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Summary: Savannas cover a significant fraction of the Earth's land surface. In these ecosystems, C3 trees and C4 grasses coexist persistently, but the mechanisms explaining coexistence remain subject to debate. Different quantitative models have been proposed to explain coexistence, but these models make widely contrasting assumptions about which mechanisms are responsible for savanna persistence. Here, we show that no single existing model fully captures all key elements required to explain tree–grass coexistence across savanna rainfall gradients, but many models make important contributions. We show that recent empirical work allows us to combine many existing elements with new ideas to arrive at a synthesis that combines elements of two dominant frameworks: Walter's two‐layer model and demographic bottlenecks. We propose that functional rooting separation is necessary for coexistence and is the crux of the coexistence problem. It is both well‐supported empirically and necessary for tree persistence, given the comprehensive grass superiority for soil moisture acquisition. We argue that eventual tree dominance through shading is precluded by ecohydrological constraints in dry savannas and by fire and herbivores in wet savannas. Strong asymmetric grass–tree competition for soil moisture limits tree growth, exposing trees to persistent demographic bottlenecks. [ABSTRACT FROM AUTHOR]

Freshwater molluscs are hosts for diverse metazoan symbionts. However, apart from the digenean helminths, symbionts of molluscs are underreported worldwide. Therefore, this study focused on the diversity of oligochaetes, leeches, mites, insect larvae and nematodes associated with gastropods and bivalves from Lake Victoria, East Africa.Overall, 1,633 mollusc specimens representing 14 species were sampled from the Kenyan part of the lake. Each host specimen was examined to determine co‐occurrence of symbionts (including digeneans) and other metazoan invertebrates, and their microhabitat preferences on/in the hosts. In addition, prevalence and abundance of symbionts were compared for molluscs obtained from an unpolluted site, and sites that are eutrophic and polluted with heavy metals.In total, 33 species were recovered from the molluscs: six oligochaetes, four insects, two mites, two nematodes, one leech and 18 digeneans. The nematode Daubaylia potomaca, mite Unionicola macani, leech Batracobdelloides sp., oligochaetes Chaetogaster limnaei, Dero digitata, Aulophorus africanus, Allonais paraguayensis and Ophidonais serpentina, and gorgoderid digenean larvae are new records for Lake Victoria. Moreover, the genus Bratislavia (Oligochaeta) is reported for the first time in Africa. Our results show that parasitic mites and leeches were absent from mollusc specimens that harboured chironomids. Likewise, there was no co‐occurrence of C. limnaei, D. potomaca and digeneans, suggesting that antagonistic interactions occur between the symbionts. Although co‐occurrence of mites and digeneans in individual mollusc hosts was common, the symbionts occupied different microhabitats. This study shows that prevalence and intensities of U. macani and C. limnaei, were significantly higher in hosts from the unpolluted site, compared with the polluted sites. What is more, D. potomaca and trichopteran larvae, were recorded only from the unpolluted site. The distribution of the chironomid Kiefferulus chloronatus suggests their preference for sites that are rich in organic matter and their ability to tolerate pollution.Information on antagonistic interactions between symbionts might be applicable in biocontrol, especially of digenean species that have veterinary or medical importance. Finally, this study shows a potential for the use of U. macani, C. limnaei, D. potomaca and insect larvae as discriminators of the quality of aquatic habitats. [ABSTRACT FROM AUTHOR]

Theorists have identified several mechanisms through which species that compete exploitatively for resources could coexist. By contrast, under the current theory, interference competitors could coexist only in rare circumstances. Yet, some types of interference competition, such as interspecific territoriality, are common. This mismatch between theory and nature inspired us to model interference competition in an eco‐evolutionary framework. We based the model on the life cycle of territorial birds and ran simulations to examine whether natural selection could rescue a superior interference competitor from extinction without driving a superior exploitative competitor extinct. We found that coexistence between interference competitors can occur over a wide range of ecologically plausible scenarios, and up to the highest levels of resource overlap. An important caveat is that coexistence requires the species to co‐evolve. Reductions in population size and levels of genetic variation could destabilise coexistence between interference competitors, and thereby increase extinction rates over current estimates. [ABSTRACT FROM AUTHOR]

