Wang Shizong, Wang Jianlong
a Collaborative Innovation Center for Advanced Nuclear Energy Technology , INET, Tsinghua University , Beijing , People's Republic of China.
b Beijing Key Laboratory of Radioactive Wastes Treatment , Tsinghua University , Beijing , People's Republic of China.
Environ Technol. 2018 Aug;39(15):1985-1993. doi: 10.1080/09593330.2017.1345989. Epub 2017 Jul 5.
The emerging organic micro-pollutants (EMOPs) cannot be effectively removed by conventional wastewater treatment processes. In this paper, the most commonly detected EMOPs in the effluent of wastewater treatment plants, including trimethoprim, sulfamethoxazole, carbamazepine, diclofenac, triclosan and methyl 3,5-dichloro-4-hydroxybenzoate, were selected to acclimate activated sludge, to enhance the biodegradation of EMOPs. The results showed that the acclimated activated sludge can significantly enhance the removal of trimethoprim, sulfamethoxazole, diclofenac, triclosan and methyl 3,5-dichloro-4-hydroxybenzoate, but slightly improve the degradation of carbamazepine. The distribution of six EMOPs between water and sludge phases demonstrated that biodegradation made a major contribution to their removal. The maximal degradation rate constants were determined to be 0.9028 (sulfamethoxazole), 0.5374 (trimethoprim), 0.4123 (triclosan), 0.3544 (diclofenac), 0.2534 (methyl 3,5-dichloro-4-hydroxybenzoate) and 0.0224 (carbamazepine). Degradation intermediate products were detected in water phase at the end of the acclimation process through the comparison of high-performance liquid chromatography figures before and after the acclimation process, suggesting that degradation products of EMOPs might be in the effluents. In summary, the acclimation of activated sludge could be an option for removing EMOPs, and more attention should be paid to the degradation products of EMOPs in the effluent.
新兴有机微污染物(EMOPs)无法通过传统的废水处理工艺有效去除。本文选取了污水处理厂出水中最常检测到的EMOPs,包括甲氧苄啶、磺胺甲恶唑、卡马西平、双氯芬酸、三氯生和3,5-二氯-4-羟基苯甲酸甲酯,对活性污泥进行驯化,以增强EMOPs的生物降解。结果表明,驯化后的活性污泥能显著提高甲氧苄啶、磺胺甲恶唑、双氯芬酸、三氯生和3,5-二氯-4-羟基苯甲酸甲酯的去除率,但对卡马西平的降解略有改善。六种EMOPs在水相和污泥相之间的分布表明,生物降解对它们的去除起主要作用。最大降解速率常数分别为0.9028(磺胺甲恶唑)、0.5374(甲氧苄啶)、0.4123(三氯生)、0.3544(双氯芬酸)、0.2534(3,5-二氯-4-羟基苯甲酸甲酯)和0.0224(卡马西平)。通过比较驯化前后的高效液相色谱图,在驯化过程结束时水相中检测到了降解中间产物,这表明EMOPs的降解产物可能存在于出水中。总之,活性污泥驯化可能是去除EMOPs的一种选择,并且应更加关注出水中EMOPs的降解产物。