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废水排放至原始溪流后磺胺抗性基因及人为污染标志物的命运。

The fate of sulfonamide resistance genes and anthropogenic pollution marker after discharge of wastewater into a pristine river stream.

作者信息

Haenelt Sarah, Wang Gangan, Kasmanas Jonas Coelho, Musat Florin, Richnow Hans Hermann, da Rocha Ulisses Nunes, Müller Jochen A, Musat Niculina

机构信息

Department of Isotope Biogeochemistry, Helmholtz Centre for Environmental Research, Leipzig, Germany.

Department of Environmental Microbiology, Helmholtz Centre for Environmental Research, Leipzig, Germany.

出版信息

Front Microbiol. 2023 Jan 25;14:1058350. doi: 10.3389/fmicb.2023.1058350. eCollection 2023.

Abstract

INTRODUCTION

Currently there are sparse regulations regarding the discharge of antibiotics from wastewater treatment plants (WWTP) into river systems, making surface waters a latent reservoir for antibiotics and antibiotic resistance genes (ARGs). To better understand factors that influence the fate of ARGs in the environment and to foster surveillance of antibiotic resistance spreading in such habitats, several indicator genes have been proposed, including the integrase gene and the sulfonamide resistance genes and .

METHODS

Here we used quantitative PCR and long-read nanopore sequencing to monitor the abundance of these indicator genes and ARGs present as class 1 integron gene cassettes in a river system from pristine source to WWTP-impacted water. ARG abundance was compared with the dynamics of the microbial communities determined 16S rRNA gene amplicon sequencing, conventional water parameters and the concentration of sulfamethoxazole (SMX), sulfamethazine (SMZ) and sulfadiazine (SDZ).

RESULTS

Our results show that WWTP effluent was the principal source of all three sulfonamides with highest concentrations for SMX (median 8.6 ng/l), and of the indicator genes , and with median relative abundance to 16S rRNA gene of 0.55, 0.77 and 0.65%, respectively. Downstream from the WWTP, water quality improved constantly, including lower sulfonamide concentrations, decreasing abundances of and and lower numbers and diversity of ARGs in the class 1 integron. The riverine microbial community partially recovered after receiving WWTP effluent, which was consolidated by a microbiome recovery model. Surprisingly, the relative abundance of increased 3-fold over 13 km of the river stretch, suggesting an internal gene multiplication.

DISCUSSION

We found no evidence that low amounts of sulfonamides in the aquatic environment stimulate the maintenance or even spread of corresponding ARGs. Nevertheless, class 1 integrons carrying various ARGs were still present 13 km downstream from the WWTP. Therefore, limiting the release of ARG-harboring microorganisms may be more crucial for restricting the environmental spread of antimicrobial resistance than attenuating ng/L concentrations of antibiotics.

摘要

引言

目前,关于污水处理厂(WWTP)向河流系统排放抗生素的规定较为稀少,这使得地表水成为抗生素和抗生素抗性基因(ARG)的潜在储存库。为了更好地理解影响环境中ARG命运的因素,并加强对在此类栖息地传播的抗生素抗性的监测,人们提出了几种指示基因,包括整合酶基因以及磺胺类抗性基因和。

方法

在这里,我们使用定量PCR和长读长纳米孔测序来监测这些指示基因和作为1类整合子基因盒存在的ARG在从原始源头到受污水处理厂影响的水的河流系统中的丰度。将ARG丰度与通过16S rRNA基因扩增子测序确定的微生物群落动态、常规水参数以及磺胺甲恶唑(SMX)、磺胺二甲嘧啶(SMZ)和磺胺嘧啶(SDZ)的浓度进行比较。

结果

我们的结果表明,污水处理厂的出水是所有三种磺胺类药物的主要来源,其中SMX浓度最高(中位数8.6纳克/升),也是指示基因、和的主要来源,它们相对于16S rRNA基因的中位数相对丰度分别为0.55%、0.77%和0.65%。在污水处理厂下游,水质不断改善,包括较低的磺胺类药物浓度、和丰度的降低以及1类整合子中ARG的数量和多样性的减少。河流微生物群落在接收污水处理厂出水后部分恢复,这通过微生物群落恢复模型得到证实。令人惊讶的是,在河流13公里的河段中,的相对丰度增加了3倍,表明存在基因内部增殖。

讨论

我们没有发现证据表明水生环境中低含量的磺胺类药物会刺激相应ARG的维持甚至传播。然而,携带各种ARG的1类整合子在污水处理厂下游13公里处仍然存在。因此,限制携带ARG的微生物的释放对于限制抗菌素耐药性在环境中的传播可能比降低纳克/升浓度的抗生素更为关键。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a7e6/9907086/272ccf75ae36/fmicb-14-1058350-g001.jpg

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