Belowground plant traits play important roles in plant diversity loss driven by atmospheric nitrogen (N) deposition. However, the way N enrichment shapes plant microhabitats by patterning belowground traits and finally determines aboveground responses is poorly understood. Here, we investigated the rhizosheath trait of 74 plant species in seven N‐addition simulation experiments across multiple grassland ecosystems in China. We found that rhizosheath formation differed among plant functional groups and contributed to changes in plant community composition induced by N enrichment. Compared with forb species, grass and sedge species exhibited distinct rhizosheaths; moreover, grasses and sedges expanded their rhizosheaths with increasing N‐addition rate which allowed them to colonize belowground habitats. Grasses also shaped a different microenvironment around their roots compared with forbs by affecting the physicochemical, biological, and stress‐avoiding properties of their rhizosphere soil. Rhizosheaths act as a "biofilm‐like shield" by the accumulation of protective compounds, carboxylic anions and polysaccharides, determined by both plants and microorganisms. This enhanced the tolerance of grasses and sedges to stresses induced by N enrichment. Conversely, forbs lacked the protective rhizosheaths which renders their roots sensitive to stresses induced by N enrichment, thus contributing to their disappearance under N‐enriched conditions. This study uncovers the processes by which belowground facilitation and trait matching affect aboveground responses under conditions of N enrichment, which advances our mechanistic understanding of the contribution of competitive exclusion and environmental tolerance to plant diversity loss caused by N deposition. [ABSTRACT FROM AUTHOR]

The prediction that higher biodiversity leads to denser niche packing and thus higher community resistance to invasion has long been studied, with species richness as the predominant measure of diversity. However, few studies have explored how phylogenetic and functional diversity, which should represent niche space more faithfully than taxonomic diversity, influence community invasibility, especially across longer time frames and over larger spatial extents.We used a 15‐year, 150‐site grassland dataset to assess relationships between invasive plant abundance and phylogenetic, functional and taxonomic diversity of recipient native plant communities. We analysed the dataset both pooled across all surveys and longitudinally, leveraging time‐series data to compare observed patterns in invasion with those predicted by two community assembly processes: biotic resistance and competitive exclusion. We expected more phylogenetically and functionally diverse communities to exhibit greater resistance to invasion.With the pooled dataset, we found support for the long‐standing observation that communities with more native species have lower abundance of invasive species, and a more novel finding that more phylogenetically diverse communities had higher abundance of invasive species. We found no influence of aggregate (multivariate) functional diversity on invasion, but assemblages with taller plants, lower variability in plant height and lower seed mass were less invaded. Viewed longitudinally, the phylogenetic diversity relationship was reversed: the most phylogenetically diverse communities were most resistant to invasion. This apparent discrepancy suggests invasion dynamics are influenced by both site attributes and biotic resistance and emphasizes the value in studying invasion across time.Synthesis. Our results provide insight into the nuances of the diversity–invasibility relationship: invasion dynamics differed for different dimensions of diversity and depending on whether the relationship was evaluated longitudinally. Our findings highlight the limitations of using single time‐point 'snapshots' of community composition to infer invasion mechanisms. [ABSTRACT FROM AUTHOR]

Competitive exclusion can be classified as deterministic or as historically contingent. While competitive exclusion is common in nature, it has remained unclear when multispecies communities formed by more than two species should be dominated by deterministic or contingent exclusion. Here, we take a fully parameterised model of an empirical competitive system between invasive annual and native perennial plant species to explain both the emergence and sources of competitive exclusion in multispecies communities. Using a structural approach to understand the range of parameters promoting deterministic and contingent exclusions, we then find heuristic theoretical support for the following three general conclusions. First, we find that the life‐history of perennial species increases the probability of observing contingent exclusion by increasing their effective intrinsic growth rates. Second, we find that the probability of observing contingent exclusion increases with weaker intraspecific competition, and not with the level of hierarchical competition. Third, we find a shift from contingent exclusion to deterministic exclusion with increasing numbers of competing species. Our work provides a heuristic framework to increase our understanding about the predictability of species persistence within multispecies communities. [ABSTRACT FROM AUTHOR]

Evaluating the mechanisms that drive plant invasions in grassland ecosystems can provide insight into subtle, yet critical, drivers of ecosystem function. Common hypotheses for invader success are that (1) an invader's physiology may allow better use of resources and competitively exclude resident natives; (2) the lack of invader‐specific herbivores and diseases may result in increased growth and competitive advantage over natives; (3) invaders may bring pathogens or herbivores that negatively impact native plants directly; (4) the invader may be able to establish earlier or later than natives, giving it a priority effect or phenological niche separation; (5) the invader may produce more seeds, and propagule pressure may allow it to eventually dominate; and (6) once the invader occurs on a site, its plant detritus or litter can offer a legacy effect advantage. Yet, a widely neglected aspect of invasion is that invaders may prime the conditions in places other than where they are currently established, giving them a pioneer effect advantage. These pioneer effects can come from plant materials that move from invaded to uninvaded areas through three pathways—pollen, litter, seeds, and their associated microbiomes—each of which can favor the invader directly or indirectly. In turn, unsuccessful cohorts of seedlings can change the biotic community through root exudates as well as any biotic load they bring with them, along with taking up nutrients and potentially subverting the litter decay cycle. When seedlings of invaders occur at times when the native species have evolved not to germinate, site priming impacts may increase or accelerate. We propose that monitoring of uninvaded areas adjacent to invaded areas is needed to assess the emerging significance of pioneer effects and site priming in advancing plant invasions, especially in grassland systems worldwide. [ABSTRACT FROM AUTHOR]