Spectral Unmixing Applied to Desert Soils for the - Naval ...

Spectral Unmixing Applied to Desert Soils for the - Naval ... Spectral Unmixing Applied to Desert Soils for the - Naval ...

26.03.2013 Views

A B C Figure 38. Inset A shows a color composite result using the ASD measured camp road endmember and 2 imagery derived endmembers for RGB color composite. Red pixels represent the camp road material. Inset B shows a color composite using an imagery derived endmember, the ASD measured camp road endmember, and another imagery derived endmember for R, G, B, respectively with green pixels representing target material. The potential trail identified with this endmember in Figure 29 shows up in green here, and is particularly noticeable as an s shape closer to the creek. With both ASD measured endmembers, the most accurate results were in the range of 9-18% pixel fill. Higher than 18% resulted in some matches and some false positives with lithified rock faces. Inset C shows an example of a color composite of the actual imagery with band combinations highlighting specific image elements. This was to help verify target material was accurately identified in the color composites depicted in A and B. 74

VII. DISCUSSION AND CONCLUSIONS A. SPECTRAL MEASUREMENTS AND SOIL DISTURBANCE Analysis of the collected spectral libraries established that there were measurable differences between spectra of disturbed versus undisturbed areas of the same composition materials. Endmembers collected in the field were all categorized by a material first undisturbed and then disturbed from the same location. The disturbances were all caused by impact-related use such as walking, driving over, or dropping something onto the soil, OHV and equestrian use (horses). Firerelated disturbances were also used in order to have information regarding camp fires to help associate the source as anthropogenic. For the initial clay collection the samples were all taken from the same area and spanned a section of roughly 1.62 Km 2 . The continuum removed spectral differences occur in the wavelength regions of approximately 500 nm, 1200 nm, and 2200 nm. The changes observed at these wavelengths involve differences in apparent reflectance received at the sensor and calculated differences in band depth and observable width differences of absorption features in the same material. Similarities in the amount of difference in depths between ASD collected endmembers and imagery derived endmembers suggested that these differences made the spectra unique enough to be successfully used to detect features such as trails based on differences in spectral characteristics. Clearly properties of soils are altered once they have been exposed to some surface disturbance, particularly those caused by impacts. It is the chemical and structural make-up of soil that causes it to exhibit its characteristic absorption feature. Previous studies have found similar changes in reflectance and spectra shape, depth, and width of vegetation exposed to gasses injected into soils. These changes were the result of a stress response by vegetation to the gasses as a function of distance from the source. It makes sense then that if reflectance changes in vegetation are a response to an ecosystem disturbance, then the reflectance changes in this study can be correlated to anthropogenically caused surface disturbances as well. The data shown in this report support this line of thinking because the changes in reflectance are similar enough to the 75

A B<br />

C<br />

Figure 38. Inset A shows a color composite result using <strong>the</strong> ASD measured camp road<br />

endmember and 2 imagery derived endmembers <strong>for</strong> RGB color composite.<br />

Red pixels represent <strong>the</strong> camp road material. Inset B shows a color<br />

composite using an imagery derived endmember, <strong>the</strong> ASD measured camp<br />

road endmember, and ano<strong>the</strong>r imagery derived endmember <strong>for</strong> R, G, B,<br />

respectively with green pixels representing target material. The potential<br />

trail identified with this endmember in Figure 29 shows up in green here,<br />

and is particularly noticeable as an s shape closer <strong>to</strong> <strong>the</strong> creek. With both<br />

ASD measured endmembers, <strong>the</strong> most accurate results were in <strong>the</strong> range of<br />

9-18% pixel fill. Higher than 18% resulted in some matches and some false<br />

positives with lithified rock faces. Inset C shows an example of a color<br />

composite of <strong>the</strong> actual imagery with band combinations highlighting<br />

specific image elements. This was <strong>to</strong> help verify target material was<br />

accurately identified in <strong>the</strong> color composites depicted in A and B.<br />

74

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