Symposium on Remote Sensing for Resources Development and Environmental Management / Enschede / August 1986
87
Classification of land features, using Landsat MSS data
in a mountainous terrain
H.Taherkia & W.G.Collins
Remote Sensing Unit, Civil Eng. Dept., Aston University, UK
ABSTRACT - This paper evaluates Landsat MSS data in a hostile terrain located in central Alborz, north of Iran.
Correlation of the Three hands of the image were evaluated, and separation of differnt ground features was
examined. Training areas of different categories were located on the image using field work. Data from the
training areas then were manipulated to eliminate unwanted pixels.
Mean and standard deviation of the categories were calculated and data which fell in the range of three
standard deviations was selected. For the execution of the training areas a selected subscene was chosen and
then classified.
1. INTRODUCTION
The study area is located in central Alborz, north
of Iran in a very hostile terrain, where the Haraz
Road traverses through. Two Landsat MSS secenes
recorded at 4th September 1972 and 13th July 1977
were used for this study.
After applying geometric and radiometric
corrections, resampling at 50x50 metres, registerig
two multitemporal images together on the DIPIX, 35
subscenes (e each of 40x40 pixels) were chosen along
the road for further investigation.
A FORTRAN program was developed to enable plotting
of the subscenes in eight colours using a Tekronix
ink jet colour plotter. The package developed can
perform mathematical manipulation of the data to
produce a variety of combinations viz: additions,
subtractions, ratios, and vegetation index/formulae
etc. and plots the output data in the form of a
histogram. These statistical analyses have been
applied on a subscene which consists of landslide,
coarse lava, scree, vegetation cover and limestone.
In processing the subscene, plots of single bands in
eight colours (from black to white) were found to be
most acceptable to the human eye. However, due to
low values of vegetation in band 5 and higher values
of them in band 7, different combinations of the
bands showed further improvement in the
identification of ground features. Subtraction of
the two bands (B7-B5) showed clearly the boundaries
of ground vegetation (Figure la). The high
reflectivities of screes and bare soil in both bands
7 and 5 when they were combined in vegetation index
(B7-B5)/(B7+B5) caused low values in the resultant
image (Figure lb). Hence all unvegetated areas
appeared dark in the vegetation index.
The results of the different combinations were
compared against the ground truths at same the scale
(1:23,000). The outcome is shown in Table 1
comparing results of different combinations of
different bands and the ground truths derived from
existing maps of the study area.
As can be seen from the eight different combinations
in Table 1, the best results are obtained after
subtraction which allows discrimination of
vegetation covered areas (units 1, 2, 3 and 4). The
worst combination appears to result from addition of
the bands, which provides no basis for significant
discrimination of the vegetated areas.
The vegetation index, shown in Table 1 and Figure 2
highlights vegetated areas, but some areas of dark
shadow are also classified in the vegetation class.
Hence the use of the vegetation index in unknown
areas produces imperfect results. Despite the
recommendation of many Remote Sensing texts that a
vegetation index should be used as a tool to
distinguish vegetated areas in the Landsat MSS
images, it seems, on the basis of this research that
the best results are obtained by subtracting band 5
from band 7 (B7-B5).
Subtraction of band 4 from band 7 (B7-B4) in both
September and July images (figure 2) resulted in
over- classification in three vegetated areas and
under-classification in one area located on the west
facing slope of the Valley (Table 1). The shadow is
responsible for misclassification in the number 3
vegetated area, whereas mixed pixels of high
reflection of vegetation in boundaries are
responsible for over-classification.
Where band 5 was subtracted from band 7 (B7-B5), two
sunfaced vegetated areas (units 1 and 2) were found
to match the base map (Figures 1 and 4) whereas two
low illuminated areas (units 3 and 4) mismatched
(Table 1 and Figure 3).
Additions of different bands in each of the
September and July images revealed no more
information in this case. Only by the additions of
both band 5 and band 7 (B7+B5) and band 7 and band 4
(B7+B4) does there seem to be slight improvement in
landslide discrimination. It should be mentioned
here that addition of two bands in image processing
systems in a vast area showed a better result in
linear features recognition.
In addition to conventional image procesing
techniques, the use of either a vegetation index or
subtraction can assist the interpreter in the
identification of unstable areas between bare soil
and in the classification of vegetated areas. Both
procedures should be performed after applying
radiometric correction to the MSS image. Without
haze removal, any mathemtical manipulation on the
data will not produce a reliable result.