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metapopulation
each habitat patch contains a different sub-population of the species and the sub-populations are linked by occasional dispersal
metapopulations are also referred to as
a population of sub-populations
what are the different types of meta-populations
shifting-mosaic and core-satellite
shifting-mosaic metapopulation
no sub-population is permanent, but the metapopulation persists because establishment of new sub-pops balances extinction of existing sub-pops
example given for shifting-mosiac metapopulations
desert mountain sheep
shifting-mosaic metapopulations have lots of
turnover
core-satellite metapopulation
one or more sub-populations is permanent and maintains smaller, more ephemeral sub-
populations through dispersal
core-satellite metapopulation example
bay checker butterfly
rescue effect
in a core-satellite metapopulation, the satellites persist because they are being
maintained by dispersal from the core; without the regular input of individuals from the core, the satellites would go extinct
first reason why satellite sub-pops may be ephemeral
they occur on small patches of high quality habitat with low carrying capacity. If the sub-population is always small then it is vulnerable to the perils of small population size
second reason why satellite sub-pops may be ephemeral
They occur on patches of low quality habitat that can support positive population growth in only a minority of years; local extinction is inevitable regardless of chance events
sink sub population refers to the
second reason why satellite sub-pops may be ephemeral
first conservation implication of metapopulation structure
For a core-satellite metapopulation, preserving the core sub-
population should be top priority
second conservation implication of metapopulation structure
For a shifting-mosaic metapopulation, preserving unoccupied but suitable habitat is essential because current sub-populations are ephemeral
third conservation implication of metapopulation structure
Dispersal is a critical process, so intervening habitat between sub-populations must be maintained to allow dispersal of the species
example of third conservation implication of metapopulation structure
removing fences for sheep, limiting off-road vehicles, no raising domestic sheep
fourth conservation implication of metepopulation strucuture
Metapopulation dynamics provides a framework for understanding functioning of populations in a fragmented landscape
What is the most likely result of the interaction between con-specific individuals in a fragmented landscape?
reduces dispersal but won’t eliminate entirely
environmental stochasticity
random variation in parameters that measure habitat quality such as climate, nutrients, pollutants, interactions with other species
preserves that have subpopulations close together maximizes
dispersal
downside of preserves that have metepopulations close together
subjected to same environmental variation like drought or natural disasters
it is important to preserve examples of
most different habitats for one species because they respond differently to environmental variation ex. more vs less resistant to drought
why is a realistic population growth model not the most efficient
lots of data and parameters; expensive and time consuming
population growth models need a balance between
simplicity and realism
N=
population size
N0=
initial population size
N1
population size one time unit in the future
N2018
population size in the year 2018
t=
time in years
Nt=
population size at some unspecified time
Nt+1=
population size one time unit beyond t
delta N=
change in population size, expressed as number of individuals gained or lost
net rate of change in population size
delta N/delta t
per capita rate of change in population size
delta N/delta N0/delta t
per capita rate of change definition
number of individuals added or lost from the population per individual in the population at the start per unit time
predicting population size one time unit in the future
Nt+1= Nt+(delta N/delta t) OR Nt+1=Nt+(1+delta N/N0/delta t)
finite range of population increase
lambda=(1+delta N/N0/delta t)
lambda or finite range of population increase can also be calculated as
Nt+1/Nt
if lambda is greater than 1
population increasing
if lambda is 1
population stable
if lambda is less than 1
population decreasing
if r is greater than 0
population increasing
if r is 0
population stable
if r is less than 0
population decreasing
exponential population growth
population growth or decline at a constant proportional rate over time; constant value for finite rate of population increase
discrete-time exponential growth model
Nt=N0lambda^t
exponential population growth if lambda=1.2 per capita growth rate =
0.2
exponential population decline if lambda=0.8 per capita growth rate =
-0.2
continuous time exponential growth model
dN/dt=rN
dN/dt=
rate of change in a population size over a very small time interval; the slope of a line tangent to the population growth curve at one time point
if you want to predict continious time population size in the future
Nt=Noe^rt
r=
intrinsic rate of population increase
ln lambda=
r
e^r=
lambda
Nt=N0e^rt equation is not
discrete; time occurring in chunks; lambda
continuous time population growth time does not occur in
chunks; continuous change over time; r
first reason why it is unrealistic to assume a constant per capita population growth rate through time
environment in which the species exists changes in time-environmental stochasticity
second reason why it is unrealistic to assume a constant per capita population growth rate through time
density of the population will affect per capita population growth rate
would you expect the per capita population growth rate to slow or increase as the population becomes more dense? why?
slow; resources become more limited with increased population size
third reason why it is unrealistic to assume a constant per capita population growth rate through time
density of populations of species with which our species interacts change through time