Abstract

Abstract Previous experiments on post‐fire establishment of two obligate seeders and two resprouting species suggested that initial establishment processes differ between wet‐ and dry‐heath habitats. Disturbance, interspecific competition between seedlings and between seedlings and adults, and access for potential predators were manipulated in the field after a fire to identify mechanisms to explain between‐ and witm'n‐habitat species coexistence. When soil surfaces are disturbed or seeds are buried, dry‐heath species can establish in the wet heath. Under natural conditions, however, wet heath is rarely disturbed by animal foragers and lack of safe sites may preclude establishment of dry‐heath species. In contrast, dry heath is often disturbed by ground foragers such as bandicoots and safe sites are plentiful for establishment of all heath species. Nevertheless, while wet‐heath species can establish in dry heath, their seedlings are apparently unable to survive there due to the drier conditions. No evidence for competition among species was detected in either type of habitat during the first 3 years of the experiment, even at elevated seedling densities. Lack of early competition and unsaturated seed‐banks may promote coexistence of species. Seedling predation from vertebrates was low and did not appear to influence patterns of coexistence within or between habitats. In terms of community theory we suggest that several interacting mechanisms are responsible for community structure in heaths after a fire. Chance and microsite disturbance are important during dispersal, while resources are critical during establishment and early survival of seedling populations. In these heath systems where fires burn extensive areas, seed‐banks may be more important in temporal storage of species than patch or spatial storage as a mechanism for maintaining coexistence and plant diversity.

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