Journal
JOURNAL OF ENVIRONMENTAL SCIENCE AND HEALTH PART B-PESTICIDES FOOD CONTAMINANTS AND AGRICULTURAL WASTES
Volume 50, Issue 4, Pages 247-260Publisher
TAYLOR & FRANCIS INC
DOI: 10.1080/03601234.2015.999592
Keywords
visible light; photocatalyst; degradation; N-doped TiO2; DDT; oxidation
Funding
- International Foundation for Science (IFS), Sweden
- Thailand Research Fund through the Royal Golden Jubilee, Ph.D. Program [PHD/0004/2549]
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1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (or p,p '-DDT) is one of the most persistent pesticides. It is resistant to breakdown in nature and cause the water contamination problem. In this work, a major objective was to demonstrate the application of N-doped TiO2 in degradation and mineralization of the p,p '-DDT under UV and visible light in aqueous solution. The N-doped TiO2 nanopowders were prepared by a simple modified sol-gel procedure using diethanolamine (DEA) as a nitrogen source. The catalyst characteristics were investigated using XRD, SEM, TEM, and XPS. The adsorption and photocatalytic oxidation of p,p '-DDT using the synthesized N-doped TiO2 under UV and visible light were conducted in a batch photocatalytic experiment. The kinetics and p,p '-DDT degradation performance of the N-doped TiO2 were evaluated. Results show that the N-doped TiO2 can degrade p,p '-DDT effectively under both UV and visible lights. The rate constant of the p,p '-DDT degradation under UV light was only 0.0121min(-1), whereas the rate constant of the p,p '-DDT degradation under visible light was 0.1282min(-1). Under visible light, the 100% degradation of p,p '-DDT were obtained from N-doped TiO2 catalyst. The reaction rate of p,p '-DDT degradation using N-doped TiO2 under visible light was sixfold higher than that under UV light. According to Langmuir-Hinshelwood model, the adsorption equilibrium constant (K) for the N-doped TiO2 under visible light was 0.03078 L mg(-1), and the apparent reaction rate constant (k) was 1.3941mg L-1-min. Major intermediates detected during the p,p '-DDT degradation were p,p '-DDE, o,p '-DDE, p,p '-DDD and p,p '-DDD. Results from this work can be applied further for the breakdown of p,p '-DDT molecule in the real contaminated water using this technology.
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