We summarize some of the population-dynamic consequences of the mosaic
structure of plant populations for the evolution of seed dispersal. A
fairly elaborated set of theoretical ideas exist regarding the evolut
ion of dispersal and we have synthesized some of them in an attempt to
make them more accessible to field ecologists. We consider the relati
onship of these general theoretical ideas to our understanding of frui
t and seed dispersal. We develop three related models to describe the
similarities and differences in how dispersal functions for risk reduc
tion (bet hedging), escaping the negative consequences of crowding, an
d escaping high concentrations of relatives. We also briefly discuss d
irected dispersal as a fourth population-dynamic aspect of dispersal.
Dispersal can have a risk-reducing function only when there is global
(metapopulation) temporal variance in success. Dispersal to escape the
negative consequences of crowding requires only spatial and local tem
poral environmental variation. Dispersal for escaping high concentrati
ons of relatives requires no environmental variation, but does require
genetic population structure. Directed dispersal, defined as non-rand
om into particular patch types contingent on the expectation of local
success, is always valuable when possible and represents an advantage
independent the others which can occur with random dispersal. In an ef
fort to accommodate for the differences between simple mathematical mo
dels and the behavior of complex natural fruit and seed dispersal syst
ems we have discussed the following issues: actual patterns of patch s
tructure and dispersal distance; the implications of plant cosexuality
, perenniality, and allocation costs of dispersal structures; and the
impact of the detailed nature of density dependence, breeding systems,
and genetic structure. We briefly compare the population-dynamic func
tions of dispersal presented here with the widely cited functions of c
olonization, escape, and directed dispersal. Finally, we suggest how t
he theoretical models can be used with field data to estimate the fitn
ess consequences of dispersal.