EGU24-7949, updated on 08 Mar 2024
https://doi.org/10.5194/egusphere-egu24-7949
EGU General Assembly 2024
© Author(s) 2024. This work is distributed under
the Creative Commons Attribution 4.0 License.

Plastic input and dynamics in industrial composting

Stoyana Peneva1,4, Quynh Nhu Phan Le2, Davi Munhoz3, Olivia Wrigley4, Flora Wille5, Giovana P.F. Macan6, Heidi Doose7, Wulf Amelung4,8, and Melanie Braun4
Stoyana Peneva et al.
  • 1Wessling GmbH, Am Umweltpark 1, Bochum, 44793, Germany (stoyana.peneva@wessling.de)
  • 2Lancaster Environment Centre, Lancaster University, Lancaster LA1 4YQ, UK
  • 3Soil Physics and Land Management Group, Wageningen University & Research, P.O. Box 47, 6700 AA Wageningen, the Netherlands
  • 4Institute of Crop Science and Resource Conservation (INRES), Soil Science and Soil Ecology, University of Bonn, Nussallee 13, 53115 Bonn, Germany
  • 5Institute of Biogeochemistry and Pollutant Dynamics, ETH Zurich, 8092 Zurich, Switzerland
  • 6Institute for Sustainable Agriculture – Spanish National Research Council (IAS-CSIC), Avda Menéndez Pidal S/N, 14004, Cordoba, Spain
  • 7Wessling Consulting Engineering GmbH & Co.KG, Feodor-Lynen Straße 23, Hannover, 30625, Germany
  • 8Agrosphere Institute (IBG-3), Forschungszentrum Jülich GmbH, Wilhelm-Johnen-Str. 52425 15 Jülich, Germany

Despite various attempts by composting facilities to remove plastics from compost, high levels of particularly small microplastics (1 µm - 5 mm, MiPs) are detected in compost.

To elucidate the potential removal or enrichment of MiP during the composting process, we first analyzed the input of macroplastics (> 20 mm, MaPs) via bio-waste collection in an industrial composting plant. Then, we further determined MiPs at five different stages during the composting process (before and after distinct shredding and screening processes), as well as in the water used for irrigation.

We found varying total concentrations of MaP in the bio-waste collected from different municipalities, ranging from 0.36 - 4.72 kg ton-1 bio-waste, with polyethylene (PE) and polypropylene (PP) being the most abundant types. Further, we found a similar presence of “foil” and “non-foil” plastics, with 0.824 ± 0.34 kg ton-1 and 0.83 ± 0.34 kg ton-1 bio-waste, respectively; only 0.3 ± 0.1 kg ton-1 bio-waste of biodegradable plastic was found. The total concentration of MaP and MiP increased from 12 items kg-1 before shredding to 34 items kg-1 bio-waste in the final compost, indicating a relative enrichment of the number of particles during the process. Analyzing the rain water used for moistening the compost (collected on the roof of the compost facility) revealed that already high amounts of PE, polyamide (PA) and PP particles with sizes of 6 - 70 µm were found in rainwater (22,714 ± 2,975; 3,108 ± 748 and 685 ± 398 particles L-1, respectively). These plastic loads were 1.4 to 5-fold lower in the process water collected after irrigation, indicating a co-contamination of compost by irrigation. 

This study highlights the importance of reducing plastic input via bio-waste, as it is one of the main sources for MiP contamination of compost, while also recognizing the challenges in effectively removing MiP during composting. The complex dynamics of MiPs, i.e. the enrichment of small MiPs, is problematic as small particles in particular have many ecotoxicological properties. We could identify irrigation water as a plastic source for compost, an input pathway that has been overlooked so far. Therefore, our results underline the need for comprehensive strategies to tackle plastic pollution throughout the composting cycle, from bio-waste input to final compost products.

 

How to cite: Peneva, S., Phan Le, Q. N., Munhoz, D., Wrigley, O., Wille, F., Macan, G. P. F., Doose, H., Amelung, W., and Braun, M.: Plastic input and dynamics in industrial composting, EGU General Assembly 2024, Vienna, Austria, 14–19 Apr 2024, EGU24-7949, https://doi.org/10.5194/egusphere-egu24-7949, 2024.