Xinjiang Key Laboratory of Environmental Pollution and Bioremediation, Xinjiang Institute of Ecology and Geography, Chinese Academy of Sciences, Urumqi, China; University of Chinese Academy of Sciences, Beijing 100049, China.
Xinjiang Key Laboratory of Environmental Pollution and Bioremediation, Xinjiang Institute of Ecology and Geography, Chinese Academy of Sciences, Urumqi, China; Key Laboratory of Microbial Technology for Industrial Pollution Control of Zhejiang Province, College of Environment, Zhejiang University of Technology, Hangzhou, China; University of Chinese Academy of Sciences, Beijing 100049, China.
Sci Total Environ. 2022 Sep 10;838(Pt 3):156263. doi: 10.1016/j.scitotenv.2022.156263. Epub 2022 May 27.
Municipal sewage sludge, a reservoir of antibiotic resistance genes (ARGs), is usually composted as fertilizer for agricultural application especially in arid and semi-arid areas. The evolution patterns of intracellular ARGs (iARGs) and extracellular ARGs (eARGs) during composting and their responses to soil salinization after long-term compost application kept unclear previously, which were systematically studied in the current study. The variation and dissemination risk of eARGs and iARGs with the salinization of farmland soils was also evaluated. Extra/intra-cellular ARGs relative abundance varied drastically through composting process. Generally, the relative abundance of the cell-free eARGs (f-eARGs) and the cell-adsorbed eARGs (a-eARGs) were 4.62 and 3.54 folds (median) higher than that of iARGs, respectively, during the entire composting process, which held true even before the sludge composting (false discovery rate, FDR p < 0.05). There was no significant difference in relative abundance between f-eARGs and a-eARGs. The relative abundance of eARGs gradually decreased with composting time but was relatively higher than iARGs. It was worth noting that iARGs rebounded in the maturation phase. However, an over ten-year application of the eARG-rich compost led to much more severe contamination of iARGs than eARGs in soil. Soil salinization caused remarkable rise of eARGs by 943.34-fold (FDR p < 0.05). The variation of ARGs during composting and soil salinization was closely related to the change of microbial community structure. In compost, the bacterial communities mainly interacting with ARGs were the Firmicutes (54 unique and 35 shared core genera); and the bacterial communities playing major roles in ARGs during soil salinization were Proteobacteria (116 unique and 53 shared core genera) and Actinobacteria (52 unique and 27 shared core genera). These findings are important for assessing the transmission risk of ARGs in compost application to farmland in arid and semi-arid areas.
城市污水污泥是抗生素耐药基因 (ARGs) 的储存库,通常作为肥料进行堆肥处理,用于农业应用,特别是在干旱和半干旱地区。以前,在堆肥过程中细胞内 ARGs (iARGs) 和细胞外 ARGs (eARGs) 的演变模式及其在长期堆肥应用后对土壤盐渍化的响应尚不清楚,本研究对此进行了系统研究。还评估了农田土壤盐渍化过程中外源/细胞内 ARGs 的变化和传播风险。通过堆肥过程,细胞外/内 ARGs 的相对丰度发生了剧烈变化。通常,在整个堆肥过程中,游离态细胞外 eARGs (f-eARGs) 和细胞吸附态 eARGs (a-eARGs) 的相对丰度分别比 iARGs 高 4.62 和 3.54 倍(中位数),即使在污泥堆肥之前(错误发现率, FDR p < 0.05)也是如此。f-eARGs 和 a-eARGs 的相对丰度没有显著差异。随着堆肥时间的延长,eARGs 的相对丰度逐渐降低,但相对高于 iARGs。值得注意的是,iARGs 在成熟阶段出现反弹。然而,经过十多年富含 eARG 的堆肥的应用,导致土壤中 iARGs 的污染比 eARGs 更为严重。土壤盐渍化导致 eARGs 显著增加了 943.34 倍(FDR p < 0.05)。在堆肥和土壤盐渍化过程中,ARGs 的变化与微生物群落结构的变化密切相关。在堆肥中,与 ARGs 主要相互作用的细菌群落主要是厚壁菌门(54 个特有和 35 个共享核心属);而在土壤盐渍化过程中对 ARGs 起主要作用的细菌群落是变形菌门(116 个特有和 53 个共享核心属)和放线菌门(52 个特有和 27 个共享核心属)。这些发现对于评估在干旱和半干旱地区将 ARGs 从堆肥应用到农田的传播风险具有重要意义。