44 45 are important determinants of AM fungal community structure, but stochastic processes like 53 dispersal can also influence AM fungal community structure and biogeographic patterns 54 (Chaudhary et al., 2008; Nielsen et al., 2016). Knowledge regarding AM fungal dispersal 55 mechanisms aids in the further incorporation of filamentous fungi into classic movement 56 ecology models (BielÄik et al., 2019). Furthermore, an improved understanding of AM fungal 57 dispersal, and how it may vary among species, improves our ability to manage mycorrhizal 58 symbioses in both natural and managed ecosystems (Hart et al., 2018). For example, efforts to 59 restore native mycorrhizal populations in anthropogenically disturbed soils could theoretically 60 focus on species with limited dispersal capabilities, but such efforts require species-specific 61 data on AM fungal dispersal to inform predictions. 62 Trait-based approaches are increasingly being utilized in ecology to shift from 63 descriptive to predictive work (Messier et al., 2010). Spores, the primary reproductive 64 propagule for AM fungi, differ among species with respect to a suite of quantifiable 65 morphological traits (e.g. intrinsic properties) that likely influence movement and dispersal 66 capabilities. Arbuscular mycorrhizas notoriously form the largest single-cell fungal spores on 67 Earth, with some species measuring larger than 1 mm in diameter and visible to the naked eye 68 (Nicolson & Schenck, 1979). However, different species form spores up to two orders of 69 magnitude smaller and, for a comparatively species-poor group, interspecific variation in AM 70 fungal spore size is considerable (Aguilar-Trigueros et al., 2018). Because spore size, to an 71 extent, can be proportional to aerial dispersal predictors such as settling velocity (Kauserud et 72 al., 2008; Norros et al., 2014), it could be a useful trait for making predictions regarding AM 73 fungal dispersal. Other spore traits, such as surface ornamentation or color may also influence 74 AM fungal aerial dispersal; species-specific pits or projections in spore surfaces could affect 75 fluid drag (Roper et al., 2008) and differences in the degree of spore melanization could be 76 linked to stress tolerances such as UV radiation during aerial movement (Deveautour et al., 77 2019). Patterns in fungal traits observed in aerially dispersed AM fungi have the potential to 78 bring increased insight into predictions regarding which species or groups of species are more 79 likely to disperse by wind or long distances. 80 128 symbioses can vary as fungal communities shift, studying AM fungal dispersal in cities has 129implications for efforts to improve urban sustainability (Chaudhary et al., 2019). We also 130 compare the measured traits of aerial spores to known traits for all described AM fungi present 131 in the FUN FUN fungal functional trait database (Zanne et al., 2019). We predict that aerial AM 132 fungal spores will possess traits more conducive to wind dispersal such as a sm...