Full text: Resource and environmental monitoring

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area. Note urban, agricultural and desert land cover types. 
removing them from potential agricultural uses with its 
concomitant negative impact on potential productivity in 
this region. The second most urbanized soils are Regosols 
and Xerosols, which are generally a young, shallow or sandy 
soils, or arid desert soils respectively. Neither of these are 
well suited to agriculture, but their use is entirely appropriate 
to urban land use, thereby sparing more useful soils. The 
FAO soils map is very course resolution and has some 
registration faults. We suspect this registration error, along 
with possible realignment of channels and glint of urban 
light onto adjacent water bodies is responsible for the 
apparent occupation of 417 km? of water by urban land 
cover. The "city lights" product was not customized for 
Egypt. We used the average threshold of >89% that proved 
effective in our study of the United States [Imhoff et al., 
1977a,b]. Further refinement of this threshold will provide 
better accuracy. We have used FAO soils-based fertility 
indices in the U.S. [Imhoff et al., 19772] to get a better idea 
of the occupation of the most ideally suited soils by urban 
lands. The Fertility Capability Classification index [FCC, 
Buol et al., 1974, Sanchez et al., 1982] was used in the 
previous study. We are now working on a modeling 
approach to further evaluate the impacts of urbanization on 
global productivity. 
Table 2. FAO Soil types under urban land cover as 
determined using the "city lights" data set [Imhoff et al., 
1997a,b]. Area measurements are in km?. 
FAO Soil Order Total Area Urbanized '96 % Area 
Yermosols 572562 7053 1.2 
Lithosols 158754 2619 1.6 
Dunes/Sand 149156 1275 0.9 
Fluvisols 55250 17993 32.6 
Solonchaks 31334 1657 5.3 
Regosols 21667 5155 23.8 
Water 4759 417 8.8 
Rock 2230 0 0.0 
Xerosols 1096 233 23.3 
Totals 996809 36423 3.4 
International Archives of Photogrammetry and Remote Sensing. Vol. XXXII, Part 7, Budapest, 1998 
        
M tes ^ 3 RE E 
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Figure 5. 1987 Landsat Thematic Mapper image of Cairo 
  
4. CONCLUSIONS 
4.1 DMSP Historic and Single Orbit Data 
Due to contrast, variable contrast, registration and gain 
issues the historical DMSP/OLS archive is difficult to use in 
more than a qualitative fashion. Further work may prove 
productive in refining this product. Further work would be 
useful as no digital data exists prior to mid-1990's from the 
DMSP/OLS program. Likewise, the single orbit digital 
DMSP/OLS product presents similar difficulties with 
unknown gain. Our work in attempting to provide a historic 
measure of urban land cover change in Egypt using these data 
was unsuccessful. : 
4.2 *City Lights" Enhancement of DMSP/OLS 
Once we discovered the method for ‘thresholding’ the NOAA 
NGDC ‘stable lights’ product [Imhoff et al., 1997a,b] we 
found that we could eliminate or significantly reduce the 
problems of misregistration, cloud cover, glint of light into 
adjacent water bodies, etc. The "city lights" product has 
proven to be an accurate representation at least in total area 
of urban land cover in our initial study in the U.S. [Imhoff et 
al., 1997a] and in this study where we find 3.7% of Egypt 
under urban land cover types. 
4.3 Landsat MSS and Thematic Mapper Data 
High resolution daylight sensors will always be highly 
suited to determination of areal extent and location of urban 
land use types. Our work showed both MSS and TM to be 
useful in this regard, although very light infrastructure, 
which may not preclude the use of lands in agriculture, may 
be interpreted as 'urban' classes in classification schemes. 
Our analysis showed that as of 1987 perhaps as much as 
12% of the area under study was in an urban class. This 
number cannot be compared directly with our whole country 
analysis because it only included the heavily urbanized area 
of Cairo and the Nile delta - a 14,400 km? area where we had 
Landsat multitemporal coverage. Problems with high 
resolution data will always include cost of acquisition, high 
data volumes, low revisit frequency, cloud cover and 
difficulty in interpretation. 
4.4 FAO Soils under Urban Land Cover Classes 
Our fusion of "city lights" urban land cover classes with 
FAO soils showed a disturbingly high occupation of the 
most prevalent agricultural soil in Egypt [Fluvisols] - 
almost 33%. This occupation follows the pattern found in 
the U.S. by Imhoff et al. [1997a] where respectively 15, 8, 7 
and 2% of the best soils were covered by urban land cover in 
the four most highly productive agricultural states in the 
U.S. [California, Illinois, Florida and Wisconsin]. 
Fortunately in the U.S. only about 2.9% of the total land 
area is urbanized and much of the country has vast areas of 
highly fertile soils. In places like Egypt where the arid 
climate greatly reduces the potential for agriculture, an 
occupation rate of 3.7% may significantly compromise 
continued agricultural productivity, especially if conversion 
of the most appropriate agricultural soils to urban land use 
continues, 
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