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Past and current projects have focused on
a variety of spatial and ecological scales including investigations on
specific species, populations, communities, and ecosystem-level
biodiversity. Examples of these projects are discussed below.
The foundation for CASE began during the
original New Mexico Gap Analysis Project (NM-GAP) funded by U.S.
Geological Survey, National GAP Program. This was the first statewide
attempt to map land cover, habitat, and conservation stewardship
(Thompson et al. 1996). The NM-GAP vegetation map identified 42 land
cover types throughout New Mexico that were used to predict potential
habitat for 584 vertebrate species. Spatial analysis of biodiversity
provided land managers and planners with landscape level data to support
conservation planning.
Involvement of the New Mexico Cooperative
Fish and Wildlife Research Unit in the original NM-GAP effort prompted
the selection of the laboratory to participate in the Southwest Regional
Gap Analysis Project (SWReGAP) which is an update of the gap analysis
effort in the Southwest. This is a multi-state, multi-agency effort
with cooperating projects in Arizona, Colorado, Nevada, Utah, and New
Mexico. The goals of this research are to map the natural vegetation of
the 5 southwestern states; 2) model habitat for vertebrate species
occurring within those states; 3) map stewardship and management
categories; 4) conduct spatial analysis; and 5) provide information for
land managers to use in conservation planning. CASE serves as regional
habitat modeling and regional land stewardship laboratory and is
responsible for completing a land cover map at the ecological system
level for New Mexico and parts of Arizona and Colorado. CASE is
facilitating the habitat modeling of 833 vertebrate species within the
regional project by providing a regional habitat protocol, facilitating
regional modeling through standardized methodology, and modeling. The
laboratory is also responsible for creating the land stewardship
coverage for use in gap analysis, data analysis, report writing, and
overall project finalization.
CASE has also integrated spatial analysis
and habitat modeling to incorporate ecological context into conservation
planning for Fort Bliss Military Reservation (Hamazaki et al. 2001).
Ecological context provides a decision system for land managers to
conserve ecological features that are abundant on, represent, and/or are
unique to Fort Bliss, rather than features which are scarce on Fort
Bliss but are contextually more conservable elsewhere. The objectives
of this research were to 1) specify an ecological context area
encompassing Fort Bliss; 2) identify and determine unique or sensitive
vegetation and animal communities on Fort Bliss, and create GIS layers
to indicate areas of the unique or sensitive vegetation and animal
communities in Fort Bliss; and 3) to use information to characterize the
ecological context of Fort Bliss. This project identified conservation
foci for Fort Bliss and demonstrated how to incorporate information
about ecological context in conservation planning (Hamazaki et al.
2003). This work demonstrated how consideration of such context can
help to identify possible adjustments to conservation priorities to
reflect the position of a jurisdiction on the landscape. This approach
provided insight for supplementing conservation planning for locally
scarce (e.g., rare or endangered) but ecological contextually abundant
ecological features. In addition, this project synthesized knowledge
about conservation and facilitated greater cooperation among landholders
and created effective and consistent region-wide conservation
strategies.
CASE has
participated in specific species or species habitat research on a wide
variety of scales. This includes research on aplomado falcon habitat,
ungulate migration, habitat modeling and risk assessment of 13 differing
taxa.
CASE cooperated in a multi-agency,
multi-country research project on aplomado falcons (Falco femoralis).
Falcon habitat was modeled in the northern Chihuahua Desert to enhance
the understanding of aplomado falcon natural history and to predict
areas of potential habitat in southern New Mexico, western Texas, and
northern Chihuahua. A unique modeling approach was taken where a
spectrally driven predictive habitat suitability model was created for
aplomado falcons based on Landsat 7 Enhanced Thematic Mapper Plus
imagery (Young et al. 2002). The predictive model was based on
landscape configuration and composition of falcon sites located during
ground surveys conducted in 1998-1999 in northern Chihuahua. Spectral
land cover properties were used in combination with Digital Elevation
Models to characterize falcon use areas in Chihuahua and identify areas
with similar spectral composition and configuration in the northern
Chihuahuan Desert. Image analyses and GIS modeling were conducted at
CASE. The predictive model for suitable aplomado falcon habitat serves
as an effective tool for identifying areas similar to falcon use areas
in Chihuahua. The predictive model and validation protocol has assisted
land managers in prioritizing areas for conservation, management, and
restoration of aplomado falcons. Users include the Bureau of Land
Management, White Sands Missile Range, Fort Bliss Military Reservation,
U.S. Fish and Wildlife Service, and numerous private groups.
