Wang Hui, Yao Hong, Sun Peizhe, Pei Jin, Li Desheng, Huang Ching-Hua
Department of Municipal and Environmental Engineering, Beijing Jiaotong University, Beijing 100044, People's Republic of China.
Department of Municipal and Environmental Engineering, Beijing Jiaotong University, Beijing 100044, People's Republic of China.
Chemosphere. 2015 Jan;119:1255-1261. doi: 10.1016/j.chemosphere.2014.09.098. Epub 2014 Nov 1.
The presence of Fe(III) ions was found to induce degradation of three tetracycline antibiotics (TCs), tetracycline (TTC), oxytetracycline (OTC) and chlorotetracycline (CTC), in aqueous solutions without light. The presence of Fe(III) promoted the degradation of TCs in most experimental pH (5.0, 7.0 and 9.0) except at pH 9.0 for CTC. Degradation rate constants of TTC, OTC and CTC reached maximum ((6.2±0.5)×10(-3) h(-1), (10.6±0.1)×10(-3) h(-1) and (15.9±0.5)×10(-3) h(-1) at pH 7.0, 20 °C) when Fe(III):TC molar ratio was 1:1, 1:1 and 2:1, respectively. Such metal-to-ligand ratios agreed well with the most favorable complexation between Fe(III) and each TC. Compared to without metals, Fe(III) enhanced the degradation rate of TTC, OTC and CTC by up to 20.67, 7.07 and 2.30 times, respectively, in clean water matrix, and also promoted degradation of TCs in real surface water and wastewater matrices. The promoted degradation likely occurred via complexation of TCs and subsequent oxidation by Fe(III). Degradation results of CTC versus 4-epi-CTC suggested Fe(III) likely binds to TCs' C4 dimethylamino group. Toxicity of the complexes evaluated using Photobacterium phosphoreum T3 was increased after several hours of reaction, suggesting the transformation products may exert a stronger toxicity than parent TCs. This study identifies new oxidative transformation of TCs induced by Fe(III) ions without light irradiation, further supporting the important role of iron species in the environmental fate of TCs.
研究发现,在无光条件下,水溶液中Fe(III)离子的存在会诱导三种四环素类抗生素(TCs),即四环素(TTC)、土霉素(OTC)和金霉素(CTC)发生降解。在大多数实验pH值(5.0、7.0和9.0)下,Fe(III)的存在促进了TCs的降解,但对于CTC在pH 9.0时除外。当Fe(III)与TC的摩尔比分别为1:1、1:1和2:1时,TTC、OTC和CTC的降解速率常数达到最大值(在pH 7.0、20℃时分别为(6.2±0.5)×10(-3) h(-1)、(10.6±0.1)×10(-3) h(-1)和(15.9±0.5)×10(-3) h(-1))。这种金属与配体的比例与Fe(III)与每种TC之间最有利的络合情况非常吻合。与无金属存在相比,在清洁水基质中,Fe(III)分别将TTC、OTC和CTC的降解速率提高了20.67、7.07和2.30倍,并且还促进了实际地表水和废水基质中TCs的降解。这种促进降解可能是通过TCs的络合以及随后被Fe(III)氧化而发生的。CTC与4-表-CTC的降解结果表明,Fe(III)可能与TCs的C4二甲基氨基结合。使用费氏弧菌T3评估的络合物毒性在反应数小时后增加,这表明转化产物可能比母体TCs具有更强的毒性。本研究确定了在无光照条件下由Fe(III)离子诱导的TCs新的氧化转化,进一步支持了铁物种在TCs环境归宿中的重要作用。