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Figure 2. Framework of the study
2.3 Vegetation indices
In the next step panchromatic band of QuickBird imagery was
applied as the base image for geometric correction of the
ASTER data. For this purpose imagine Auto Sync module of
ERDAS was used to perform automatic image registration. In
order to extract more useful information from the ASTER
images, appropriate image enhancements were applied on the
different spectral bands. To reduce the effects of the background
reflectance, a variety of indices were examined and the most
suitable indices identified among them.
The most known and widely used ratio-based index,
Normalized Difference Vegetation Index (NDVI), which is
sensitive to soil background, was used in this study. NDVI is
calculated on a per-pixel basis as the normalized difference
between the red and near infrared bands from an image:
NDVI= (NIR-RED)/ (NIR+RED)
Also three of the most commonly used and functionally
different broadband soil VIs were selected (Bannari et al., 1995;
Kasawani et al., 2010).
The VIs was calculated and analyzed using Spatial-Modeler
module in ERDAS Imagine. The VIs involved in this study are
as follows:
-PVI (Richardson and Wiegand 1977):
PVI = sin (a) NIR — cos (a) Red
Where,
a = angle between soil line and NIR axis
- SAVI (Huete 1988):
SAVI = [(NIR — R)/ NIR+R+L] X 1+L
Where,
L = 0.5 to minimize the soil influence, but the range of value is
reduced. These values are depending on the red reflectance that
has a coherent relation with soil influence.
- TSAVI (Baret and Guyot 1991):
TSAVI = a (NIR — aR — b)/ [Red + a (NIR — b) + 0.08 (1 + a2)]
Where,
a — slope of soil line determine by NIR plot
b = intercept of soil line
2.4 Preparing the crown area map
In order to preparing the crown area map, delineated individual
tree crowns were used. About 30 plots were located randomly
on the image with an area about 1 ha and then average crown
area has been calculated for each plot.
Then, mean DNs of plots with vegetation indices, was
calculated. simple linear regression was done between quantities
of vegetation indices as dependent (Y) variable and same
quantities of each plot in crown area as independent variable
(Xi).
3 RESULTS AND DISCUSSION
This paper applied color image segmentation to delineate
individual tree crowns from QuickBird images to estimate mean
tree per hectare for one of the most common tree species in
Zagros forest in Iran. The results were compared with field data
in the crown by crown basis. No missing crown was found and
the delineated crowns shoed perfect match with field measured
crowns. The models were developed using single linear
regression analysis, where the dependent variables were
vegetation indices, and the independent variable was mean
crown area per ha. The validation was carried out using paired t-
Student test and standard error of estimation. The results
indicated significant correlation between average crown area
per ha and vegetation indices. Figure 3 illustrate the scatter plot
and fitted line for each index. The scatter plots showed different
crown area for the same value of VIs. That means several
factors other than crown area contribute in creating surface
reflectance of the area. To produce certain values of the VIs not
only crown size is important but also tree spatial pattern is
significant. Small scattered single trees make more mixed pixels
in the border comparing to the one big tree with the identical
crown area. Moreover, the ratio between crown area and pixel
size is important. Many small crowns can be successfully
delineated using QuickBird imagery while can have strong
reflectance on the ASTER image.The investigation of several
VIs to estimate mean crown area in open forests showed the
relative preference of indices which are based on soil and
background characteristics.
4 CONCLUSION
One of the main objectives of this study was to evaluate the
capability and suitability of the ASTER satellite data, to
estimate average crown area per ha in open forests of Iran. The
presented results showed that spectral and spatial information of
the ASTER imagery can be correlated with the biophysical
forest parameters. At least spatial resolution more than the
average crown diameter is needed for successful development
of empirical relationships between remote sensing data and field
measurements.
Very high resolution remote sensing data can be used to provide
reliable crown area map.
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