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Morphology, Absorption Spectra, and Photocatalytic Activity of Nanosized Solid Solution Ti_(1-x)Eu_xO_(2-x)/2

机译:纳米固溶体Ti_(1-x)Eu_xO_(2-x)/ 2的形貌,吸收光谱和光催化活性

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摘要

Tremendous interest in titanium dioxide is caused by its important practical application as a photocata-lyst of oxidation of toxic and colored organic compounds dissolved in water, as well as of water disinfection. Titanium dioxide, is an environmentally safe compound. Its use is not associated with accumulation of wastes that should be utilized or disposed of. It is believed that the higher photocatalytic activity of ana-tase, as compared with rutile, is due to the higher position of the Fermi level, the better ability to adsorb oxygen, and stronger tendency to hydroxylation [1]. However, titanium dioxide with the anatase structure as a photocatalyst has disadvantages that limit its use. Because of the wide band gap (E = 3.2 eV), anatase is active only in the UV spectral range and absorbs an insignificant part of solar light (~5%) [2, 3]. The enhancement of the photocatalytic activity of titanium dioxide and its shift toward longer wavelength can be achieved by doping the metal and oxygen sub-lattices of titania, as well as by changing the size and morphology of particles and modifying their bulk and surface properties. The introduction of lanthanide ions into the anatase structure leads to narrowing of the band gap and considerably decreases the electron-hole pair recombination rate, which improves the anatase photocatalytic activity under visible light irradiation [4|. However, there are data that point to the lack of such a correlation since the absorption band edge of anatase doped with various lanthanides is not noticeably shifted [5|. The difficulty of describing the mechanism of photocatalysis for these objects, as well as the inconsistency of the optical and catalytic properties of doped titania, is due to that different methods of synthesis of the photocatalyst have been used, which leads to oxides of different morphology, dimension, micro-structure, and structure imperfection.
机译:对二氧化钛的极大兴趣是由于其重要的实际应用作为光催化溶解在水中的有毒和有色有机化合物的氧化以及水消毒的。二氧化钛是一种环境安全的化合物。它的使用与应利用或处置的废物的积累无关。可以认为,与金红石相比,锐钛矿具有更高的光催化活性,这是由于费米能级较高,吸附氧的能力更强以及羟化趋势更强[1]。然而,具有锐钛矿结构的二氧化钛作为光催化剂具有限制其使用的缺点。由于宽带隙(E = 3.2 eV),锐钛矿仅在紫外线光谱范围内才有活性,并吸收不重要的太阳光(〜5%)[2,3]。通过掺杂二氧化钛的金属和氧亚晶格,以及通过改变颗粒的尺寸和形态以及改变其体积和表面性质,可以实现二氧化钛的光催化活性的增强及其向更长波长的转变。将镧系离子引入锐钛矿结构会导致带隙变窄,并显着降低电子-空穴对的复合速率,从而改善了可见光照射下的锐钛矿光催化活性[4 |。但是,有数据表明缺乏这种相关性,因为掺杂有各种镧系元素的锐钛矿的吸收带边缘没有明显偏移[5 |。难以描述这些物体的光催化机理,以及掺杂的二氧化钛的光学和催化性能不一致,是由于使用了不同的光催化剂合成方法,导致形成不同形态的氧化物,尺寸,微观结构和结构缺陷。

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