Tan Yulan, Cao Xuedi, Chen Shujuan, Ao Xiaoling, Li Jianlong, Hu Kaidi, Liu Shuliang, Penttinen Petri, Yang Yong, Yu Xiumei, Liu Aiping, Liu Chengxi, Zhao Ke, Zou Likou
College of Resource, Sichuan Agricultural University, Chengdu, Sichuan 611130, China.
College of Food Science, Sichuan Agricultural University, Ya'an, Sichuan 625014, China.
Sci Total Environ. 2023 Mar 25;866:161386. doi: 10.1016/j.scitotenv.2023.161386. Epub 2023 Jan 4.
Municipal sewage sludge has been generated in increasing amounts with the acceleration of urbanization and economic development. The nutrient rich sewage sludge can be recycled by composting that has a great potential to produce stabilized organic fertilizer and substrate for plant cultivation. However, little is known about the metals, pathogens and antibiotic resistance transfer risks involved in applying the composted sludge in agriculture. We studied changes in and relationships between heavy metal contents, microbial communities, and antibiotic resistance genes (ARGs), heavy metal resistance genes (HMRGs) and mobile genetic elements (MGEs) in aerobic composting of sewage sludge. The contents of most of the analyzed heavy metals were not lower after composting. The bacterial α-diversity was lower, and the community composition was different after composting. Firmicutes were enriched, and Proteobacteria and potential pathogens in the genera Arcobacter and Acinetobacter were depleted in the composted sludge. The differences in bacteria were possibly due to the high temperature phase during the composting which was likely to affect temperature-sensitive bacteria. The number of detected ARGs, HMRGs and MGEs was lower, and the relative abundances of several resistance genes were lower after composting. However, the abundance of seven ARGs and six HMRGs remained on the same level after composting. Co-occurrence analysis of bacterial taxa and the genes suggested that the ARGs may spread via horizontal gene transfer during composting. In summary, even though aerobic composting is effective for managing sewage sludge and to decrease the relative abundance of potential pathogens, ARGs and HMRGs, it might include a potential risk for the dissemination of ARGs in the environment.
随着城市化进程的加快和经济的发展,城市污水污泥的产量不断增加。营养丰富的污水污泥可以通过堆肥进行回收利用,这对于生产稳定的有机肥料和植物栽培基质具有巨大潜力。然而,对于将堆肥污泥应用于农业所涉及的金属、病原体和抗生素抗性转移风险,人们了解甚少。我们研究了污水污泥好氧堆肥过程中重金属含量、微生物群落以及抗生素抗性基因(ARGs)、重金属抗性基因(HMRGs)和移动遗传元件(MGEs)之间的变化及其相互关系。堆肥后,大多数分析的重金属含量并未降低。细菌的α多样性降低,堆肥后的群落组成也有所不同。厚壁菌门富集,而变形菌门以及弓形杆菌属和不动杆菌属中的潜在病原体在堆肥污泥中减少。细菌的差异可能是由于堆肥过程中的高温阶段,这可能会影响对温度敏感的细菌。堆肥后,检测到的ARGs、HMRGs和MGEs数量减少,几种抗性基因的相对丰度也降低。然而,七种ARGs和六种HMRGs的丰度在堆肥后仍保持在同一水平。细菌分类群与基因的共现分析表明,ARGs可能在堆肥过程中通过水平基因转移传播。总之,尽管好氧堆肥对于处理污水污泥和降低潜在病原体、ARGs和HMRGs的相对丰度是有效的,但它可能存在ARGs在环境中传播的潜在风险。