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METHODOLOGY
Landscape Information Infrastructure in
Pennsylvania
Statewide spring/summer coverage of Landsat
Thematic Mapper (TM) data provided through the Multi-Resolution
Land Characteristics Consortium (MRLC) is the foundation of the
Pennsylvania-GAP landscape information infrastructure. This foundation
consists of hyperclusters which are built with the ISODATA facility
of ERDAS Imagine. First, every pixel in each scene is distributed
directly among a set of 255 clusters, with no sampling whatsoever.
Then complete bandwise signature information is compiled in conjunction
with the clustering, and this is used to compute relative brightness
measures for visible, infrared, and greenness.
Those brightness values permit us to construct cluster image mosaics
across scene boundaries. The clusters, with their tables of averaged
spectral attributes, permit us to render generalized image reconstructions—which
are export-compatible with the ARC/INFO Grid facility and are free
of proprietary restrictions on redistribution. Statewide cluster
images will be transferred to CD-ROM as a distribution medium and
made available on a cost recovery basis for production of the CD-ROMs.
These cluster images preserve visual landscape pattern and are free
of thematic focus.
The tables of scenewise cluster properties are kept separate from
the CD-ROM on diskette, which permits the tables to be augmented
as we proceed with landscape interpretations of the clusters. The
first such augmentation is a text-field characterization for each
cluster. Next follows cluster categorization according to a modified
UNESCO classification of land use/land cover which is substantially
compatible with Anderson. This is a northeastern states adaptation
of physiognomy and formation levels from a provisional scheme set
forth by The Nature Conservancy (TNC). Landscape interpretations
of clusters are formulated photointerpretively using the suite of
facilities available in ERDAS Imagine.
Floristic categorizations of forest clusters are then assembled
as separate relational tables keyed to each cluster. Reference to
supplemental information sources and assistance of cooperators is
required in the floristic interpretation phase. The base floristic
categorization will reflect Society of American Foresters cover
types as a point of departure for classification of alliance types.
It has been determined that spatial (patchwise) specificity comes
later in the analytical scenario.
The first step toward patchwise specificity is contiguity-controlled
spatial filtering to merge cluster patches less than one hectare
with larger neighboring patches. Another reason for preferring ISODATA
clusters is that their numbering and initiation protocols induce
strong correlation between cluster number and multispectral composite
brightness. Since major land use/land cover differences find expression
in composite brightness, attribution criteria for spatial merger
can be satisfactorily handled in terms of cluster numbers for micro-patch
suppression.
After imposing a one-hectare minimum on patchwise occurrence of
clusters, the clusters are next vectorized via the Vector module
of Imagine. Imagine is particularly advantageous in this regard
by virtue of using the same vector format as ARC/INFO and supporting
interactive image-based editing of such coverages. The commonality
extends to virtual identity of "Clean" and "Build"
operations. The initial attributes for polygons are scene ID and
cluster number. These, in turn, serve to index the relational tables
of cluster properties and scene metadata.
Floristic categorization is obtained from "multiway" analysis.
Categories for recognition are determined from cluster characterizations.
Training sets and signatures are obtained directly from the TM image
data classified at the pixel level in supervised mode. A supervised
strategy is also used to label clusters by classifying the cluster's
mean vectors. The map of labeled clusters and the direct supervised
classification are then differenced in terms of category numbers.
Where the difference map is zero, there is local agreement between
cluster-based classification and direct supervised classification.
Nonzeros in the difference map indicate localities of disagreement
and thus uncertainty. Overlaying the cluster-patch polygons on the
difference map shows problem areas for classification. These are
investigated with the help of cooperators to determine how GIS variables
can be used to formulate rules of reclassification that will treat
landscape settings selectively. Appropriate GIS variables are transferred
by overlay as cluster-polygon attributes. Reclassification takes
place on a polygon-by-polygon basis via ARC/INFO macros. Any remaining
problems are resolved by direct interactive editing. Since the rules
of reclassification represent elements of landscape understanding,
they are saved in text form as well as the AMLs.
Following vegetation analysis, any additional site-level GIS variables
required by vertebrate habitat models are also transferred by overlay
as attributes for the respective cluster-patch polygons. What results
from this phase is a one-hectare minimum database of polygonal landscape
segments corresponding to patches of clusters. Since more than one
cluster may occur in a particular vegetation class, polygon boundaries
are not necessarily vegetation boundaries. To produce a vegetation
map, the polygonal database is processed to dissolve boundaries
between polygons having the same attribute. This set of "cluster-patch"
polygons, then, constitutes the primary framework for the landscape
information infrastructure.
Next comes a series of criterion-based polygon aggregations to a
coarser scale. The scale change factors, in terms of minimum polygon
size, are 5-hectare, 10-hectare, 20-hectare, and 100-hectare minimum
levels. One objective in this reductive rescaling is to retain a
visual semblance of landscape pattern, corresponding to views from
increasing altitudes. Selected mixture and diversity attributes
due to rescaling will be computed and entered in polygon attribute
tables (PATs). When transferred from coarser to finer scales, such
attributes provide vicinity context.
Scale generalization by polygon aggregation ensures that segments
from different levels are strictly nested. When landscape interpretations
are extracted from imagery of different resolutions, there is usually
at least some degree of nonagreement. To overcome this lack of agreement,
direct on-screen photointerpretation of TM data at a 100-hectare
resolution is being developed to further differentiate between human-caused
and natural vegetation types. The two classes being recognized are
woody successional matrix versus anthropogenically sustained herbaceous
matrix. Islands of either type less than 100 hectares are not delineated.
Boundary cutoffs in digitizing are likewise not considered significant
if less than 100 hectares. This mapping speaks directly to high-level
landscape fragmentation and provides a comparator for the strategy
of polygon aggregation.
Each polygon data layer, representing a given scale, has a companion
layer of indexing points. The layers of indexing points enable construction
of polygon pyramids across scales. With the point indexing approach,
pyramids can be constructed for hierarchies of imperfectly aligned
polygons. It is also possible to adapt the point indexing strategy
for "fuzzy" nesting.
Concurrently with Gap Analysis, a second major application of this
Pennsylvania landscape information infrastructure is to formulate
ecological land types and land type associations under the Bailey
scheme being promoted as ECOMAP by the U.S. Forest Service. Deliberations
en route to these formulations will add to the depth of landscape
understanding.
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