Samoa. Wilson bundled the species into three
stages. Stage 1 species are those that dominate in the
marginal habitats: open lowland forest, grassland,
and littoral habitats (Fig. 9.2). They have greater
ecological amplitudes than the other species, as
they also occur in other habitats. They tend to be
trail-making ants, nesting in the soil. Stage 1 species
typically show a continuous distribution with no
tendency to break into locally distinct races. Stage 2
of the process sees ants ‘returning’ to the dominant
vegetation types, of interior and montane forest,
within which they are more likely to be found
nesting in logs or similar habitats. If they succeed in
adapting to the inner rain forests they eventually
differentiate to species level within Melanesia,
forming superspecies or species groups. As they
differentiate, they are liable to exhibit reduced gene
flow across their populations. Stage 3 species occupy
similar habitats to those of stage 2, but evolution has
now proceeded to the point where the species group
is centred on Melanesia and lacks close relatives in
Asia. This may be, in part, a function of change in
Melanesia, and in part of the contraction in the
group remaining in Asia. Progress within the cycle
is thus marked by a general pattern of restriction of
species to narrower ranges of environments within
the island interiors. Meanwhile, these lineages have
been replaced by a new wave of colonists occupy-
ing the beach and disturbed habitats.
Pivotal to this inferred evolutionary system is
that the process is driven by the continuing (albeit
infrequent) arrival of new colonist species. Their
colonization initiates interactions that push earlier
colonists from the open habitats. This is because the
earlier colonists are likely to have become more
generalized in the time since they themselves colo-
nized, as they spread into additional habitats, thus
losing competitive ability in their original habitats
(Brown and Gibson 1983). This model is persuasive
in that it provides answers to some seemingly
puzzling phenomena. For example, it helps explain
why species inhabiting interior forests of the
oceanic islands are more closely related to species
of disturbed habitats on New Guinea, than to those
species that have similar niches and which occur in
mature forest on New Guinea. Although largely a
unidirectional model, it was suggested that some
lineages did find a way out of their alleyway,
perhaps temporarily. Occasionally, a stage 3 species
may readapt to the marginal habitats, becoming
210 EMERGENT MODELS OF ISLAND EVOLUTION
Per cent
Increasing faunal size
Littoral Savanna Monsoon
forest
Lowland
rain forest
(marginal)
Lowland
rain forest
(interior)
Montane
rain forest
100
0
50
Figure 9.1Proportions of ponerine ant species in different habitats, as a function of their geographical distribution. The marginal habitats, to
the left, contain both smaller absolute numbers of species and higher percentages of widespread species. Dark columns, species widespread in
Melanesia; stippled columns, species restricted to single archipelagos in Melanesia but belonging to groups centred in Asia or Australia; blank
columns, species restricted to single archipelagos and belonging to Melanesia-centred species groups. (Redrawn from Wilson 1959.)