis reaction of water. Visible light is irradiated from the outside while performing magnetic stirring using a closed-cycle catalytic reaction device. A 300W xenon lamp was used as a light source, and a container made of borosilicate glass was used as a reaction tank. Light of a long wavelength is obtained by passing the light through a chopper filter (wavelength>420 nm), and then irradiates the photocatalyst. Detection and quantification of generated hydrogen and oxygen were performed by gas chromatography.
实验结果表明:氢和氧的化学计量比为2∶1,从而证明:依靠可见光实现了水的完全分解。氢及其发生的速度如表1所示。这与把In的一部分替换为Ni时的性能大为不同。在此类半导体中,x=0.1时活性最大。The experimental results show that the stoichiometric ratio of hydrogen and oxygen is 2:1, which proves that the complete decomposition of water is realized by relying on visible light. Hydrogen and the rate at which it occurs are shown in Table 1. This is very different from the performance when a part of In is replaced by Ni. In such semiconductors, the activity is maximum at x=0.1.
In1-xMxAO4中,类同上述实施例,分别从用IrO2、CoO、NiOx、RuO2、CuO、ZnO等氧化物取代NiO,能得到类似的复合氧化物,效果亦类似。In In 1-x M x AO 4 , similar to the above examples, by replacing NiO with oxides such as IrO 2 , CoO, NiO x , RuO 2 , CuO, and ZnO, similar composite oxides can be obtained with similar effects. .
同理,V2O5、Nb2O5取代Ta2O5,类同上述实施例,能得到类似的复合氧化物,效果亦类似。Similarly, replacing Ta 2 O 5 with V 2 O 5 and Nb 2 O 5 , similar to the above-mentioned embodiment, a similar composite oxide can be obtained, and the effect is also similar.
实施例2Example 2
用RuO2代替实施例1中的NiOx作为助催化剂。In1-xNixTaO4半导体掺入1.0wt%RuO2的方法是通过RuCl4水溶液的浸渍、200℃下5小时干燥、500℃下氧化气体下2小时煅烧来实现的。其结果如表1所示。此时也可得知:在可见光下水完全分解。IrO2的实施例同上。 RuO2 was used instead of NiOx in Example 1 as a cocatalyst. In1 - xNixTaO4 semiconductors doped with 1.0wt% RuO2 were achieved by impregnation with RuCl4 aqueous solution, drying at 200 °C for 5 h, and calcination at 500 °C under oxidizing gas for 2 h. The results are shown in Table 1. Also at this time, it can be seen that water is completely decomposed under visible light. The embodiment of IrO2 is the same as above.
电沉积法即电解工艺将Pt贵金属、Co过渡金属沉积在In1-xNixTaO4半导体上,得到作为具有微结构的光催化剂。其结果同表1相近。也可以使用Pt碳聚集在In1-xNixTaO4等类似的半导体上。The electrodeposition method, that is, the electrolysis process, deposits Pt noble metals and Co transition metals on the In 1-x Ni x TaO 4 semiconductor to obtain a photocatalyst with a microstructure. The results are similar to Table 1. It is also possible to use Pt carbon aggregated on In 1-x Ni x TaO 4 and similar semiconductors.
实施例3Example 3
为了确认有机物的分解在可见光下可以比较高效地进行,在水溶液中进行甲醇的分解。使用Pt(0.1wt%)作为In0.9Ni0.1TaO4的助催化剂。将0.5g的光催化剂放入240ml纯水和10ml甲醇的混合液中悬浊、使其发生光分解反应。使用封闭循环类催化反应装置,一边进行磁搅拌,一边从外部照射可见光。光源使用300W的氙灯,反应槽使用硼硅酸玻璃制成的器皿。来自光源的光,光通过斩波滤波器(波长>420nm)得到长波长的光,然后照射试料(光催化剂)。用气相色谱法进行所产生的氢和氧的检测与定量。实验结果表明,氢以146μmol/h的速度稳定产生,不产生氧。这表明在可见光的照射下,发生了如下反应:空穴将甲醇氧化分解,电子还原水产生了氢。In order to confirm that the decomposition of organic matter can be carried out relatively efficiently under visible light, the decomposition of methanol was carried out in an aqueous solution. Pt (0.1 wt%) was used as a co-catalyst for In 0.9 Ni 0.1 TaO 4 . 0.5 g of the photocatalyst was suspended in a mixed solution of 240 ml of pure water and 10 ml of methanol to cause a photolysis reaction. Visible light is irradiated from the outside while performing magnetic stirring using a closed-cycle catalytic reaction device. A 300W xenon lamp was used as a light source, and a container made of borosilicate glass was used as a reaction tank. The light from the light source passes through a chopper filter (wavelength>420nm) to obtain long-wavelength light, and then irradiates the sample (photocatalyst). Detection and quantification of generated hydrogen and oxygen were performed by gas chromatography. The experimental results showed that hydrogen was produced stably at a rate of 146 μmol/h, and no oxygen was produced. This indicates that under the irradiation of visible light, the following reactions occurred: the holes oxidatively decomposed methanol, and the electrons reduced water to generate hydrogen.
