Development of an individual-based model to evaluate elk (Cervus elaphus nelsoni) movement and distribution patterns following the Cerro Grande Fire in north central New Mexico, USA
Introduction
Long-term studies on the movement and distribution patterns of species at local and regional scales are needed because those are the scales at which conservation strategies are planned and implemented (Saunders and Hobbs, 1991). In early May 2000, the Cerro Grande Fire (CGF) in north central New Mexico burned approximately 19,020 ha as well as 400 residences in the town of Los Alamos. That fire, coupled with the region's unique fire history and interagency collaborations, presented a unique opportunity to study the long-term ecological consequences of large-scale fires on the regional elk (Cervus elaphus nelsoni) herd. Consequently, a “Participating Agreement” was signed by the Santa Fe National Forest (USFS), U.S. Department of Energy's Los Alamos National Laboratory (LANL), and the National Park Service (BNM) to collaborate in data collection efforts to evaluate and mitigate potential changes in movement and distribution patterns of elk following the Cerro Grande Fire.
Though many methods are available for modeling animal movements and distribution (e.g., path analysis, fractal analysis, random walks, structural equation modeling), there has been a growing interest in the use of individual-based models (IBMs) in ecological applications. Individual-based approaches to modeling animal movements address principles that are largely ignored in other modeling environments. First, IBMs acknowledge that individuals are behaviorally and physiologically distinct because of genetic and environmental influences and second, they acknowledge that interactions among individuals are inherently localized (Slothower et al., 1996, Schank, 2001). An advantage to IBMs is that they do not require many of the simplifying assumptions and mathematical derivations typically needed in more aggregated models (Railsback et al., 1999) thus resulting in a more realistic representation of real-world phenomena.
Integrated models of disturbance and succession offer a means of comparing long-term effects of fire events on forest vegetation and other ecosystem processes, including animal movement and distribution that may otherwise be difficult to observe empirically (Keane et al., 1989, He and Mladenoff, 1999, Turner et al., 2001). In addition, successional models enable evaluation of the cumulative effects of management practices and ecosystem response in a spatial context over long time periods (Keane and Hann, 1998). Several approaches have been used to model post-fire succession (Keane and Long, 1998, Barrett, 2001, Turner et al., 2001) but current efforts are focused on stochastic approaches that examine the relationship between fire regimes and landscape heterogeneity as well as fire-affected landscape changes through time (He and Mladenoff, 1999). The majority of post-fire successional models are designed specifically for evaluating forest (i.e., tree) dynamics and not the understory component to the degree deemed critical for modeling elk movement and distribution. As a result, the temporal resolution of such models is often in the range of years to decades—much longer than the daily or seasonal time step desired to evaluate elk movement across the Jemez.
Though studies have evaluated the effects of fire scale and pattern on elk (C. elaphus) (Turner et al., 1994), no studies have related the effects of post-fire landscape succession on ungulate movements and distribution using dynamic modeling techniques. Consequently, models linking the responses of herbivores to environmental heterogeneity and successional dynamics following large-scale fires are needed (Turner et al., 1994). Therefore, the purpose of this study was twofold: (1) to identify, calibrate, and validate a model that could simulate the underlying post-fire successional processes driving elk movement and distribution following the CGF; (2) to develop and integrate into the post-fire successional model a spatially-explicit, stochastic, individual-based model to evaluate potential movement and distribution patterns of elk in relation to spatial and temporal aspects of the CGF. Conceptualization, development, integration, and validation of the individual-based model are discussed here. Identification, development, and validation of the post-fire successional model are described in Rupp (2005).
Section snippets
Area description
The Pajarito Plateau, located in the Jemez Mountains of north central New Mexico, was formed by an ash flow of volcanic activity about 1.4 million years ago (Wilcox and Breshears, 1994). The region is classified as a wildland–urban interface and is politically segmented, making natural resource management difficult. The most conspicuous and influential government entity is Los Alamos National Laboratory (11,200 ha). It is bordered by Bandelier National Monument (13,290 ha) to the southwest, Santa
Model conceptualization
One of the primary objectives of the research was to analyze potential movement pathways across the Jemez typically used in “migration” and assess whether these pathways may change in response to spatial and temporal aspects of the Cerro Grande Fire. By definition, migration indicates a periodic shift from one seasonal home range to another, which can be assessed through an analysis of site fidelity within each range (Hooge, 2003, pers. comm.). The elk population in the Jemez Mountains,
Results
Overall patterns of habitat use by simulated animals during 2001–2004 were consistently similar to patterns observed in the independent test set. Because simulated animals were programmed to follow the advancing and receding snow line, they exhibited less movement down mesa tops than the real population. Overall habitat-use patterns were consistent with the real population, though simulated animal densities were higher than those of the real animals just south of the Cerro Grande burn area and
Discussion and future research
Quantifying landscape connectivity requires spatially-explicit methods that are sensitive to the possibility of complex interactions between the behavior of individual animals and landscape structure (Pither and Taylor, 1998). Spatial simulation models that evaluate interactions among cells in a raster-based environment provide a powerful approach to modeling spatial dynamics of complex systems based on individual-level properties (Wiens et al., 1993). However, simulation models are critically
Acknowledgements
Our appreciation goes out to The Canon National Parks Science Scholars Program and the Ecology Group at LANL for funding this project. We would also like to thank the Valles Caldera National Preserve, New Mexico Department of Game and Fish, U.S. Forest Service, Bandelier National Monument, Telonics, Inc., Santa Clara Reservation, and Adventure Aviation for assistance with collar retrieval. Dr. Michael Coughenour, developer of the SAVANNA Ecosystem Model, offered valuable insight and guidance in
References (63)
- et al.
Statistical validation
Ecol. Model.
(1993) - et al.
Movement rules for individual-based models of stream fish
Ecol. Model.
(1999) Testing ecological models: the meaning of validation
Ecol. Model.
(1996)- et al.
Individual-based modeling in ecology: what makes the difference?
Trends Ecol. Evol.
(1996) - et al.
Individual-based model of sympatric populations of brown and rainbow trout for instream flow assessment: model description and calibration
Ecol. Model.
(1998) Migration
- Allen, C.D., 1996. Elk response to the La Mesa Fire and current status in the Jemez Mountains. In: Allen, C.D. (tech...
Social behavior of elk, Cervus canadensis nelsoni, in the Jackson Hole area of Wyoming
Behaviour
(1952)The Elk of Jackson Hole. Bulletin 10
(1958)- Barrett, T.M., 2001. Models of vegetative change for landscape planning: a comparison of FETM, LANDSUM, SIMPPLLE, and...
Evaluating techniques to monitor elk movement across fence lines
Wildl. Soc. B
The SAVANNA Landscape Model—Documentation and Users Guide
Applied Statistics and the SAS Programming Language
Soil morphology of canopy and intercanopy sites in piñon-juniper woodland
Soil Sci. Soc. Am. J.
The social organization of a sedentary population of North American elk: a model for understanding other populations
Individual-based Modeling and Ecology
Pattern-oriented modeling in population ecology
Sci. Total Environ.
Spatially explicit and stochastic simulation of forest-landscape fire disturbance and succession
Ecology
Personal communication
Course in “The Analysis of Telemetry Data in the GIS Environment”
Animal Movement Extension to Arcview. (ver. 2.0)
Simulation of vegetation dynamics after fire at multiple temporal and spatial scales—a summary of current efforts
A comparison of coarse scale fire effects simulation strategies
Northwest Sci.
Use and interpretation of logistic regression in habitat-selection studies
J. Wildl. Manage.
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