School of Environmental Science and Engineering, Tianjin University, Tianjin 300072, China.
College of Environmental Science and Engineering, Ministry of Education Key Laboratory of Pollution Processes and Environmental Criteria, Nankai University, Tianjin 300071, China.
Water Res. 2015 Nov 15;85:458-66. doi: 10.1016/j.watres.2015.09.010. Epub 2015 Sep 7.
The propagation of antibiotic resistance genes (ARGs) is an emerging health concern worldwide. Thus, it is important to understand and mitigate their occurrence in different systems. In this study, 30 ARGs that confer resistance to tetracyclines, sulfonamides, quinolones or macrolides were detected in two activated sludge wastewater treatment plants (WWTPs) in northern China. Bacteria harboring ARGs persisted through all treatment units, and survived disinfection by chlorination in greater percentages than total Bacteria (assessed by 16S rRNA genes). Although the absolute abundances of ARGs were reduced from the raw influent to the effluent by 89.0%-99.8%, considerable ARG levels [(1.0 ± 0.2) × 10(3) to (9.5 ± 1.8) × 10(5) copies/mL)] were found in WWTP effluent samples. ARGs were concentrated in the waste sludge (through settling of bacteria and sludge dewatering) at (1.5 ± 2.3) × 10(9) to (2.2 ± 2.8) × 10(11) copies/g dry weight. Twelve ARGs (tetA, tetB, tetE, tetG, tetH, tetS, tetT, tetX, sul1, sul2, qnrB, ermC) were discharged through the dewatered sludge and plant effluent at higher rates than influent values, indicating overall proliferation of resistant bacteria. Significant antibiotic concentrations (2%-50% of raw influent concentrations) remained throughout all treatment units. This apparently contributed selective pressure for ARG replication since the relative abundance of resistant bacteria (assessed by ARG/16S rRNA gene ratios) was significantly correlated to the corresponding effluent antibiotic concentrations. Similarly, the concentrations of various heavy metals (which induce a similar bacterial resistance mechanism as antibiotics - efflux pumps) were also correlated to the enrichment of some ARGs. Thus, curtailing the release of antibiotics and heavy metals to sewage systems (or enhancing their removal in pre-treatment units) may alleviate their selective pressure and mitigate ARG proliferation in WWTPs.
抗生素耐药基因(ARGs)的传播是全球范围内一个新出现的健康问题。因此,了解并减轻它们在不同系统中的发生非常重要。在这项研究中,在中国北方的两个活性污泥废水处理厂(WWTP)中检测到了 30 种赋予四环素、磺胺类、喹诺酮类或大环内酯类抗生素耐药性的 ARGs。携带 ARGs 的细菌在所有处理单元中都存在,并且在氯消毒后比总细菌(通过 16S rRNA 基因评估)更能存活。尽管从原水到出水,ARGs 的绝对丰度通过 89.0%-99.8%,但在 WWTP 出水样本中仍发现相当高的 ARG 水平[(1.0±0.2)×10(3)到(9.5±1.8)×10(5)拷贝/mL)]。ARGs 集中在废污泥中(通过细菌沉降和污泥脱水),其浓度为(1.5±2.3)×10(9)到(2.2±2.8)×10(11)拷贝/g 干重。12 种 ARGs(tetA、tetB、tetE、tetG、tetH、tetS、tetT、tetX、sul1、sul2、qnrB、ermC)通过脱水污泥和工厂出水以比进水值更高的速率排出,表明耐药菌的总体增殖。在所有处理单元中都存在显著的抗生素浓度(为原水浓度的 2%-50%)。这显然为 ARG 复制提供了选择压力,因为耐药菌的相对丰度(通过 ARG/16S rRNA 基因比值评估)与相应的出水抗生素浓度显著相关。同样,各种重金属(其诱导与抗生素类似的细菌耐药机制-外排泵)的浓度也与一些 ARGs 的富集相关。因此,减少抗生素和重金属向污水系统的释放(或在预处理单元中增强其去除)可能会减轻它们的选择压力,并减轻 WWTP 中 ARG 的增殖。
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