对有机物污染物质的分解:用于去除废水中酚、酸、酮、醛等复杂化学物质,可以参见用二氧化钛方法处理方法:东南大学CN01238388“治理废水废气的光催化反应器。Decomposition of organic pollutants: It is used to remove complex chemical substances such as phenols, acids, ketones, and aldehydes in wastewater. You can refer to the treatment method with titanium dioxide: Southeast University CN01238388 "Photocatalytic Reactor for Treating Wastewater and Waste Gas.
本实施例用于对含酚废水(对苯二甲酸的生产废水)的处理,用上述条件,0.5g的光催化剂放入250ml废水,氙灯直接照射2小时,COD去除率达到80%以上。This embodiment is used for the treatment of phenol-containing wastewater (production wastewater of terephthalic acid). With the above conditions, 0.5g of photocatalyst is put into 250ml of wastewater, and the xenon lamp is directly irradiated for 2 hours, and the COD removal rate reaches more than 80%.
本实施例用于对古龙酸废水的处理:0.5g的光催化剂放入250ml废水氙灯直接照射2小时,肉眼观察脱色效果明显。This embodiment is used for the treatment of gulonic acid wastewater: put 0.5g of photocatalyst into 250ml of wastewater and directly irradiate it with a xenon lamp for 2 hours, and the decolorization effect is obvious by visual observation.
实施例4Example 4
在实施例3中,使用Pt(1wt%)作为In0.8Cu0.2TaO4的助催化剂,Pt(1wt%)作为In0.8Fe0.2TaO4的助催化剂。把0.5g的光催化剂放入240ml纯水和10ml甲醇的混合液中悬浊、使其发生水的光分解反应。使用封闭循环类催化反应装置,一边进行磁搅拌,一边从外部照射可见光。光源使用400W的高压水银灯,反应槽使用硼硅酸玻璃制成的器皿,照射可见光和紫外线。用气相色谱法进行产生的氢和氧的检测与定量。实验结果表明,氢以100μmol/h及80μmol/h的速度稳定产生,不产生氧。这表明发生了如下反应:空穴将甲醇氧化分解,电子还原水产生了氢。In Example 3, Pt (1 wt %) was used as a co-catalyst for In 0.8 Cu 0.2 TaO 4 , and Pt (1 wt %) was used as a co-catalyst for In 0.8 Fe 0.2 TaO 4 . Put 0.5g of photocatalyst into the mixed solution of 240ml of pure water and 10ml of methanol and suspend it to cause the photolysis reaction of water. Visible light is irradiated from the outside while performing magnetic stirring using a closed-cycle catalytic reaction device. A 400W high-pressure mercury lamp was used as a light source, and a container made of borosilicate glass was used as a reaction tank to irradiate visible light and ultraviolet rays. Detection and quantification of generated hydrogen and oxygen were performed by gas chromatography. The experimental results show that hydrogen is stably produced at a rate of 100 μmol/h and 80 μmol/h, and no oxygen is produced. This indicates that the following reactions occurred: the holes oxidatively decompose methanol, and the electrons reduce water to produce hydrogen.
比较例1Comparative example 1
在实施例1中,对未置换Ni的NiOx/InTaO4及RuO2/InTaO4的活性进行评价,但其比NiOx/Inl-xNixTaO4及RuO2/In1-xNixTaO4的实施例1的活性要低。In Example 1, the activity of NiOx/InTaO 4 and RuO2/InTaO 4 which did not replace Ni was evaluated, but the activity of NiOx/In lx Ni x TaO 4 and RuO2/In 1-x Ni x TaO 4 was evaluated. 1 is less active.
比较例2Comparative example 2
在代表性的光催化剂Pt-TiO2中,仅在可见光照射下,没有任何反应。In the representative photocatalyst Pt-TiO2, there is no reaction only under visible light irradiation.
