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Last modified
1/26/2010 12:35:30 PM
Creation date
10/11/2006 11:00:00 PM
Metadata
Fields
Template:
Water Supply Protection
File Number
8220.101.10
Description
Colorado River-Water Projects-Glen Canyon Dam/Lake Powel-Glen Canyon Adaptive Management
Basin
Colorado Mainstem
Water Division
5
Date
1/1/2004
Author
Phillip Davis
Title
Review of Results and Recommendations from the GCMRC 200-2003 Remote Sensing Initiative for Monitoring Environmental Resources Within the Colorado River Ecosystem
Water Supply Pro - Doc Type
Report/Study
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<br />microns per picture element (1700 dpi) was adequate to retain all of the infomlation in the <br />photographs (compare Figures 28 and 29); a scan resolution higherthan 15 microns produces too <br />much image noise to be useful in photogrammetry. In addition, evaluations of various data <br />compression engines during the remote-sensing initiativc determined that the best compression <br />software was Gzip because it is lossless. frce-ware, and not copyrighted. At this time. the film <br />library is being converted to digital format by the IT program and. since the beginning of the <br />initiative. all image data collections have been delivered in digital format and have been <br />duplicated for archival preservation. An ArclMS system has been implemented by the IT <br />program which allows easy access to most of the collected digital data. <br /> <br />4.2.2. Most suitable image data for geomorphology <br /> <br />Concerning future data collections, scientific review of image data collected during the <br />remote-sensing initiative at different spatial resolutions showed Ihat 15-20-cm resolution was <br />sufficient for geomorphic mapping of physical resources. We found that digital, orthorectified <br />panchromatic imagery with 18-cm resolution can be acquired at about one-half the cost of color <br />imagery. However, evaluations of different types of image data for mapping physical resources <br />showed that CIR imagery discriminates surface materials better than panchromatic data (compare <br />Figures 30 and 31) and allows more accurate digital classification of sand bars and debris tlows <br />than does panchromatic imagery (Davis et aI., 2002b). In fact. CIR imagery (Figure 31) was <br />found 10 be better than true-color imagery (Figure 29) for mapping sand bars and debris tlows, <br />mainly because CIR imagery allows more complete removal of vegetation cover, which in turn <br />allows more accurate determination of geologic surface textures (Davis et aI., 2002b). Surface <br />texture was found to be a very important characteristic for distinguishing smooth sand bars and <br />rough debris tlows (Davis et aI., 2002b); this was also found in other surficial-geologic studies <br />(Shih and Schowengerdt. 1983; Anys et al.. 1994) <br /> <br />4.2.3. Airborne approaches for ground topography <br /> <br />In March and in August-September of 2000, GCMRC collected L1DAR data with <br />different collection parameters to evaluate the ability ofLlDAR to provide lopography at <br />acceptable vertical accuracies on bare surfaces and on vegetated surfaces at the GCM RC <br />sediment long-term monitoring sites. The March data were collected with the ALMS (Aeroscan <br />Laser Mapping System) sensor at a spot spacing of 3.75 m and a spot diameter of 1.5 m. The <br />August-September data were collected with the RAMS (Remote Airborne Mapping System) <br />sensor at a l-m spot spacing and a 0.5-m spot diameter; Ihese data were acquired both in August <br />and in September over the same four long-term monitoring siles using the same collection ~ <br />parameters to evaluate the precision ofLlDAR elevation data. Photogrammetric data were <br />derived from stereo image data (I A,OOO-scale photography) that were collected in September <br />2000 for one of the four study areas. Ground-survey elevation transects were performed at the <br />sites during the L1DAR surveys and stakeout surveys were conducted at selected L1DAR point <br />locations after the L1DAR surveys on different types of bare surfaces and within vegetated <br />terrain. The L1DAR data sets and the photogrammetry data set were compared to the ground <br />survey data to determine each data set's vertical accuracy. Various analyses were performed on <br />these data over a two-year period (e.g., Davis et aI., 2002a; Mietz et al.. 2002), culminating in a <br />final detailed evaluation of these data (Davis et al.. submitted). <br /> <br />Our evaluations of high-resolution photogrammetry and of different rcsolution and <br />replicate L1DAR data with respect to GCMRC monitoring requirements for sediment deposits <br />provided the following conclusions; <br /> <br />24 <br />
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