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CHARACTERISTICS OF NATURAL ORGANIC MATTER DEGRADATION IN WATER BY UV/H_2O_2 TREATMENT

机译:UV / H_2O_2处理水中天然有机物的降解特性。

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This study evaluated the UV/H_2O_2 system for degradation of natural organic matter in water. The photolysis experiments were conducted in a 10-1 batch reactor using a 450-watt high-pressure mercury vapor lamp as the light source. The addition of H_2O_2 in water greatly improved the rate of humic acid degradation by UV light and 90% of the humic acid was removed within 30 min of photolysis. Kinetic data showed that the first-order reaction could be used to describe the kinetics of both humic acid oxidation and H_2O_2 decomposition, and the optimum H_2O_2 dose was 0.01%~0.05% for humic acid oxidation. It was also observed that the absorption of UVC (UV with wavelength between 200 and 280 nm) is responsible for the dissociation of H_2O_2 to generate the reactive hydroxyl radicals. Depending on the initial dosages, the H_2O_2 added to the system can be completely decomposed by UV within 50 to 90 minutes. Upon UV irradiation, the humic intermediates with smaller molecular sizes increase as a result of the degradation of larger humic substances. Photolysis of surface water also shows that the UV/H_2O_2 was effective in reducing trihalomethanes (THMs) formation in treating surface water with high contents of organic precursors. The distribution of THMs shifted from chlorine-THMs to bromine-THMs after UV/H_2O_2 treatments when bromide was present in water. However, higher H_2O_2 dosages would be necessary for the photolysis of surface water containing high concentrations of organic THM precursors. As observed from the Fourier transform infrared (FTIR) spectra, the functional groups of treated humic acids were destructed significantly, including -OH (from -COOH and -COH), aromatic -C=C, and -C=O conjugated with aromatic rings.
机译:这项研究评估了UV / H_2O_2系统对水中天然有机物的降解。光解实验是在10-1批反应器中进行的,使用450瓦高压汞蒸气灯作为光源。水中加入H_2O_2极大地提高了腐殖酸在紫外光下的降解速度,在光解30分钟内去除了90%的腐殖酸。动力学数据表明,一级反应可用于描述腐殖酸氧化和H_2O_2分解的动力学,腐殖酸氧化的最佳H_2O_2剂量为0.01%〜0.05%。还观察到UVC(波长在200至280nm之间的UV)的吸收是导致H_2O_2离解以产生反应性羟基的原因。根据初始剂量,添加到系统中的H_2O_2可以在50至90分钟内被紫外线完全分解。在紫外线照射下,由于较大的腐殖质的降解,分子尺寸较小的腐殖中间体增加了。地表水的光解还表明,UV / H_2O_2可有效减少三卤甲烷(THMs)的形成,以处理有机物含量较高的地表水。当水中存在溴化物时,UV / H_2O_2处理后,THMs的分布从氯-THMs变为溴-THMs。但是,对于含有高浓度有机THM前体的地表水进行光解,将需要更高的H_2O_2剂量。从傅立叶变换红外(FTIR)光谱中观察到,处理过的腐殖酸的官能团被严重破坏,包括-OH(来自-COOH和-COH),芳族-C = C和-C = O与芳环共轭。

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