表1:光催化剂活性Table 1: Photocatalyst activity
Claims (9)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2003101062806A CN1321742C (en) | 2003-11-13 | 2003-11-13 | Visible light response photocatalyst and application thereof |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2003101062806A CN1321742C (en) | 2003-11-13 | 2003-11-13 | Visible light response photocatalyst and application thereof |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN1544144A CN1544144A (en) | 2004-11-10 |
| CN1321742C true CN1321742C (en) | 2007-06-20 |
Family
ID=34334065
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CNB2003101062806A Expired - Fee Related CN1321742C (en) | 2003-11-13 | 2003-11-13 | Visible light response photocatalyst and application thereof |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN1321742C (en) |
Families Citing this family (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN100423293C (en) * | 2006-04-30 | 2008-10-01 | 南京大学 | Preparation method of solar cell |
| CN102872853A (en) * | 2012-09-26 | 2013-01-16 | 北京工业大学 | A three-dimensional ordered macroporous InVO4 visible light-responsive photocatalyst, preparation and application |
| CN104209135B (en) * | 2013-05-31 | 2017-03-15 | 天津大学 | A kind of high-efficiency visible light stimulates water splitting to produce hydrogen and oxygen catalyst and its preparation method |
| CN104307527A (en) * | 2014-10-24 | 2015-01-28 | 桂林理工大学 | Visible light responsive photocatalyst InFeZn5O8 and its preparation method |
| CN104841440B (en) * | 2015-05-07 | 2017-12-12 | 北京化工大学 | A kind of heterojunction type tri compound semiconductor light-catalyst and preparation method thereof |
| CN107376960A (en) * | 2017-07-11 | 2017-11-24 | 柳州若思纳米材料科技有限公司 | A kind of preparation method of nickel doping phosphoric acid indium photochemical catalyst |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1422694A (en) * | 2001-12-06 | 2003-06-11 | 中国科学院大连化学物理研究所 | Catalyst for reduction of nitrogen oxide, its preparation method and use |
-
2003
- 2003-11-13 CN CNB2003101062806A patent/CN1321742C/en not_active Expired - Fee Related
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1422694A (en) * | 2001-12-06 | 2003-06-11 | 中国科学院大连化学物理研究所 | Catalyst for reduction of nitrogen oxide, its preparation method and use |
Also Published As
| Publication number | Publication date |
|---|---|
| CN1544144A (en) | 2004-11-10 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Mehtab et al. | Rare earth doped metal oxide nanoparticles for photocatalysis: a perspective | |
| Singh et al. | Erbium doped TiO2 interconnected mesoporous spheres as an efficient visible light catalyst for photocatalytic applications | |
| Li et al. | Oxygen vacancies-modified S-scheme Bi2Ti2O7/CaTiO3 heterojunction for highly efficient photocatalytic NO removal under visible light | |
| Belousov et al. | Pyrochlore oxides as visible light-responsive photocatalysts | |
| Masekela et al. | Green synthesis and enhanced photocatalytic performance of Co-Doped CuO nanoparticles for efficient degradation of synthetic dyes and water splitting | |
| Palas et al. | Bioinspired metal oxide particles as efficient wet air oxidation and photocatalytic oxidation catalysts for the degradation of acetaminophen in aqueous phase | |
| CN100408166C (en) | AgTO2Visible light response photocatalysis material of type composite oxide and application thereof | |
| Imranullah et al. | Stable and highly efficient natural sunlight driven photo-degradation of organic pollutants using hierarchical porous flower-like spinel nickel cobaltite nanoflakes | |
| CN101612561A (en) | Visible light-responsive bismuth composite oxide photocatalyst and preparation method thereof | |
| JP3742873B2 (en) | Photocatalyst, method for producing hydrogen using the same, and method for decomposing toxic substances | |
| JP3890414B2 (en) | Perovskite complex oxide visible light responsive photocatalyst, hydrogen production method using the same, and hazardous chemical decomposition method | |
| Chang et al. | Synthesis and photocatalytic activity of monolithic Fe2O3/TiO2 | |
| CN1321742C (en) | Visible light response photocatalyst and application thereof | |
| CN104190404B (en) | Visible light-responded photochemical catalyst SmNbMo2O10And preparation method thereof | |
| CN102228836B (en) | Visible light-responsive composite oxide photocatalyst Li3Co2Nb1-xTaxO6 and its preparation method | |
| CN100377778C (en) | Titanium oxide photocatalyst excited by visible light and its synthesis method | |
| JP4997627B2 (en) | Visible light responsive photocatalyst | |
| JP3834625B2 (en) | Indium barium composite oxide visible light responsive photocatalyst, method for producing hydrogen using this photocatalyst, and method for decomposing harmful chemical substances | |
| CN1905940A (en) | Photocatalyst based on composite oxide responsive to visible light and method for decomposition and removal of harmful chemical material using the same | |
| Kikugawa et al. | Photoinduced degradation of organic dye over LiBiO3 under illumination of white fluorescent light | |
| JP4296259B2 (en) | Method for producing hydrogen | |
| KAMAL et al. | Solar radiation assisted Photocatalytic Degradation of Congo red using Ce doped LaCoO\(_ {3}\): photocatalytic degradation of dyes | |
| CN1214864C (en) | Visible light-responsive photocatalysts and their applications of bismuth-based composite oxides of alkali metals and Ag | |
| Mekonnen | An overview of the developments of nanotechnology and heterogeneous photocatalysis in the presence of metal nanoparticles | |
| Panahi et al. | Synthesis and visible-light photocatalytic activity of nanoperovskites and exploration of silver decoration to enhance photocatalytic efficiency |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| C19 | Lapse of patent right due to non-payment of the annual fee | ||
| CF01 | Termination of patent right due to non-payment of annual fee |