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The effect of titanium dioxide alumina beads on the photocatalytic degradation of picloram in water

机译:二氧化钛氧化铝珠对水中吡咯烷的光催化降解作用

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Photocatalytic degradation of pesticides with titanium dioxide (TiO2) and other catalysts has shown promise as a potential water remediation method. Titanium-based powders have been used in photocatalytic degradation studies but have limitations. The objective of this study was to determine picloram degradation in water using various UV light sources and low-pressure metal organic chemical vapor deposition titanium dioxide alumina beads (TDABs) as a catalyst. A triple-annular, flow-through photoreactor was used as a degradation chamber. A picloram test solution of 50,mug/mL was introduced to the photoreactor inlet and recycled for 10 h at a flow rate of 50 mL/min. Three ultraviolet light sources were compared for their photocatalytic capacity (UV-A, UV-B, and UV-C) both with and without TDABs. TDABs were added to the photoreactor at 1.8 g/cm(3). Dark treatments with and without TDABs were included to quantify hydrolysis or adsorption. A 500-muL aliquot was taken from the test solution 14 times during the 10-h recycling period. Sampling times ranged from 0 to 600 min (10 h). These aliquots were placed in a vial and analyzed by high performance liquid chromatography equipped with a photodiode array detector. Picloram was not significantly hydrolyzed or adsorbed to TDABs during the experiment. The picloram degradation rate with UV-A and TDABs (t(1/2) = 119.5 min) was greater than the degradation rate of UV-A alone (t(1/2) = 2288 min). Picloram degradation was not enhanced by the presence of TDABs with either UV-B or UV-C. This may be attributed to inadequate TDAB densities and/or poor light penetration in the photoreactor. Rapid picloram degradation occurred with both UV-B and UV-C, regardless of the presence of TDABs with mean half-lives ranging from 7 to 18 min. These rates were 8 to 16 times faster than picloram degradation using UV-A with TDABs. TDABs' greatest photocatalytic effect was with the lowest energy light source (UV-A). However, picloram degradation was not enhanced when TDABs were combined with more powerful, shorter wavelength light. [References: 28]
机译:用二氧化钛(TiO2)和其他催化剂光催化降解农药已显示出有望作为一种潜在的水修复方法。钛基粉末已用于光催化降解研究,但有局限性。这项研究的目的是使用各种紫外线光源和低压金属有机化学气相沉积二氧化钛氧化铝珠(TDABs)作为催化剂来测定水中的吡咯仑降解。使用三环流通式光反应器作为降解室。将50.ug/mL的吡咯烷测试溶液引入光反应器入口,并以50 mL / min的流速循环10小时。比较了使用和不使用TDAB的三种紫外光源的光催化能力(UV-A,UV-B和UV-C)。 TDABs以1.8 g / cm(3)的量添加到光反应器中。包括有和没有TDAB的深色处理,以量化水解或吸附。在10小时的循环期间,从测试溶液中取出500毫升等分试样14次。采样时间为0到600分钟(10小时)。将这些等分试样置于小瓶中,并通过配备有光电二极管阵列检测器的高效液相色谱进行分析。在实验过程中,吡氯仑没有明显水解或吸附到TDABs上。 UV-A和TDAB的吡咯烷降解速率(t(1/2)= 119.5 min)大于单独的UV-A降解速率(t(1/2)= 2288 min)。含有UV-B或UV-C的TDAB并不能增强吡氯仑的降解。这可能归因于光敏反应器中TDAB密度不足和/或光穿透性差。 UV-B和UV-C均发生快速的吡咯喃降解,无论是否存在平均半衰期为7至18分钟的TDAB。这些速率比使用具有TDAB的UV-A降解吡咯烷快8至16倍。 TDAB的最大光催化作用是使用最低能量的光源(UV-A)。但是,将TDAB与更强大,更短波长的光结合使用时,吡氯吡喃的降解作用不会增强。 [参考:28]

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