Description
This is a layer representing the extent of land on the
western Mogollon Plateau that is predicted to fall under the legal
guidance of the Mexican Spotted Owl (Strix occidentalis lucida)
management guidelines. The layer was built using ForestERA vegetation
layers
and the definitions of Mexican Spotted Owl habitat outlined in the management
guidelines for that species (USFWS 1995). The layer has a resolution
of 90m (0.8 ha or 2 acres).
Purpose
This data layer was created as part of the ForestERA project
to support landscape-scale forest restoration planning efforts by
a broad group of stakeholders including federal and state agencies, academic
institutions, and non-governmental entities. These data are intended
for regional analyses over spatial extents on the order of tens to
hundreds of thousands of acres, and were not developed for use at
finer
spatial scales, although they may be useful for some applications
at finer scales.
Development
This layer was developed using the ForestERA dominant
overstory vegetation layer, a slope layer derived from a United States
Geological Survey digital elevation model (DEM), a layer depicting
specially designated protected areas (roadless areas, wilderness areas,
and national parks and monuments ) obtained from the Arizona Land Resource
Information System (ALRIS), and a layer identifying designated Mexican
Spotted Owl Protected Activity Centers (PACs) obtained from the United
States Forest Service.
The layer is a prediction of the extent of the landscape that falls
under the legal guidelines for management of Mexican Spotted Owl habitat.
Habitat areas
are defined as being either “protected habitat”, or “restricted
habitat”. The legal management guidelines for each of these designations
are outlined in an official document (USFWS 1995). Protected habitat includes
Mexican Spotted Owl PACs, areas of mixed-conifer or pine-oak vegetation on
slopes greater than 40%, and areas of mixed-conifer or pine-oak vegetation
in specially designated protected areas. Restricted habitat includes all other
areas of mixed-conifer and pine-oak habitat. We were unable to obtain data
layers that identified past management actions or tree size. Thus, areas that
had been logged in the past 20 years, and areas that did not contain enough
large trees were not eliminated from the habitat designations.
Two additional
rules were used to clean the map. First areas identified as mixed-conifer
in the ForestERA vegetation map, but occurring above 9500 ft,
were eliminated. These areas are actually covered by spruce-fir vegetation,
which is not included in the management guidelines. There is very little
spruce-fir on the western Mogollon Plateau, and so the ForestERA layer
does not distinguish
spruce-fir from other mixed-conifer. Seconsly, any isolated patches of habitat
that covered less than 20 acres were eliminated, as these areas were considered
too small to fall under the management guidelines.
Accuracy Assessment
As this layer represents management definitions,
rather than specific habitat designations, no true accuracy assessment
is possible. We refer readers to the accuracy assessment for the
ForestERA dominant overstory vegetation layer and the ForestERA slope
layer for
information on their accuracy. The accuracy of the PAC layer and
the specially designated protected area layer are assumed to meet the
accuracy
requirements of the agencies that created them.
Sources of errors
Some areas of protected and restricted habitat
are likely to be slightly overestimated since we did not have information
on tree size nor management history, which might have eliminated
some areas from consideration under the management guidelines. However,
the vegetation layer tends to underpredict both pine-oak and mixed-conifer
vegetation, so there is likely some general underprediction of habitat
across the entire study area.
Recommendations
We recommend that this layer be used at a minimum
resolution of 90m (0.8 ha or 2 acres) for purposes of analysis and
display. However, ForestERA data layers were not designed for analyses
at the level of individual pixels, and uncertainty in the data will
generally decline over greater spatial extents. Therefore, we recommend
using larger analysis units, with groupings of at least 50 cells
(40 ha or 100 acres). Finally, we reiterate that ForestERA data layers
were developed for the purpose of regional landscape-level planning,
and we suggest that the analyses be applied over spatial extents
of
tens to hundreds of thousands of acres. We recognize, however, that
this layer may be useful for analyses over smaller spatial extents
depending on the type and purpose of those analyses.
Literature Cited
U. S. Fish and Wildlife Service (USFWS). 1995. Recovery
plan for the Mexican Spotted Owl (Strix occidentalis lucida). U. S.
Fish and Wildlife
Service, Albuquerque, New Mexico.
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