Deer/Panther Model: A Simulation Model for Florida
Panthers and White-tailed Deer in the Everglades and Big Cypress
Landscapes
ATLSS Deer/Panther model development was deferred while extensive
scenario evaluations were being produced during 1998 and 1999
for the Central and Southern Florida
Comprehensive Study Review (Restudy). Model development has now resumed,
and efforts are ongoing to enhance the realism of the model and
expand the model area to include areas to the north and west of Big
Cypress National Preserve (BCNP).
The Deer/Panther model was designed to be used as a management and
evaluation tool to analyze the relative effects of alternative water
management scenarios on long-term population dynamics of the Florida
panthers and their primary prey species, white-tailed deer. Originally
conceived as one component of a group of interconnected ATLSS models
and driven by an improved and expanded SFWMD Hydrology Model, the
model's projected functionality has been somewhat compromised by the necessary
modifications of original plans. These modifications resulted in an
indefinite delay in the planned provision of expanded hydrology inputs
from the District and postponement of development of a vegetation
succession model. A description of the Deer/Panther model in early
development was presented at the Florida Panther Conference in Ft. Myers
in November 1994 (Comiskey et al. 1997).
A management decision made as part of ongoing panther recovery efforts has
also impacted model development. Eight females of the closely related
Texas subspecies (Puma concolor stanleyana) were introduced into South
Florida population (Puma concolor coryi) in 1995 to enhance genetic
variability of the inbred Florida panthers. The habitat use patterns,
interactions and significant reproductive contributions of these
panthers and their offspring, now estimated to make up about half of
the entire South Florida panther population, has necessitated
reevaluation and reformulation of panther behavior rules for the
model.
The following efforts have been undertaken to make Deer/Panther
simulations more realistic and computationally efficient:
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Analyses of radio telemetry data and a review of published literature
about panthers in South Florida led to the realization that panther
population dynamics cannot be realistically modeled within the the
original ATLSS model area, restricted by availability of hydrologic
inputs from the SFWMD Hydrology Model. An approach to providing an
expanded model area has been developed, including
the production of ATLSS High Resolution Hydrology estimates at the 500-m and
100-m scales of resolution.
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The underlying habitat type map for the Deer/Panther model is provided
by the Florida GAP
Analysis Vegetation Map, developed by Florida
Cooperative Fish and Wildlife Research Unit, University of Florida at
Gainesville (U.S. Geological Survey, Biological Resources Division).
A stable version of the FGAP vegetation map (Version 6.6) has
recently become available, and the extensive work required to adapt
this new and substantially modified version for use in Deer/Panther is
near completion. The vegetation component of Deer/Panther, which
provides spatial and temporal variation in available forage for the
deer herd, is being modified to provide realistic levels of Type I, II,
and III forage based on the FGAP Version 6.6 vegetation types, and deer
and panther behaviors which are influenced by habitat type are also
being modified to account for the habitat map change.
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The most recent version of the evolving ATLSS landscape classes has
been incorporated into Deer/Panther, dramatically reducing the run-time
required for simulations. Final timings and comparisons to
observational data have been deferred until incorporation of the new
habitat map has been completed.
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The predictive capabilities of an individual-based model are closely
tied to the realism of the decision rules which determine how
individual animals move across the landscape, interact with one another
and respond to their environment. The definition of these rules is in
turn tied to the availability and interpretation of empirical
observations about these behaviors and movement patterns.
The success of the genetic introgression project has changed the course
of panther recovery, and contradicted and confounded
published theories and opinions about panther ecology in South Florida,
including ideas about habitat use, home range establishment, female
fecundity, kitten survival, and dispersal patterns.
F1 panthers and
their offspring have been vigorous and healthy thus far, showing none
of the heart and reproductive problems seen in the Florida panthers.
Comparison of pre- and post-introgression monitoring data provides many
insights into panther habitat use and relative fecundity, suggesting the
degree to which reproductive fitness and kitten survival of Florida
panthers may have been compromised by generations of inbreeding.
For example,
panther literature has reflected the commonly held perception that Big
Cypress south of I-75 could not sustain a breeding population of
panthers because of thinning forest cover and poor soils. However, the
largest population expansion over the past two years has taken place in
this area. With this in mind, the telemetry data set of panther
location observations (1981-1995) on which preliminary panther behavior
rules for the Deer/Panther model were based has been expanded to
include observations through December 1999 so that recent trends can be
reflected in revised behavior rules. Observations from January--July
2000 are now available and will be incorporated as soon as data are
received. The ATLSS PanTrack Tool is being
used to display and analyze
panther telemetry data for the purpose of redefining behavior rules for
use in the Deer/Panther Model.
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Work has begun on an ATLSS model of vegetation succession in
South Florida, which will enhance the predictive capabilities of
Deer/Panther as well other ATLSS models.
The ATLSS Deer/Panther Model and the PanTrack telemetry viewing tool were
subjects of poster presentations
at the Greater Everglades Ecosystem Restoration (G.E.E.R.) Science
Conference held in Naples, Florida, December 11-15, 2000, hosted
by The Science Coordination Team, a committee of the South Florida
Ecosystem Restoration Task Force and Working Group.
Principal Deer/Panther model developer Jane Comiskey accepted a
position on the USFWS Florida Panther Subteam of MERIT (Multi-Species
Ecosystem Recovery Implementation Team) and has participated in the
work of this committee since December 1999. The coming year is shaping
up to be a pivotal one for panther monitoring and recovery. Decisions
are being made about the value of monitoring data, the validity of past
interpretations of accumulated data, the level of effort at which
monitoring of panthers should continue, the need for multiple capture
teams operating in South Florida, and the apportioning of recovery
tasks among the cooperating agencies. A recent restructuring has taken
place of groups directing panther recovery, and a major revision of the
Florida Panther Recovery Plan is being produced by the Jacksonville
office of USFWS. As part of this revision, decisions will be made
about the future course of genetic introgression and about possible
reintroduction of panthers into other parts of their historic range.
ATLSS hopes to use the knowledge and experience accumulated over the
period of Deer/Panther Model development to make useful contributions
to the decision-making process.