Release of antibiotic resistant bacteria and genes in the effluent and biosolids of five wastewater utilities in Michigan

生物固体 流出物 污水处理 废水 四环素 细菌 活性污泥 化学 微生物学 制浆造纸工业 抗生素 生物 环境工程 环境科学 遗传学 工程类
作者
Mariya Munir,Kelvin Wong,Irene Xagoraraki
出处
期刊:Water Research [Elsevier BV]
卷期号:45 (2): 681-693 被引量:849
标识
DOI:10.1016/j.watres.2010.08.033
摘要

The purpose of this study was to quantify the occurrence and release of antibiotic resistant genes (ARGs) and antibiotic resistant bacteria (ARB) into the environment through the effluent and biosolids of different wastewater treatment utilities including an MBR (Membrane Biological Reactor) utility, conventional utilities (Activated Sludge, Oxidative Ditch and Rotatory Biological Contactors-RBCs) and multiple sludge treatment processes (Dewatering, Gravity Thickening, Anaerobic Digestion and Lime Stabilization). Samples of raw wastewater, pre- and post-disinfected effluents, and biosolids were monitored for tetracycline resistant genes (tetW and tetO) and sulfonamide resistant gene (Sul-I) and tetracycline and sulfonamide resistant bacteria. ARGs and ARB concentrations in the final effluent were found to be in the range of ND(non-detectable)-2.33 × 106 copies/100 mL and 5.00 × 102–6.10 × 105 CFU/100 mL respectively. Concentrations of ARGs (tetW and tetO) and 16s rRNA gene in the MBR effluent were observed to be 1–3 log less, compared to conventional treatment utilities. Significantly higher removals of ARGs and ARB were observed in the MBR facility (range of removal: 2.57–7.06 logs) compared to that in conventional treatment plants (range of removal: 2.37–4.56 logs) (p < 0.05). Disinfection (Chlorination and UV) processes did not contribute in significant reduction of ARGs and ARB (p > 0.05). In biosolids, ARGs and ARB concentrations were found to be in the range of 5.61 × 106–4.32 × 109 copies/g and 3.17 × 104–1.85 × 109 CFU/g, respectively. Significant differences (p < 0.05) were observed in concentrations of ARGs (except tetW) and ARB between the advanced biosolid treatment methods (i.e., anaerobic digestion and lime stabilization) and the conventional dewatering and gravity thickening methods.
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