EGU25-5999, updated on 14 Mar 2025
https://doi.org/10.5194/egusphere-egu25-5999
EGU General Assembly 2025
© Author(s) 2025. This work is distributed under
the Creative Commons Attribution 4.0 License.
Oral | Thursday, 01 May, 16:20–16:30 (CEST)
 
Room 2.15
Nanoplastic- Fungi interaction – insights from various laboratory scales
Sascha Müller1, Hanbang Zou1, Martin Lundqvist2, Tommy Cedervall2, Micaela Mafla Endara3, and Edith Hammer1
Sascha Müller et al.
  • 1Aquatic Ecology, Department of Biology, Lund University (ULUND) – Ekologihuset, Sölvegatan 37, 22362 Lund, Sweden
  • 2Biochemistry and Structural Biology, Department of Chemistry, Lund University (ULUND) Sölvegatan 39, 22362 Lund, Sweden
  • 3Department of Forest Mycology and Plant Pathology; Division of Forest Microbiology, Swedish University of Agricultural Sciences (SLU), Almas allé 5, 756 51 Uppsala, Sweden.

Nanoplastic (NP) exposure to the terrestrial water cycle poses an emerging threat to subsurface ecosystems, while the continuous release of NP increases the risk of drinking water contamination.
Fungal communities are a crucial component of terrestrial ecosystems. Traditionally, their presence and functions have been studied in shallow soils as part of the soil microbiome or above ground as decomposers or pathogens. Recent mycobiome screening studies of groundwater wells have revealed the presence of fungal species in deeper aquifers. This confirms the presence of fungi across all compartments of the terrestrial water cycle, highlighting the need to investigate their role in contaminant transport processes.
Fungi have demonstrated the ability to immobilize dissolved organic contaminants, heavy metals, and pharmaceuticals from polluted waters. However, studies examining their effect on NP removal remain limited. Existing research generally lacks the integration of liquid flow dynamics, which is crucial for understanding fungal interactions in natural water systems.
We present a dataset, which shows dynamics of NP-fungi interaction across multiple laboratory scales. Our study compares batch adsorption experiments with transport experiments conducted in inoculated microfluidic chips and transport columns. Carboxylated polystyrene nanoparticles of 100 nm and 250 nm serve as model NPs. Following fungal inoculation in growth media, the experiments are conducted under various ion concentrations of CaCl and flow velocities ranging from 1 m/d and 30 m/d.
Our results indicate scale-dependent modes of NP-fungal interactions. In batch-scale experiments, higher ion concentrations significantly enhance the adsorption efficiency of NPs to fungal hyphae. In contrast, experiments conducted in microfluidic chips and transport columns reveal altered behavior, with notably lower adsorption efficiencies observed.
This suggests that in natural environments, factors such as the spatial distribution of hyphae, ion concentration, flow rates, and consequently reaction times, collectively influence the efficiency of NP removal by fungal communities.

How to cite: Müller, S., Zou, H., Lundqvist, M., Cedervall, T., Mafla Endara, M., and Hammer, E.: Nanoplastic- Fungi interaction – insights from various laboratory scales, EGU General Assembly 2025, Vienna, Austria, 27 Apr–2 May 2025, EGU25-5999, https://doi.org/10.5194/egusphere-egu25-5999, 2025.