CASE supported a Research Unit project
focusing on San Antonio Mountain in northcentral New Mexico. This is
important winter habitat for an interstate elk (Cervus elaphus)
population that moves between Colorado and New Mexico. Little was known
about herd demographic, temporospatial distribution, and extent elk
contributed to resource conflicts. Research was conducted to: 1)
estimate demographic attributes of the San Antonio Mountain winter range
(SAW) elk population, 2) characterize temporospatial dynamics of SAW elk
among seasonal ranges, and 3) evaluate resource conflicts in relation to
timing and extent of SAW elk movements as they contact various land
ownership properties (Kantar 2002, Smallidge et al. 2003). Population
estimates (Gould et al 2004) and herd composition counts relied on
spatial data to develop and implement appropriate sampling protocol.
Demographic field data were processed using spatial analysis software to
support population parameter estimation. Classification and analysis of
the temporospatial distribution of elk was heavily dependent on spatial
data and spatial analysis at each step of the evaluation. Migration
timing and routes, seasonal elk distributions, and herd temporospatial
distributions were estimated, classified, and evaluated using spatial
analysis software. Spatial information was further employed in
developing sampling protocol for resource conflict evaluation involving
SAW elk. Research supported a Doctoral student, Master’s student, and 1
research technician. Research results of demographics, temporospatial
distribution, and resource conflicts of San Antonio Mountain wintering
elk were delivered to New Mexico Department of Game and Fish, U.S.D.I.
Bureau of Land Management, U.S.D.A. Forest Service, and Rocky Mountain
Elk Foundation with the intent to support various management decision
making processes.
CASE examined how the Species At Risk
(SAR) concept could be extended to evaluate potential of a sensitive
species to impact military missions and the ability for that species to
be managed in such a manner as to preclude federal listing in the future
(Boykin et al. 2001). This study identified species for assessment,
prepared habitat models for species assessment and conducted field
surveys for reconnaissance, testing, and validation of modeling, and
evaluated prospective existing risk assessment models for application to
SAR evaluation. Using a structured and documented review protocol, a
list of >300 taxa considered sensitive by various public and private
conservation agencies and organizations was condensed to fewer than 30
demonstrably at-risk species. These at-risk species included the
black-tailed prairie dog, Colorado chipmunk, ferruginous hawk, Baird’s
sparrow, a land snail complex, and the night-blooming cereus. Through
habitat modeling (Bak et al. 2001, Kroll et al. 2003, Rivieccio et al.
2003) and an integrated risk assessment (Andersen et al. In Press) we
produced a landscape perspective useful to military installations and
others in relation to conservation responsibility. Management of listed
species consumes large amounts of time and money and can interfere with
the military mission. This proactive management approach can be a major
benefit to the Army's future ability to test and train on its
installations.
CASE
conducted a fire ecology study on White Sands Missile Range (WSMR). The
study provided a historical perspective on the role of fire on the
range, analyzed existing vegetation data, and conducted spatial analysis
to derive a three tiered management stratification of WSMR for fire
management (Boykin 2000). The study provided needed ecological
background for WSMR to complete a range-wide fire management plan.
Using this hierarchy, a large-scale vegetation map and GIS, we created
simplistic risk models based on fuel models, topography, and sites of
concern for natural resource managers. The resulting maps provided a
landscape view of the fire risk to natural and human resources and
allowed land managers to take a landscape approach in fire management.
Working with Big Bend National Park, CASE
conducted a spatial analysis of vegetation change in the Chisos
Mountains (Ernst et al. 2003). Historical aerial photography and
multi-temporal satellite images were used to investigate change
occurring in the Chisos Mountain woodlands. Historic aerial
photographs, MSS satellite images, and Landsat 7 Enhanced Thematic
Mapper (ETM+) imagery were classified and analyzed to detect the change
in the extent and cover of vegetation communities. Over time, the
proportion of area occupied by individual land cover classes remained
relatively consistent. This study is providing managers a historical
perspective on the change in woody species composition and the role of
fire within the system.
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