island biogeography · the theory of island biogeography: on an ecological scale, the equilibrium...
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Island Biogeography
On an evolutionary scale, the equilibrium number of species
results from the balance between rates of extinction and speciation
Island biogeography: the study of the abundance and diversity of
species on islands, or “island like habitats (mountain tops, ponds,
forest patches…)
The theory of island
biogeography:
On an ecological scale, the
equilibrium number of species
results from the balance
between rates of colonization
and local extinction (depends
on the # of species present)
Evidence for species equilibrium
1. Survey of arthropods on small mangrove islands at different
distances off Florida (determined species diversity)
2. Fumigated islands to kill all species
3. Re-censused islands for 2 years to look at colonization
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Evidence for species equilibrium
1. The number of species
accumulates quickly and
then tapers off
2. The equilibrium number of
species is similar to the
original values for each
island
3. The species are turning
over (changing) although
the number of species
stays the same
4. Why?
Num
ber
of specie
s p
resent
Predefaunation surveys
The equilibrium theory of island biogeography
Rates of immigration by new species will decline as the number of species
already there increases (e.g. it is increasingly unlikely that a new colonist
represents a new species for the island)
Rates of extinction increase as the number of species on the island increases
a) more species to go extinct
b) competition and predation are likely to increase with increasing diversity
The species
equilibrium will be
reached when rates
of immigration
match extinction -
species composition
may change, but the
number will stay the
same
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The equilibrium theory of island biogeography
All mangrove islands were
small, but the ones closest
to the mainland had the
highest equilibrium number
of species
Why would distance
change the equilibrium
number of species?
The equilibrium theory of island biogeography
Immigration and extinction curves vary as a function of island size
and distance
Far islands will have slower
colonization rates
Small islands will have higher
extinction rates
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The equilibrium theory of island biogeography
Immigration and extinction curves vary as a function of island size
and distance
small
large
S S S S
Tests of the equilibrium theory of island biogeography
Islands closer to Australia
(the mainland source) have
more species
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Tests of the equilibrium theory of island biogeography
Islands in the East
Indies:
bigger islands have
more species
Wooded habitats:
larger fragments have
more species
Application of island biogeography theory to conservation
Habitats are becoming more and more fragmented (like islands)
Can we manage so as to maximize diversity within these fragments?
Park design
assumptions:
a) immigration will be
minimal since unprotected areas
surrounding parks will be destroyed
b) Species equilibrium
numbers will be driven by
extinction
conclusions:
a) small parks will have higher extinction rates
minimal
immigration
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Application of island biogeography theory to conservation
Extinction rates in US National parks
8520,736 0Kootenay-Banff-
Jasper-Yoho
8410,328 4Grand Teton-
Yellowstone
764,93118Grand Canyon
824,627 7Glacier-Waterton Lakes
753,628 6Olympic
943,38923Sequoia-Kings
Canyon
942,08325Yosemite
691,04931Rocky Mountain
8597632Mount Rainier
4371226Manning
Provincial
8264131Crater Lake
7742643Lassen Volcanic
6114436Bryce Canyon
Age
(years)
Area
(km2)
% loss of
mammals
Park/Park
Assemblage
Small parks have :
a) higher rates of extinction
b) species with low populations are most
vulnerable (predators, jaguars, wolves…)
c) Extinction of predators can alter diversity
of prey
Habitat fragmentation Roads bring colonists who clear the
land (Rondonia, Amazonian Brazil)
Roads reduce biodiversity by:
a) making barriers to dispersal (many
organisms wont cross a road or even
go near the edge of their habitat
b) increasing colonization by weedy
species and invasives
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Park design : how can we minimize loss?
better worse why?
1. Size extinction less
2. Number Immigration more
3. Distance Immigration more
4. Connectivity Immigration more
(corridors)
Effects of connectivity (corridors)
Plant species diversity for patches of long
leaf pine habitat that were unconnected or
connected to other patches via corridors
Effects of connectivity (corridors)
Plant species diversity for patches of long
leaf pine habitat that were unconnected or
connected to other patches via corridors
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Effects of connectivity (corridors)
unconnected
connected
At the beginning of the
experiment, plants were
removed and recolonized
over time
But no difference for exotic species
(yellow bars)
Connected patches had higher
diversity of native species (green bars)
Park design : how can we minimize loss?
better worse why?
1. Size extinction less
2. Number Immigration more
3. Distance Immigration more
4. Connectivity Immigration more
(corridors)
4. Shape Extinction less with
less edge effects
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Edge effects: size and shape
Effects of shape and amount of edge habitat
Plant species diversity for patches that had lots of edges (winged) had lower
species diversity than those with less edge effects (rectangular)
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Minimum critical size project, Amazon, Brazil (size and edge effects)
In partnership with cattle ranchers
and loggers, created habitat
islands of different sizes (1-100ha)
and monitored changes in diversity
Smaller fragments lost diversity
faster than bigger ones, but
diversity in all fragment sizes
declined
Edge effects were enormous
(changes in the abiotic
environment near edges, such as
increased light, drought stress,
wind…) caused higher mortality
and species loss
Characteristics of species that make them vulnerable to extinction
rarity
dispersal
ability
diet
specialization
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Characteristics of species that make them vulnerable to extinction
trophic
status
life span
r (reproductive
ability)
Conservation biology
Understanding how to
manage ecosystems to
maximize preservation of
biodiversity