Abstract

AbstractQuestionsTo gain insights into the role of species‐by‐species replacements in cloud forest community structuring, we asked: (1) What are the effects of the spatial distribution of standing individuals on the seed rain, soil seed bank, and sapling density and survival in this cloud forest?; and (2) What is the prevalence of conspecific vs heterospecific replacements in the regeneration of this forest?LocationSanto Tomás Teipan, Oaxaca State, southern Mexico.MethodsIn a 1‐ha cloud forest plot, we assessed seed rain, seed bank, and sapling density and survival of four canopy tree species (Chiranthodendron pentadactylon, Cornus disciflora, Quercus laurina and Oreopanax xalapensis). All standing individuals of these and other tree species (diameter at breast height [DBH] ≥ 2.5 cm) were mapped. We used neighbourhood models to examine the spatial patterns of the three life cycle stages relative to the spatial distribution of adults. The neighbourhood effect was assessed through the Neighbourhood Index, which integrates information on size (DBH) and distance to adults. Data analysis was based on maximum likelihood and model selection procedures.ResultsWe found large between‐species differences regarding the spatial patterns of seeds and saplings. Three species showed evidence for the Janzen–Connell effect operating at the seed (Chiranthodendron pentadactylon and Quercus laurina) or sapling (Oreopanax xalapensis) stage. We also found support for a critical role of specific microsite factors (i.e. niche differentiation) in the regeneration of two species (Chiranthodendron pentadactylon and Cornus disciflora).ConclusionsSeed and sapling distribution patterns suggest the prevalence of heterospecific replacements and that both Janzen–Connell and niche differentiation effects contribute to this pattern. Our results largely support the notion that the prevalence of heterospecific replacements among canopy species promotes species co‐existence in cloud forests.

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