Abstract

Plant–soil feedbacks (PSFs) have gained attention for their potential role in explaining plant growth and invasion. While promising, most PSF research has measured plant monoculture growth on different soils in short‐term, greenhouse experiments. Here, five soil types were conditioned by growing one native species, three non‐native species, or a mixed plant community in different plots in a common‐garden experiment. After 4 years, plants were removed and one native and one non‐native plant community were planted into replicate plots of each soil type. After three additional years, the percentage cover of each of the three target species in each community was measured. These data were used to parameterize a plant community growth model. Model predictions were compared to native and non‐native abundance on the landscape. Native community cover was lowest on soil conditioned by the dominant non‐native, Centaurea diffusa, and non‐native community cover was lowest on soil cultivated by the dominant native, Pseudoroegneria spicata. Consistent with plant growth on the landscape, the plant growth model predicted that the positive PSFs observed in the common‐garden experiment would result in two distinct communities on the landscape: a native plant community on native soils and a non‐native plant community on non‐native soils. In contrast, when PSF effects were removed, the model predicted that non‐native plants would dominate all soils, which was not consistent with plant growth on the landscape. Results provide an example where PSF effects were large enough to change the rank‐order abundance of native and non‐native plant communities and to explain plant distributions on the landscape. The positive PSFs that contributed to this effect reflected the ability of the two dominant plant species to suppress each other's growth. Results suggest that plant dominance, at least in this system, reflects the ability of a species to suppress the growth of dominant competitors through soil‐mediated effects.

Highlights

  • Plant–soil feedbacks (PSFs) have rapidly gained attention as a potential mechanism explaining plant abundance, coexistence, succession, and invasion (Bailey & Schweitzer, 2016; van Der Putten et al, 2013; van der Heijden, Bardgett, & van Straalen, 2008)

  • Mathematical models suggest that positive PSFs will result in persistent monocultures, whereas negative PSFs will result in coexistence through species replacements (Bever, 1994; Bever, Westover, & Antonovics, 1997; Vincenot, Cartenì, Bonanomi, Mazzoleni, & Giannino, 2017)

  • Both the native and non-­native plant communities realized positive PSFs. When these data were used to parameterize a plant growth model, native plants were predicted to dominate their own soils and non-­native plants were predicted to dominate their own soils. This prediction was consistent with patterns of plant abundance on the landscape: native plants dominate and are persistent on never-­tilled fields and non-­native plants dominate and are persistent on abandoned-­agricultural fields (Kulmatiski, 2006)

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Summary

Introduction

Plant–soil feedbacks (PSFs) have rapidly gained attention as a potential mechanism explaining plant abundance, coexistence, succession, and invasion (Bailey & Schweitzer, 2016; van Der Putten et al, 2013; van der Heijden, Bardgett, & van Straalen, 2008). Positive PSF results when a plant grows better on “self” than “other” soils. Negative PSF results when a plant grows better on “other” than “self” soils. Mathematical models suggest that positive PSFs will result in persistent monocultures, whereas negative PSFs will result in coexistence through species replacements (Bever, 1994; Bever, Westover, & Antonovics, 1997; Vincenot, Cartenì, Bonanomi, Mazzoleni, & Giannino, 2017). These model predictions, assume that plants are competitively equivalent. Some of the best support for PSF model predictions comes from correlations between PSF and plant abundance on the landscape, but even these correlative tests remain rare (Bennett et al, 2017; Klironomos, 2002; Mangan et al, 2010; Teste et al, 2017)

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