remain
within the population, and the average heterozygosis and gene diversity (or
"expected heterozygosis") relative to the starting levels.
VORTEX
also monitors the
inbreeding coefficients of each animal, and can reduce the juvenile survival of
inbred animals to model the effects of inbreeding depression.
VORTEX
is an individual-based model. That is,
VORTEX
creates a representation of
each animal in its memory and follows the fate of the animal through each year of
its lifetime.
VORTEX
keeps track of the sex, age, and parentage of each animal.
Demographic events (birth, sex determination, mating, dispersal, and death) are
modeled by determining for each animal in each year of the simulation whether
any of the events occur. (See figure below.) Events occur according to the specified
age and sex-specific probabilities. Demographic stochastic is therefore a
consequence of the uncertainty regarding whether each demographic event occurs
for any given animal.
VORTEX Simulation Model Timeline
Breed Immigrate Supplement
^- Age 1 Year
^————^ Census
Death Emigrate Harvest Carrying
Capacity Truncation
Events listed above the timeline increase N, while
events listed below the timeline
decrease N.
VORTEX
requires a lot of population-specific data. For example, the user must
specify the amount of annual variation in each demographic rate caused by
fluctuations in the environment. In addition, the frequency of each type of
catastrophe (drought, flood, epidemic disease) and the effects of the catastrophes on
survival and reproduction must be specified. Rates of migration (dispersal) between
each pair of local populations must be specified. Because
VORTEX
requires
specification of many biological parameters, it is not necessarily a good model for
the examination of population dynamics that would result from some generalized
life history. It is most usefully applied to the analysis of a specific population in a
specific environment.
Further information on
VORTEX
is available in Lacy (1993a) and Miller and
Lacy (1999). Dealing with Uncertainty
It is important to recognize that uncertainty regarding the biological parameters of a
population and its consequent fate occurs at several levels and for independent
reasons. uncertainty can occur because the parameters have never been measured
on the population. Uncertainty can occur because limited field data have yielded
estimates with potentially large sampling error. Uncertainty can occur because
independent studies have generated discordant estimates. Uncertainty can occur
because environmental conditions or population status have been changing over
time, and field surveys were conducted during periods which may not be
representative of long-term averages. Uncertainty can occur because the
environment will change in the future, so that measurements made in the past may
not accurately predict future conditions.
Sensitivity testing is necessary to determine the extent to which uncertainty in input
parameters results in uncertainty regarding the future fate of the pronghorn
population. If altemative plausible parameter values result in divergent predictions
for the population, then it is important to try to resolve the uncertainty with better
data. Sensitivity of population dynamics to certain parameters also indicates that
those parameters describe factors that could be critical determinants of population
viability. Such factors are therefore good candidates for efficient management
actions designed to ensure the persistence of the population.
The above kinds of uncertainty should be distinguished from several more sources
of uncertainty about the future of the population. Even if long-term average
demographic rates are known with precision, variation over time caused by
fluctuating environmental conditions will cause uncertainty in the fate of the
population at any given time in the future. Such environmental variation should be
incorporated into the model used to assess population dynamics, and will generate a
range of possible outcomes (perhaps represented as a mean and standard deviation)
from the model. In addition, most biological processes are inherently stochastic,
having a random component. The stochastic or probabilistic nature of survival, sex
determination, transmission of genes, acquisition of mates, reproduction, and other
processes preclude exact determination of the future state of a population. Such
demographic stochastic should also be incorporated into a population model,
because such variability both increases our uncertainty about the future and can
also change the expected or mean outcome relative to that which would result if
there were no such variation. Finally, there is "uncertainty" which represents the
alterative actions or interventions which might be pursued as a management
strategy. The likely effectiveness of such management options can be explored by
testing alterative scenarios in the model of population dynamics, in much the same
way that Sensitivity testing is used to explore the effects of uncertain biological
parameters.
Results
Results reported for each scenario include:
Deterministic r — The deterministic population growth rate, a projection of the
mean rate of growth of the population expected from the average birth and death
rates. Impacts of harvest, inbreeding, and density dependence are not considered in
the calculation. When r == O, a population with no growth is expected; r < O
indicates population decline; r > O indicates long-term population growth. The
value of r is approximately the rate of growth or decline per year.
The deterministic growth rate is the average population growth expected if
the population is so large as to be unaffected by stochastic, random processes. The
deterministic growth rate will correctly predict future population growth if: the
population is presently at a stable age distribution; birth and death rates remain
constant over time and space (i. e., not only do the probabilities remain constant,
but the actual number of births and deaths each year match the expected values);
there is no inbreeding depression; there is never a limitation of mates preventing
some females from breeding; and there is no density dependence in birth or death
rates, such as a Allee effects or a habitat "carrying capacity" limiting population
growth. Because some or all of these assumptions are usually violated, the average
population growth of real populations (and stochastically simulated ones) will
usually be less than the deterministic growth rate.