Territorial group size in Australian magpies (Gymnorhina tibicen) ranges from monogamous pairs to groups of more than 20 individuals. It has been hypothesized that large territorial groups result from the retention of juveniles after a breeding eort. If this is true, local populations consisting of large groups are likely to exhibit the most genetic structure, because over time similar genotypes will tend to be con®ned to limited areas if juveniles are predominantly philopatric. The objective of the present study was to test this hypothesis using allozyme and mitochondrial DNA data to provide indirect estimates of regional gene¯ow (derived from hierarchical population subdivision analyses). These data were used in combination with estimates of group size to infer patterns of dispersal among magpie populations across mainland Australia. Territorial groups were signi®cantly larger in the south-west compared to three eastern regions. Although inferred levels of gene¯ow were substantial for all four regions, a striking pattern emerged from both sets of genetic data: more dierentiation was evident among populations in the south-western region than in any eastern region. We conclude that levels of juvenile dispersal in¯uence group size in G. tibicen, because in the south-western region where groups were largest, populations were most genetically dierentiated. Our results suggest that contrasting population genetic structures may develop within a single species as a result of dierences in social system. Keywords: allozymes, Australian magpie, bird, dispersal, gene¯ow, mitochondrial DNA.
IntroductionA characteristic feature of most vertebrates is the permanent movement made by ospring from the site of their birth to their ®rst breeding locality (natal dispersal) and, less conspicuously, subsequent movement from one breeding site to another either within or between breeding seasons (breeding dispersal) (Greenwood et al., 1979).Ecologists have debated for many years why animals leave the relative safety of where they were born in search of a new home they may not even ®nd (Dobson et al., 1998). Costs of such behaviour may include a greater risk of mortality and a lack of knowledge of the new site that may make it more dicult to ®nd food, mates and nesting sites (Fleischer et al., 1984). There are also potential diculties associated with entering established sites and sequestering a new territory (Myers, 1974). On the other hand, several bene®ts may accrue to successful dispersers thus favouring the evolutionary maintenance of dispersal behaviour, e.g. better access to environmental resources such as food and social resources such as mates (Dobson et al., 1998), avoidance of inbreeding depression (Koenig & Pitelka, 1979) and lower exposure to predators and disease (Stenseth & Lidicker, 1992). Overall therefore, the consequences of dispersal can range from premature death without reproducing, to discovery and exploitation of a highquality habitat patch with an ideal mate (Gadgil, 1971).Provided that a disperser reproduc...