Magnetic biochar promotes the risk of mobile genetic elements propagation in sludge anaerobic digestion

Yanru Zhang1, Yinping Xiang2, Rui Xu3

  • 1Hunan Academy of Forestry and State Key Laboratory of Utilization of Woody Oil Resource, Changsha, 410004, China; School of Chemical Engineering, Zhengzhou University, Zhengzhou, 450001, China; College of Environmental Science and Engineering, Hunan University, Changsha, 410082, China.

Insights

Magnetic biochar addition to anaerobic digestion (AD) sludge increases mobile genetic elements (MGEs) abundance, raising antibiotic resistance gene risks. However, optimal magnetic biochar dosage boosts biogas yield by enhancing microbial activity.

Area of Science:

  • Environmental microbiology
  • Biotechnology
  • Biochar applications

Background:

  • Mobile genetic elements (MGEs) drive antibiotic resistance gene spread via horizontal gene transfer.
  • The impact of magnetic biochar on MGEs in anaerobic digestion (AD) sludge is not well understood.
  • Investigating MGEs behavior under magnetic biochar influence is crucial for managing AD systems.

Purpose of the Study:

  • To evaluate the effects of varying magnetic biochar dosages on MGEs in AD reactors.
  • To assess the influence of magnetic biochar on microbial communities and biogas production.
  • To determine the relationship between magnetic biochar, MGEs, and potential host bacteria.

Main Methods:

  • Anaerobic digestion experiments with different magnetic biochar dosages.
  • Quantification of MGEs absolute and relative abundance using molecular techniques.
  • Analysis of microbial community structure and co-occurrence networks.
  • Redundancy analysis and variation partitioning to identify influencing factors.

Main Results:

  • Optimal magnetic biochar dosage (25 mg g⁻¹ TSadded) maximized biogas yield by enhancing hydrolysis and methanogenesis.
  • Magnetic biochar significantly increased total MGEs abundance (11.58%-77.37%) and specifically enriched ISCR1 (158.90-214.16%).
  • IntI1 abundance decreased, with removal rates of 14.38-40.00%, inversely proportional to biochar dosage.
  • Proteobacteria, Firmicutes, and Actinobacteriota were identified as main MGEs hosts.
  • Polysaccharides, protein, and soluble chemical oxygen demand (sCOD) were key drivers of MGEs variation.

Conclusions:

  • Magnetic biochar alters MGEs abundance by modifying host community structure and abundance in AD systems.
  • While enhancing biogas production, magnetic biochar application increases the proliferation risk of MGEs.
  • Further research is needed to balance biogas optimization with the control of antibiotic resistance gene reservoirs.