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Vegetation Classification and Mapping Project Report - USGS

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Base Map Class Development<br />

names being adjusted based on the input<br />

of park staff during that meeting.<br />

3.1.5. Base Map Automation<br />

The Geographic Information Systems<br />

Spatial Analysis Laboratory (GISSAL) in<br />

the Department of Geography at Kansas<br />

State University provided the technical<br />

expertise to automate the polygons<br />

<strong>and</strong> associated map class <strong>and</strong> modifier<br />

assignments, creating a spatial vegetation<br />

map database.<br />

3.1.5.1 Aerial Photograph Mosaic<br />

SCPN provided GISSAL with one<br />

complete set of the 1:6,000 true color<br />

aerial photographs. Each of the 9 in x 9 in<br />

contact prints was scanned at a resolution<br />

of 500 dpi <strong>and</strong> full color depth, then<br />

saved in TIF image format, resulting in<br />

an uncompressed file size of 74.5 MB<br />

per photo. Digital versions of the aerial<br />

photographs were cropped in Adobe<br />

Photoshop 6.0 (Adobe Systems Inc., San<br />

Jose, CA) to remove the black borders<br />

present on the original hardcopy photos.<br />

Orthorectification was performed with<br />

ER Mapper 7.0 (Leica Geosystems, San<br />

Diego, CA) using National Elevation<br />

Dataset (NED) digital elevation models<br />

(DEMs) as the height reference. Northing<br />

<strong>and</strong> easting for ground control points<br />

(GCPs) were determined from an existing<br />

low-resolution digital orthophotograph.<br />

Between four <strong>and</strong> six GCPs common<br />

to each scanned aerial photograph <strong>and</strong><br />

corresponding digital orthophotograph<br />

were defined within ER Mapper until a<br />

root mean square error (RMS ) of ≤ 1<br />

error<br />

pixel (equivalent to an error of less than<br />

0.3048 meters or 12 inches) was achieved.<br />

When necessary, additional GCPs were<br />

identified to meet this threshold. The<br />

output projection <strong>and</strong> datum for the final<br />

product were UTM Zone 12N <strong>and</strong> NAD<br />

83.<br />

Individual orthorectified photographs<br />

were compressed at a ratio of 1:35<br />

<strong>and</strong> saved in ECW format. Each of the<br />

individual orthorectified digital photos<br />

was combined in a mosaic operation<br />

<strong>and</strong> color-balanced in ER Mapper to<br />

produce the final seamless 1:6,000 scale<br />

digital photomosaic, at 0.3048 meter or 12<br />

inch pixel resolution, for the park <strong>and</strong> its<br />

environs.<br />

3.1.5.2 <strong>Vegetation</strong> Map Database<br />

Development<br />

The photointerpretation team provided<br />

more than 1000 transparent polyester<br />

sheet overlays with map polygon<br />

delineation to GISSAL. Each overlay<br />

included boundary information for<br />

delineated map polygons, along with codes<br />

representing the numeric reference for the<br />

base map class, including any applicable<br />

modifiers. Overlays were scanned <strong>and</strong><br />

converted into black <strong>and</strong> white digital<br />

raster files (TIF format) for processing <strong>and</strong><br />

archiving.<br />

Digital versions of the scanned overlays<br />

were orthorectified in ER Mapper 7.0<br />

using 1/3 arc second (10 meter) digital<br />

elevation models (DEMs) from the<br />

National Elevation Dataset (NED) as<br />

the height reference, <strong>and</strong> the previously<br />

created digital orthophotomosaic as the<br />

base map. As was performed previously<br />

with orthorectification, 4-6 GCPs common<br />

between the scanned overlays <strong>and</strong> the<br />

high-resolution orthophotomosaic<br />

were defined within ER Mapper until<br />

a horizontal root mean square error<br />

(RMS ) of ≤ 1pixel (equivalent to 0.3048<br />

error<br />

meters or 12 inches) was achieved. If<br />

necessary, additional GCPs were identified<br />

to meet this threshold.<br />

After orthorectification was completed,<br />

each overlay was subjected to a rasterto-vector<br />

conversion using the ArcScan<br />

extension available with the ArcGIS<br />

9.2 (ESRI, Redl<strong>and</strong>s, CA) software.<br />

Vector line features generated from the<br />

scanned vegetation boundaries were<br />

“edge-matched” with boundary lines<br />

generated from adjacent overlays <strong>and</strong> then<br />

converted into polygon features. Map<br />

unit attribute information, read directly<br />

from photointerpreter markings on the<br />

27

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