The Indicator
As a means of illustrating the amount of forest providing different degrees
of distance from non-forest cover, this indicator provides information on the
percentage of forest surrounded by small, medium, and larger neighborhoods
(defined below) containing at least 90% forest. The percentage of forest
that meets a certain set of criteria is calculated by determining what fraction
of pixels (squares of forest 30 meters, or about 100 feet, on a
side) is in the center of a window that meets the criteria. Thus,
the percentage of forest that has 90% or more forest cover within a radius of
about 250 feet (the immediate neighborhood, about 5 acres) is determined
by counting the number of pixels that are in the center of a 5-acre window that
contains at least 90% forest.
The Data
Data Source/Collection Methodology: Data for this indicator were prepared
by Kurt Riitters, USDA Forest Service (see http://www.srs.fs.fed.us/4803/landscapes/).
The data are based on the National Land Cover Dataset, which is described in
more detail in the technical
note for the national extent indicator. This is a 30-meter resolution remote-sensing-based
dataset that provides, among other things, forest/non-forest cover information
for the lower 48 states. The unit of data is the pixel, which is a square approximately
30 meters on a side.
Data Manipulation: The data presented here are from a moving window
analysis. In this approach, the algorithm describes many successive, overlapping
windows of a certain size, making it possible to characterize the
area surrounding each individual forest pixel, in addition to knowing its forest/non-forest
status. As the window moves across the dataset, each pixel is used
as the center of a window; thus, it is possible to determine how many forest
pixels are surrounded by different amounts of forest.
Five window sizes were used for this analysis but only three are reported here.
The three reported sizes are 2.25 hectares, referred to here as the immediate
neighborhood, 5 acres, or within a radius of about 250 feet;
65.61 hectares, referred to here as the local neighborhood, 160
acres, or with a radius of about one-quarter mile; and 5314. 41
hectares, referred to here as the larger neighborhood, 13,000 acres,
or within a radius of about one and a half miles. These sizes correspond
to 25 pixels (a square of 5 x 5 pixels); 729 pixels (a square of 27 x 27 pixels)
and 59,049 pixels (a square of 243 x 243 pixels). The other two window sizes
were 7.29 hectares and 590.5 hectares. (Note: This analysis uses a square window,
since each remote sensing pixel is square. Thus, the page text description of
the radius of the neighborhood is an approximation to
make the presentation clearer to a non-technical audience, and is written as
if the window were round.)
The analysis on which the data presented here was based determines, for each
pixel and window size, whether it is surrounded by at least 60% forest, at least
90% forest, or exactly 100% forest. For this report, the 90% criterion was chosen.
The 90% criterion was selected based on considerations of data quality and previous
experience with this analytical approach. The alternate interpretations, along
with a detailed description of the methodology, are described in detail in K.H.
Riitters et al. (submitted).
Table 3 presents the results of the full analysis, including all window sizes
and all three degrees of forest cover. As in the original publication, the table
uses the term core to refer to areas surrounded by 100% forest cover
for the indicated window size, interior to refer to areas surrounded
by at least 90% forest cover for the indicated window size, and connected
for areas surrounded by at least 60% forest cover for the indicated window size.
Data presented in the body of the report are indicated with an asterisk.
The satellite remote-sensing data presented here can, in theory, distinguish
non-forest areas as small as 100 feet on a side (10,000 square feet) from adjacent
forest pixels. In practice, the accuracy of doing this depends on the contrast
between forest and non-forest land cover, which is, in general, quite good.
In addition, geometry plays an important role in distinguishing non-forest land
cover. For example, a clearing that fills several 100-foot by 100- foot pixels
would probably be more easily detected than a winding road that may fill some
pixels and only partially fill others. For further reading on habitat fragmentation,
see other related indicators in this document and also Noss and Csuti (1997)
and Wilcove et al. (1986).
References
Noss, R.F., and B. Csuti. 1997. Habitat fragmentation, pp. 269304. In
G.K. Meffe and R.C. Carroll (eds.), Principles of conservation biology. Second
edition. Sunderland, MA: Sinauer Associates.
Riitters, K.H., et al. Fragmentation of continental United States forests.
Submitted to Ecosystems.
Wilcove, D.S., C.H. McLellan, and A.P. Dobson. 1986. Habitat fragmentation
in the temperate zone, pp. 237256. In M.E. Soulé (ed.), Conservation
biology: The science of scarcity and diversity. Sunderland, MA: Sinauer Associates.
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