The Indicator
This measure would report the percentage of grasslands and shrublands in patches
of different sizes. Patch sizes and percentages would be reported separately
for grasslands and shrublands. The patch sizes for this indicator are as follows:
less than 10 acres, 1099 acres, 100999 acres, 10009,999 acres,
and 10,000 acres or greater.
Species and ecosystem processes are sensitive to spatial heterogeneity. Landscape
diversity is an important component of species diversity, habitat conservation,
and human health. While much research has been undertaken to determine these
relationships in forested ecosystems, there is general agreement among grass/shrub
experts that such spatial patterns are important in grasslands and shrublands
as well. For example, in the sagebrush/grassland mosaic of western intermountain
basins, fuel buildup after a period of minimal grazing and sufficient rainfall
creates highly flammable conditions. When a fire does occur, the sagebrush is
greatly reduced in abundance because it cannot sprout, unlike nearly all the
grassland plants. Grassland expands, reducing the area of habitat for sagebrush-dependent
species.
The Data Gap
High-quality satellite data provide an excellent baseline to assess future
changes in patch sizes. Many of the indicators in this report are based on data
from the National Land Cover Dataset, produced by a federal interagency consortium
including the U.S. Geological Survey, the USDA Forest Service, the National
Oceanographic and Atmospheric Administration, and the U.S. Environmental Protection
Agency (see http://www.epa.gov/mrlc/nlcd.html
and the technical note for
the national extent indicator. It is expected that satellite data will be
used for this indicator.
However, the software currently available for analyzing patch size characteristics
was developed for use on relatively small landscape areas. It is not designed,
and cannot be used, to process datasets as large as are required for this indicator.
An alternative approach involves analyzing patch characteristics for smaller
landscape areas (such as 7.5 x 7.5 km), then combining the statistics on these
many individual areas to describe much larger areas, such as ecoregions. However,
in this approach, any patch that crosses the boundary of one of the 7.5 by 7.5
km squares is not accurately represented, because a portion is in one square
and a portion is in the adjoining square. This is referred to as a rightcensored
distribution and will provide consistent underestimates of the number of larger
patches.
In addition, the indicator should distinguish between lands that have been
altered (e.g., cultivated and seeded for pastures) and more natural
lands; only patches of the more natural grasslands and shrublands would be included.
References
Turner, M.G., and R.G. Gardner, eds. Quantitative methods in landscape ecology.
Springer-Verlag Ecological Studies, Vol. 82. New York: Springer-Verlag.
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