College of Environmental Sciences, Sichuan Agricultural University, 211 Huimin Road, Chengdu, 611130, People's Republic of China.
Environ Geochem Health. 2024 Aug 21;46(10):385. doi: 10.1007/s10653-024-02164-3.
Due to anthropogenic activities such as mining, several agricultural soils are polluted by multiple heavy metals. However, it is still unclear whether multiple heavy metals could affect the distribution of antibiotic resistance genes (ARGs), and how metals affect ARGs. To understand ARGs' distribution in heavy metal-polluted soils, we chose soils contaminated by different types and contents of heavy metals to determine the ARGs' number and abundance through high-throughput quantitative real-time PCR (HT-qPCR) in this study. Additionally, the factors affecting ARGs' distribution, such as soil properties, mobile genetic genes (MGEs), and bacterial communities, were explored. The results demonstrated that the sampled soils were primarily contaminated by Cd, As, Pb, and Zn, and the pollution load index (PLI) values of these metals ranged from 1.3 to 2.7, indicating a low to moderate degree of heavy metal contamination. The number and abundance of ARGs ranged from 44 to 113 and from 2.74 × 10 copies/g to 1.07 × 10 copies/g, respectively. Besides, abundant MGEs in soils, ranging from 1.84 × 10 copies/g to 5.82 × 10 copies/g, were observed. The pathway analysis suggested that MGEs were the most important factor directly affecting ARG abundance (0.89). Notably, heavy metals also affected the ARG abundance. Proteobacteria and Actinobacteria, the main heavy metal tolerant bacteria, were found to be the main hosts of ARGs through network analysis. ARG-carrying pathogens (ACPs) in agricultural soils were found to carry MGEs, indicating a high risk of dissemination. This study provided important information for understanding the ARGs' fate and also the key factors affecting ARGs' spread in multiple heavy metal-contaminated soils.
由于采矿等人为活动,一些农业土壤受到多种重金属的污染。然而,目前尚不清楚多种重金属是否会影响抗生素抗性基因(ARGs)的分布,以及金属如何影响 ARGs。为了了解重金属污染土壤中 ARGs 的分布,我们选择了受不同类型和含量重金属污染的土壤,通过高通量实时定量 PCR(HT-qPCR)来确定 ARGs 的数量和丰度。此外,还探讨了影响 ARGs 分布的因素,如土壤特性、移动遗传基因(MGEs)和细菌群落。结果表明,采样土壤主要受到 Cd、As、Pb 和 Zn 的污染,这些金属的污染负荷指数(PLI)值在 1.3 到 2.7 之间,表明重金属污染程度为低到中度。ARGs 的数量和丰度分别在 44 到 113 和 2.74×10 拷贝/g 到 1.07×10 拷贝/g 之间。此外,土壤中还存在丰富的 MGEs,其丰度在 1.84×10 拷贝/g 到 5.82×10 拷贝/g 之间。途径分析表明,MGEs 是直接影响 ARG 丰度的最重要因素(0.89)。值得注意的是,重金属也会影响 ARG 的丰度。通过网络分析发现,耐重金属的主要细菌 Proteobacteria 和 Actinobacteria 是 ARGs 的主要宿主。在农业土壤中发现,携带 ARG 的病原菌(ACPs)携带 MGEs,表明其传播风险较高。本研究为了解 ARGs 的命运以及影响多种重金属污染土壤中 ARGs 传播的关键因素提供了重要信息。