Introduction

The last decade has seen rapid growth in research dedicated to seedling ecology (Kitajima, 2007). This reflects an increased recognition of the importance of variation in seedling survival in determining patterns of adult abundance and distribution. Many seedling studies have grown out of larger programs investigating community dynamics in natural systems. Nonetheless, the results of these studies are often directly relevant to the management and conservation of human-altered ecosystems where changing environmental conditions and altered biotic interactions can directly affect seedling recruitment success. In extreme cases, human-mediated disturbances may be sufficient to invoke community-wide recruitment failure, leading to stalled succession or to shifts in vegetation type. Disturbance effects, however, can also have more subtle effects on recruitment success, resulting in changes in forest composition that may take decades or more to become apparent (Dirzo & Miranda, 1990).

Seedlings are particularly vulnerable to disturbance. Most species have no equivalent of the dormancy that facilitates seed survival through periods with adverse environmental conditions. Instead, alterations in light or soil moisture availability often impact seedlings first because their small leaf area and shallow rooting depth limit their ability to integrate resource capture over space. Similarly, only a small fraction of tree species have seed reserves that persist for more than a few months after germination, leaving seedlings vulnerable to damage and to temporal fluctuations in resource supply (Kitajima, 1996a; Harms & Dalling, 1997). Seedlings are also especially susceptible to natural enemies and fire.