Predominant frameworks for understanding plant ecology have an aboveground bias that neglects soil micro-organisms. This is inconsistent with recent work illustrating the importance of soil microbes in terrestrial ecology. Microbial effects have been incorporated into plant community dynamics using ideas of niche modification and plant-soil community feedbacks. Here, we expand and integrate qualitative conceptual models of plant niche and feedback to explore implications of microbial interactions for understanding plant community ecology. At the same time we review the empirical evidence for these processes. We also consider common mycorrhizal networks, and suggest these are best interpreted within the feedback framework. Finally, we apply our integrated model of niche and feedback to understanding plant coexistence, monodominance, and invasion ecology. Plant Community Ecology Models Overlook Soil Microbial InteractionsCommunities of competing plant species are stabilized by stronger negative intraspecific interactions relative to interspecific interactions [1]. Traditionally, strong negative intraspecific interactions have been thought to result from high resource use overlap [2,3]. These models of resource partitioning have been developed into an influential framework for understanding plant community dynamics, but the empirical evidence supporting them is still limited. Plant competition experiments have not shown unequivocally that the strength of intraspecific competition exceeds that of interspecific competition [4] and the empirical evidence of coexistence of competing plant species through resource partitioning remains mixed [5][6][7].In response to the perceived limitations of explaining species coexistence through resource partitioning, plant ecologists have increasingly looked for mechanisms that might limit the negative effect of competition on inferior competitors and thereby slow competitive exclusion. For instance, competition-colonization tradeoffs can allow inferior competitors to persist through their greater likelihood of establishing in transient gaps in vegetation [8].© 2010 Elsevier Ltd. All rights reserved.Corresponding author: Bever, J. D. (jbever@indiana.edu). Publisher's Disclaimer: This is a PDF file of an unedited manuscript that has been accepted for publication. As a service to our customers we are providing this early version of the manuscript. The manuscript will undergo copyediting, typesetting, and review of the resulting proof before it is published in its final citable form. Please note that during the production process errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain. Current theory neglects the less visible organisms in the soil and this might be one reason for the limited success in finding a mechanism to explain the coexistence of competing plant species. The presence and composition of soil microbial communities has been shown to have large impacts on plant-plant interactions [14][15][16] and con...

Arbuscular mycorrhizal (AM) symbioses are formed by approximately 80% of vascular plant species in all major terrestrial biomes. In consequence an understanding of their functions is critical in any study of sustainable agricultural or natural ecosystems. Here we discuss the implications of recent results and ideas on AM symbioses that are likely to be of particular significance for plants dealing with abiotic stresses such as nutrient deficiency and especially water stress. In order to ensure balanced coverage, we also include brief consideration of the ways in which AM fungi may influence soil structure, carbon deposition in soil and interactions with the soil microbial and animal populations, as well as plantplant competition. These interlinked outcomes of AM symbioses go well beyond effects in increasing nutrient uptake that are commonly discussed and all require to be taken into consideration in future work designed to understand the complex and multifaceted responses of plants to abiotic and biotic stresses in agricultural and natural environments.

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We performed a field experiment to test whether the presence of litter produced by the dominant species in the first successional year affects the plant community structure in the following year. We removed the litter of Setaria faberii (the first-year dominant) in midfall, early spring, mid-spring, or late spring. Both the fall and early spring removal increased the biomass of Erigeron annuus, which became dominant, and reduced the biomass of S. faberii. In the fall-removal treatment more plants of E. annuus flowered, while early spring removal increased the biomass of rosettes (non-flowering individuals) at the end of the growing season. In the other treatments and in the control S. faberii retained dominance, but its biomass was the highest in mid-spring removal plots. The removal of litter of S. faberii in the fall and in early spring allowed E. annuus to pre-empt the site and dominate the community. When litter was not removed, it strongly hindered the growth of E. annuus, favoring S. faberii. These results highlight the importance of litter as a historical factor linking interactions across successive generations, and controlling the community structure.

Aims To study the relationship between changes in soil properties and plant community characters produced by grazing in a meadow steppe grassland and the composition and diversity of spore-producing arbuscular mycorrhizal fungi (AMF). Methods A field survey was carried out in a meadow steppe area with a gradient of grazing pressures (a site with four grazing intensities and a reserve closed to grazing). The AMF community composition (characterized by spore abundance) and diversity, the vegetation characters and soil properties were measured, and root colonization by AMF was assessed. Results AMF diversity (richness and evenness) was higher under light to moderate grazing pressure and declined under intense grazing pressures. Results of multiple regressions indicated that soil electrical conductivity was highly associated with AMF diversity. The variation in AMF diversity was partially associated to the density of tillers of the dominant grass (Leymus chinensis), the above and below-ground biomass and the richness of the plant community. Conclusions We propose that the relationship between plants and AMF is altered by environmental stress (salinity) which is in turn influenced by animal grazing. Direct and indirect interactions between vegetation, soil properties, and AMF community need to be elucidated to improve our ability to manage these communities.