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Inactivation of Bacteria E. coli and photodegradation of humic acids using natural sunlight

机译:使用自然阳光灭活细菌大肠杆菌和腐殖酸的光降解

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In this work, the disinfection of bacteria Escherichia coli and degradation of humic acids, using sunlight, sunlight + TiO2 (Degussa P25) in suspension or TiO2 supported on Ahlstrom paper (NW10) fixed around concentric tubes inside the photoreactor, were investigated in a pilot plant. The inactivation of bacteria E. coli proved to be more efficient (only 1 kJuv/L for 5-log decrease in concentration) when using sunlight and TiO2 in suspension. However, true disinfection was not achieved under the conditions reported in this work. A first-order model was able to fit the photocatalytic deactivation of E, coli ([TiO2] = 50 mg/L) with an inactivation rate constant of 8.21 L/kJ. A Langmuir-Hinshelwood-like model was successfully applied for modelling photolysis and supported-TiO2 photocatalysis of bacteria E. coli, considering an initial latency period, a classical log-linear behaviour and a tail region. The effect of the flow rate between 5 and 15 L/min was negligible in the inactivation of E. coli in the presence of sunlight and supported TiO2. The inactivation rate constant increased with the initial concentration of E. coli. Almost no bacteria! regrowth was observed in dark conditions during 24 h after illumination of E. coli suspension until complete deactivation. The humic acids (HA) degradation was also investigated by solar photocatalysis with suspended and supported TiO2 and exposure to sunlight-only, in a CPC photoreactor. Supported-TiO2 photocatalysis of HA originated 70% concentration reduction after Q_(UV) ≈14 kJ/L, whereas only 20% reduction was obtained by photolysis and slurry photocatalysis. First-order kinetic constants of 0.088 and 0.010 L/kJ were obtained, respectively, for suspended and supported TiO2.
机译:在这项工作中,通过试点研究了使用日光,日光+悬浮的TiO2(Degussa P25)或负载在固定在光反应器内同心管上的Ahlstrom纸(NW10)上的TiO2悬浮液中的TiO2(Degussa P25)和阳光对细菌的消毒和腐殖酸的降解。厂。当在悬浮液中使用日光和TiO2时,细菌大肠杆菌的灭活被证明是更有效的(浓度降低5个对数仅1 kJuv / L)。但是,在这项工作中报告的条件下没有实现真正的消毒。一阶模型能够以8.21 L / kJ的失活速率常数拟合大肠杆菌的光催化失活([TiO2] = 50 mg / L)。考虑到初始潜伏期,经典的对数线性行为和尾部区域,成功地将Langmuir-Hinshelwood样模型应用于细菌的光解和负载型TiO2光催化建模。在存在阳光和负载的TiO2的条件下大肠杆菌的灭活中,流速在5 L / min至15 L / min之间的影响可忽略不计。灭活速率常数随大肠杆菌的初始浓度而增加。几乎没有细菌!大肠杆菌悬浮液光照后24小时内,在黑暗条件下观察到再生长,直至完全失活。腐殖酸(HA)的降解还通过在CPC光反应器中通过悬浮和负载的TiO2的太阳光催化以及仅暴露于阳光下进行了研究。 Q_(UV)≈14kJ / L后,HA的负载型TiO2光催化导致浓度降低70%,而光解和淤浆光催化仅降低20%。悬浮和负载的TiO2的一级动力学常数分别为0.088和0.010 L / kJ。

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