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Before we can discuss the effects of fragmentation, we must identify
the species likely to be affected.2 That means identifying species in
which fragmentation will alter
- the distribution of populations,
- the migration rates among populations, or
- the sizes of local populations.
Let's start with the last one first. For animals, the ones most
severely affected are (obviously) those with large home ranges,
because we expect these species to be entirely lost from small
fragments.
- ivory-billed woodpeckers: ca. 7km
per breeding pair
- European goshawk: home range of 30-50km
- male mountain lion (puma): home range of
400km
Suppose that 50 males are needed for a population to have a
reasonable chance of persistence for a couple of centuries. This
would require an area of about 20,000km
, which is roughly
equivalent to the area of Connecticut, Rhode Island, and Cape Cod
combined. Fortunately, puma are learning to live in close proximity
to development, so completely undeveloped habitat doesn't appear to
be necessary to conserve them. Some of the habitat they use can be
moderately altered, as in south Florida or southern
California. You see occasional news reports of joggers being
attacked by puma in southern California, and I've had people tell me
that attacks also occur occasionally on trails near Boulder,
Colorado.
- Forest birds--size of area needed for 50% probability of
occurrence [7]
- Great Crested Flycatcher: 0.3ha (a circle about 60m in diameter)
- Cerulean Warbler: 1000ha (a circle about 3.5km in diameter)
Consequence: species composition of small fragments will differ from
that of large fragments. The species remaining in small fragments will
not be a random subset of those originally present. Species with large
area requirements will be preferentially lost.
Some years ago Deborah Rabinowitz [6] developed a
typology of rarity that is both interesting and useful in thinking
about the possible impacts
of fragmentation (Table 1).
Table 1:
Rabinowitz' typology of rarity
| |
Geographic range |
| |
Large |
Small |
| |
Habitat specificity |
Habitat specificity |
| Local population size |
Wide |
Narrow |
Wide |
Narrow |
| Large |
locally abundant, large range, several habitats |
locally abundant, large range, specific habitat |
locally abundant, restricted range, several habitats |
locally abundant, restricted range, specific habitat |
| Small |
locally sparse, large range, several habitats |
locally sparse, large range, specific habitat |
locally sparse, restricted range, several habitats |
locally sparse, restricted range, specific habitat |
|
Notice that Rabinowitz identifies three axes of rarity:
- limited geographic range,
- specific habitat requirements, and
- low population density.
Plants (or animals) that are rare in either of the first two senses
seem unlikely to be greatly affected by habitat fragmentation, except
to the extent that habitat fragmentation leaves them outside a
fragment. To put it another way, they will be affected by habitat destruction, but habitat fragmentation may have little impact
on either the migration rate among populations or the sizes of
local populations.3
Furthermore, not all plants or animals that are widely distributed
will suffer the effects of fragmentation. Those that are patchily
distributed are already fragmented. Unless fragmentation
disrupts patterns of migration among the populations that remain, it
will have fewer effects than it will on those that are
continuously distributed.
Think about what this means, though. The plants4 that are most likely to be affected by habitat
fragmentation:
- are broadly and continuously distributed,
- have relatively non-specific habitat requirements, and
- are numerically abundant almost everywhere they occur.
These are roughly the characteristics we associate with plant species
regarded as ecosystem dominants: douglas fir and hemlock in the
Pacific northwest, mixed hardwoods in the Northeast. In short,
whatever the effects of fragmentation are, they may be exhibited in a
minority of species, but that minority of species will be the ones
that have the largest impact on the structure and function of
ecosystems in which they occur.
Next: Dynamics and impacts of
Up: Habitat fragmentation
Previous: Introduction
Kent Holsinger
2009-11-03