Although most plastic pollution originates on land, current research largely remains focused on aquatic ecosystems. Studies pioneering terrestrial microplastic research have adapted analytical methods from aquatic research without acknowledging the complex nature of soil. Meanwhile, novel methods have been developed and further refined. However, methodical inconsistencies still challenge a comprehensive understanding of microplastic occurrence and fate in and on soil. This review aims to disentangle the variety of state-of-the-art sample preparation techniques for heterogeneous solid matrices to identify and discuss best-practice methods for soil-focused microplastic analyses. We show that soil sampling, homogenization, and aggregate dispersion are often neglected or incompletely documented. Microplastic preconcentration is typically performed by separating inorganic soil constituents with high-density salt solutions. Not yet standardized but currently most used separation setups involve overflowing beakers to retrieve supernatant plastics, although closed-design separation funnels probably reduce the risk of contamination. Fenton reagent may be particularly useful to digest soil organic matter if suspected to interfere with subsequent microplastic quantification. A promising new approach is extraction of target polymers with organic solvents. However, insufficiently characterized soils still impede an informed decision on optimal sample preparation. Further research and method development thus requires thorough validation and quality control with well-characterized matrices to enable robust routine analyses for terrestrial microplastics.

Plastic pollution is increasingly perceived as an emerging threat to terrestrial environments, but the spatial and temporal dimension of plastic exposure in soils is poorly understood. Bioturbation displaces microplastics (>1 μm) in soils and likely also nanoplastics (<1 μm), but empirical evidence is lacking. We used a combination of methods that allowed us to not only quantify but to also understand the mechanisms of biologically driven transport of nanoplastics in microcosms with the deep-burrowing earthworm Lumbricus terrestris. We hypothesized that ingestion and subsurface excretion drives deep vertical transport of nanoplastics that subsequently accumulate in the drilosphere, i.e., burrow walls. Significant vertical transport of palladium-doped polystyrene nanoplastics (diameter 256 nm), traceable using elemental analysis, was observed and increased over 4 weeks. Nanoplastics were detected in depurated earthworms confirming their uptake without any detectable negative impact. Nanoplastics were indeed enriched in the drilosphere where cast material was visibly incorporated, and the reuse of initial burrows could be monitored via X-ray computed tomography. Moreover, the speed of nanoplastics transport to the deeper soil profile could not be explained with a local mixing model. Earthworms thus repeatedly ingested and excreted nanoplastics in the drilosphere calling for a more explicit inclusion of bioturbation in nanoplastic fate modeling under consideration of the dominant mechanism. Further investigation is required to quantify nanoplastic re-entrainment, such as during events of preferential flow in burrows.

Sewage sludge applications release contaminants to agricultural soils, such as potentially toxic metals and microplastics (MPs). However, factors determining the subsequent mobility of MPs in long-term field conditions are poorly understood. This study aimed to understand the vertical distribution of MPs in soils amended with sewage sludge in comparison to conventional mineral fertiliser for 24 years. The depth-dependent MP mass and number concentrations, plastic types, sizes and shapes were compared with the distribution of organic carbon and metals to provide insights into potentially transport-limiting factors. Polyethylene, polypropylene and polystyrene mass concentrations were screened down to 90 cm depth via pyrolysis-gas chromatography/mass spectrometry. MP number concentrations, additional plastic types, sizes, and shapes were analysed down to 40 cm depth using micro-Fourier transform-infrared imaging. Across all depths, MP numbers were twice and mass concentrations 8 times higher when sewage sludge was applied, with a higher share of textile-related plastics, more fibres and on average larger particles than in soil receiving mineral fertiliser. Transport of MPs beyond the plough layer (0-20 cm) is often assumed negligible, but substantial MP numbers (42 %) and mass (52 %) were detected down to 70 cm in sewage sludge-amended soils. The initial mobilization of MPs was shape- and size-dependent, because the fractions of fragmental-shaped and relatively small MPs increased directly below the plough layer, but not at greater depths. The sharp decline of total MP concentrations between 20 and 40 cm depth resembled that of metals and organic matter suggesting similar transport limitations. We hypothesize that the effect of soil management, such as ploughing, on soil compactness and subsequent transport by bioturbation and via macropores drives vertical MP distribution over long time scales. Risk assessment in soils should therefore account for considerable MP displacement to avoid underestimating soil exposure.

Micro- and nanoplastics (MNPs) are small plastic particles that are emitted to soils via a range of different pathways with potentially adverse effects on the soil ecosystem. In this thesis, field and laboratory studies were done to investigate the spatial distribution of MNPs in agricultural soils for an improved understanding of input pathways, transport mechanisms and potentially transport limiting factors that modify local exposure levels. Microplastics (MPs) detected in soil profiles taken from long-term field trials revealed that amendments with sewage sludge led to higher exposure to MPs than when conventional mineral fertiliser was applied. Moreover, substantial transport was observed in the field, likely a combined result of macropore transport and bioturbation as influenced by soil management and earthworm activity. Microcosm studies of MNPs with the deep-burrowing earthworm Lumbricus terrestris revealed bioturbation as a relevant transport mechanism both for nanoplastics and MP fibres. Relatively small particles were transported faster, but particle aspect ratio and volume likely play decisive roles for the potential ingestion and subsequent transport rate by earthworms. Collectively, the results highlight the need to consider horizontal and vertical MNP mobility in soils, in particular transport by bioturbation, for future monitoring schemes and mass balances. The comparison of a range of analytical methods to quantify and characterise MNPs revealed further need to optimize detection and recovery, as well as improve conversion methods between particle- and mass-based approaches for achieving reliable exposure estimates. Further investigations are necessary to assess the transport potential of other MNP shapes and sizes, by other earthworm ecotypes and under differing soil conditions and soil management systems.

Microplastic pollution of the terrestrial environment and its potential impact on ecosystem services are gaining increasing public and scientific attention. Although the number of investigations on microplastic presence in soil under different management systems is growing, knowledge on the potential mobility of microplastics and their spatial distribution within soil is still lacking. In particular, microplastic fibres are often considered less mobile in soil due to their elongated shape and the resulting potential entanglement in pore structures or aggregated soil particles. While these processes may affect their water-driven transport, biologically-driven transport may still occur unimpeded because particles may be ingested by macrofauna such as earthworms. Micro- and nanoplastic transport by earthworms has been previously observed, however, the effect of particle shape on the transport dynamics is still elusive.For understanding microplastic fibre transport in soil from a mechanistic perspective, we performed a series of process-studies with deep-burrowing earthworms, i.e. Lumbricus terrestris, in microcosms. We utilized metal-doped fibrous polyethylene terephthalate (PET) microplastics (1.27±0.66 mm) for a facilitated detection through acid extraction and subsequent analysis via inductively-coupled plasma mass-spectrometry. Fibres were spiked into the top of the soil columns of the microcosms, which were sampled according to specific depth segments every 7 days for four weeks. As a result, we were able to quantify fibre transport in soil profiles with a temporal resolution. Earthworms were important drivers of vertical transport of microplastic fibres in the soil, with fibres visibly incorporated into burrow walls. Thus, despite their elongated shape and relative larger size, microplastic fibres are not necessarily immobilized by interactions with soil particles, but continuously affected by burrowing soil organisms. Understanding these transport dynamics and the potential spatial distribution of microplastics of different shapes and sizes in the field is crucial in order to support appropriate sampling schemes for monitoring and for obtaining accurate mass estimates of microplastic pollution of terrestrial ecosystems.