Microplastics spatiotemporal distribution and plastic-degrading bacteria identification in the sanitary and

Naying Li1, Zhiyong Han1, Nanfei Guo1

  • 1State Key Laboratory of Geohazard Prevention and Geoenvironment Protection (Chengdu University of Technology), Chengdu 610059, China; State Environmental Protection Key Laboratory of Synergetic Control and Joint Remediation for Soil & Water Pollution (Chengdu University of Technology), Chengdu 610059, China; College of Ecology and Environment, Chengdu University of Technology, Chengdu 610059, China.

Insights

Microplastics (MPs) in landfills degrade over time, with smaller sizes becoming more abundant. Specific plastic-degrading microorganisms (PDMs) are linked to the breakdown of different plastic types, indicating biological effects contribute to MP formation.

Area of Science:

  • Environmental Science
  • Microbiology
  • Polymer Science

Background:

  • Municipal solid waste landfills (MSWLs) are significant sources of microplastics (MPs).
  • The spatiotemporal distribution and degradation mechanisms of MPs in MSWLs remain unclear.
  • Landfills act as bioreactors for plastic-degrading microorganisms (PDMs).

Purpose of the Study:

  • To investigate the distribution and degradation of MPs in sanitary (SL) and non-sanitary landfills (NSL).
  • To identify dominant PDMs and their correlation with MP degradation.
  • To understand the role of biological effects in MP formation within MSWLs.

Main Methods:

  • Sampling of MPs and PDMs from SL and NSL at various depths.
  • Analysis of MP abundance, size distribution, and surface morphology.
  • Identification and quantification of PDMs using microbial techniques.
  • Correlation analysis between PDM abundance and MP degradation indicators.

Main Results:

  • Common MPs found include polyethylene (PE), polypropylene (PP), polystyrene (PS), polyurethane (PU), polyamide (PA), polyethylene terephthalate (PET), and polyvinyl chloride (PVC), with abundance from 0 to 80 items/g.
  • MPs showed surface degradation (fading, roughness, cracks, holes) with increasing landfill depth and age.
  • Tiny MPs (< 100 µm) increased significantly with depth (28.14%–49.13% in SL, 24.54%–59.51% in NSL), while large MPs decreased.
  • Dominant PDMs identified: Lysinibacillus and Bacillus in SL, Candidatus_Caldatribacterium in NSL.
  • PE degradation correlated with Candidatus_Cloacimonas and Candidatus_Caldatribacterium; PS and PA with Candidatus_Contubernalis; PVC with Candidatus_Caldatribacterium.

Conclusions:

  • Microplastic degradation in landfills is influenced by both physical/chemical and biological factors.
  • Specific PDMs play a crucial role in the degradation of different types of MPs.
  • The increasing abundance of smaller MPs suggests fragmentation processes are significant in landfill environments.
  • Biological degradation contributes to the overall transformation and potential formation of MPs within MSWLs.