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Ecological restoration is notoriously unpredictable because similar actions can result in different outcomes. Outcomes can also differ for species and functional components of communities depending on how restoration actions and abiotic conditions alter community assembly trajectories. Quantifying variation in community trajectories across restorations for both species and traits is rare, but can help to resolve underlying assembly processes and refine strategies to maximize restoration success.We quantified the importance of soil resources, seed mix richness, and prescribed fire for variation in plant species and functional trait trajectories over 6 years across 20 restored tallgrass prairies in the mid‐western United States. We predicted stronger convergence for traits than species, with species and trait compositions converging more across restorations on resource‐poor soils and with frequent fires due to stronger abiotic filtering. In contrast, we predicted species and trait compositions would converge more slowly or diverge across restorations with resource‐rich soils, with less frequent fires, and seeded with more species due to weaker filtering and more stochasticity.Communities generally converged over time; however, the rate of convergence was determined by soil resources, not restoration actions. Restorations converged more across resource‐rich sites. In contrast to patterns of species convergence, variation in trait composition remained stable over time regardless of soil resources or restoration actions.The unexpected pattern of species, but not trait, convergence during community assembly appears to result from increasing dominance of a native C4 bunchgrass, Andropogon gerardii that coincides with proportional declines of other C4 grasses that share similar traits.Synthesis and applications. Restoration outcomes may be more predictable than typically considered. Trait compositions were stable and variation in species compositions decreased over time owing to site conditions, where resource‐rich soils produced more consistent outcomes. Our study shows monitoring multiple facets of biodiversity across restorations can reveal why outcomes vary and inform broad‐scale restoration planning. [ABSTRACT FROM AUTHOR]

Control of invasive exotic species in restorations without compromising the native plant community is a challenge. Efficacy of exotic species control needs to consider collateral effects on the associated plant community. We asked (1) if short-term control of a dominant exotic invasive, Lespedeza cuneata in grassland restorations allows establishment of a more diverse native plant community, and (2) if control of the exotic and supplemental seed addition allows establishment of native species. A manipulative experiment tested the effects of herbicide treatments (five triclopyr and fluroxypyr formulations plus an untreated control) and seed addition (and unseeded control) on taxonomic and phylogenetic diversity, and community composition of restored grasslands in three sites over three years. We assessed response of L. cuneata through stem density counts, and response of the plant community through estimates of canopy cover. Herbicide treatments reduced the abundance of the exotic in the first field season leading to a less dispersed community composition compared with untreated controls, with the exotic regaining dominance by the third year. Supplemental seed addition did not provide extra resistance of the native community to reinvasion of the exotic. The communities were phylogenetically over-dispersed, but there was a short-term shift to lower phylogenetic diversity in response to herbicides consistent with a decrease in biotic filtering. Native plant communities in these grassland restorations were resilient to short-term reduction in abundance of a dominant invasive even though it was insufficient to provide an establishment window for native species establishment.

Few studies link seed dispersal with its demographic consequences, or provide reliable estimates of seed dispersal effectiveness. One reason is the complexity of measuring the suitability for plant recruitment of seed arrival sites. In this study, I compare three methods that differ in the effort required to measure site suitability for seedling recruitment. All are based on the proportion of seeds that become seedlings (seedling-to-seed ratios). Method I is the most detailed and labour intensive. The fate of seeds was followed throughout the different steps of the recruitment process, from fruit removal until seedling emergence, including both seeds dispersed by different animals and undispersed seeds. Method II is based on seed addition experiments. Seeds were sowed in plots, and seedlings emerging were counted in the following two seasons. In Method III, average seed input during dispersal was measured with soil seed bank samples taken in pre- and post-dispersal periods, and seedling emergence estimated with samples of three seasons. Method II provided results similar to those of Method I, which, conversely, provides more insight in the actual processes driving recruitment. Method III, however, systematically underestimated site suitability (seedling-to-seed ratios) by about 50% as compared to the other methods in all microhabitats studied. Relative instead of absolute indices of site suitability were, however, reliable with this method. Method II and III are significantly less costly and could be good alternatives to Method I for some purposes, simplifying future studies on the demographic consequences of seed dispersal and the effectiveness of dispersers. [ABSTRACT FROM AUTHOR]

Control of invasive exotic species in restorations without compromising the native plant community is a challenge. Efficacy of exotic species control needs to consider collateral effects on the associated plant community. We asked (1) if short-term control of a dominant exotic invasive, Lespedeza cuneata in grassland restorations allows establishment of a more diverse native plant community, and (2) if control of the exotic and supplemental seed addition allows establishment of native species. A manipulative experiment tested the effects of herbicide treatments (five triclopyr and fluroxypyr formulations plus an untreated control) and seed addition (and unseeded control) on taxonomic and phylogenetic diversity, and community composition of restored grasslands in three sites over three years. We assessed response of L. cuneata through stem density counts, and response of the plant community through estimates of canopy cover. Herbicide treatments reduced the abundance of the exotic in the first field season leading to a less dispersed community composition compared with untreated controls, with the exotic regaining dominance by the third year. Supplemental seed addition did not provide extra resistance of the native community to reinvasion of the exotic. The communities were phylogenetically over-dispersed, but there was a short-term shift to lower phylogenetic diversity in response to herbicides consistent with a decrease in biotic filtering. Native plant communities in these grassland restorations were resilient to short-term reduction in abundance of a dominant invasive even though it was insufficient to provide an establishment window for native species establishment. [ABSTRACT FROM AUTHOR]