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Estimating woody vegetation cover in an African Savanna using remote sensing and geostatistics.

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Usually, regression is the empirical method applied to field and remote sensing data for the spatial estimation of woody vegetation variables. Cokriging was used to evaluate the cross-correlated information between SPOT (Satellites Pour l'Observation de la Terre or Earth-observing Satellites)-derived vegetation variables and field-sampled woody vegetation percent canopy cover and density.

Introduction 1.1 Background

Aim and Objectives of the study

In light of this background, the aim of this study was to investigate the utility of high-resolution satellite imagery in combination with geostatistics to determine the density and spatial distribution of woody vegetation cover in a semi-arid African savanna. Evaluate the utility of different vegetation indices and textural measures to characterize savanna woody vegetation cover.

Key Research Questions

An integration of remote sensing and geostatistics (specifically cokriging) was used to estimate woody vegetation density and spatial distribution in an experimental study area of ​​Kruger National Park, South Africa. Predict woody vegetation cover and density using geostatistical techniques (especially cokriging) with vegetation spectral data obtained from SPOT or the measure of image structure that best correlates with woody cover and wood density variables.

Organisation of the Thesis

Correlate SPOT-derived variables (VIs, raw images, and texture indices) with field-sampled woody cover parameters.

SAVANNA WOODY VEGETATION

Study Area

KNP is crossed by seven major river systems, all of which originate in the west of PKN and drain a combined area of ​​about 860 000 Ha (Mabunda et al. 2003). However, in the Shingwedzi region of Kruger National Park, the structure of mopane forest which is a dry savanna of southern Africa, there is little local variation in the relative dominance of tree and shrub forms of the dominant species, Colophospermum mopane throughout the succession. environmental settings such as landforms and available plant moisture status (Khomo &.

Figure 1.2: Location of the Study Area in the Kruger National Park (KNP)- South Africa
Figure 1.2: Location of the Study Area in the Kruger National Park (KNP)- South Africa

Literature Review

  • Remote sensing of vegetation density estimation and Savanna study
  • Savanna Woody Cover Estimation and Remote Sensing
  • Vegetation indices and Remote Sensing of Woody vegetation Cover
  • Description of SPOT5 derived Vegetation Indices
  • Remote sensing of Savanna Vegetation and Image Texture analysis
  • Geostatistics and Remote Sensing of Savanna woody vegetation
  • Geostatistical measures of spatial variation
  • Lessons learnt from Literature Review

However, the main focus is on the utility of satellite remote sensing techniques for the spatial estimation of woody vegetation cover. This parameter is highly related to the size of objects in the sample data (Woodcock et al. 1988a).

Materials and Methods 3.1 Introduction

  • Software and Field Materials
  • Methods

The method explains and outlines the theoretical considerations that are integrated into the techniques used for this study. In the pre-field work, all available information about the study area was collected and processed before starting the actual field work. However, because the distance between VCA sites is very large (Figure 3.3) and does not represent the range of spatial influence in the surrounding woody vegetation community, spatial interpolation of KNP's VCA data does not provide reliable spatial vegetation maps (Wessels et al. 2006).

Percent woody canopy cover per plot was assessed by estimating the total area covered by all trees in the plot. Crown diameter of trees was determined by measuring individual tree canopy in the north-south and east-west directions. This approach of clustering helps to reduce the large distances (3km-12km) between VCA sites, which do not provide reliable spatial interpolation of the surrounding vegetation resources (Wessels et al. 2006) in the KNP.

For spatial interpolation of vegetation sources, it is crucial that the samples are representative of the surrounding vegetation sources in the study area (Mutanga & Rugege 2006) and follow a regular pattern, which also ensures that the maximum spatial interpolation (e.g. kriging) error is minimized (Webster & Oliver 2001).

Figure 3.1: Field Design and Data Collection
Figure 3.1: Field Design and Data Collection

0.5NIR R

For the SPOT5 multispectral scanner (MS) system, this difference corresponds to the ratio or spectral differences between bands 3 and 2. In this regard, in addition to the four bands for the SPOT5 MS image, five vegetation indices were calculated as follows:

NIR R

Relationship between Spot image Data and Woody Vegetation

  • Descriptive Statistics
  • Relationship between SPOT5 Spectral Data and Woody Vegetation Cover
  • Relationship between Image Texture and Woody Vegetation Cover
  • Predicting woody vegetation parameters using multiple independent SPOT variables

This chapter reports results obtained from analysis of the relationship between savanna forest vegetation parameters and remotely sensed SPOT image data. Before determining the relationship between field and remotely sensed data, analysis of the spatial structure (data distribution and normality testing) of the data sets is presented. After an analysis of the relationship between the datasets, the chapter presents the results of the best woody vegetation correlates predicted using several independent SPOT variables.

The results of the Kolmogorov-Smirnov D-statistics (K-S) test, which showed that the data sets under test are normally distributed, are shown in Table 4.1. This can be attributed to the configuration of the texture algorithms on the image bands, as well as the effect of the spatial resolution of the SPOT image bands. Betas of the SPOT variables (Table 4.3) used in the stepwise linear regression equation were input to the ArcGIS Spatial Analyst Tool (Raster Calculator) to calculate the regression model equation using the selected SPOT data for the predictor variables.

The prediction accuracy of the models was calculated using RMSE analysis on an independent %canopy wood cover and tree density (data n = 25).

Table 4.1: Descriptive statistics for best woody and SPOT variables (Total n = 100).
Table 4.1: Descriptive statistics for best woody and SPOT variables (Total n = 100).

Geostatistical analysis

  • Selecting Optimal Field and Spot Derived Vegetation Variables for Cokriging
  • Investigating Directional Influence or Anisotropy in the Datasets
  • Estimating Woody variables using ordinary kriging and Cokriging
  • Evaluation of the prediction error of the kriging models
  • Comparing the cokriging method with ordinary kriging and regression approaches
  • Summary of Results

The resulting variogram surfaces reflected a gradual increase in semi-variogram values ​​from the center in all directions (Figure 5.1) for both the %canopy and tree density datasets. The semivariogram of the fit model for % wooded canopy and the prediction of tree density in the study area were at a lag size of 3000. The prediction error was smaller in the eastern part, all the way to the center of the study area.

The predictive performance of the cokriging approach was further compared to that of ordinary kriging as well as stepwise linear regression using the 1st order Mean texture measure for SPOT MS Band 3 data. Descriptive statistics of the datasets showed normal distribution for the sampled woody correlates as well as remotely sensed datasets. Chapter five presented the results obtained from geostatistical (variogram modeling and the kriging interpolations) analysis of the woody canopy cover and density as well as the 1st order Mean texture measure for SPOT MS Band 3.

However, the prediction error maps (Figure 5.3) showed high prediction error in the upper and lower western corners of the study area.

Figure 5.1: The isotropic variogram surfaces for measured %woody canopy cover (a) and  tree density (b) datasets
Figure 5.1: The isotropic variogram surfaces for measured %woody canopy cover (a) and tree density (b) datasets

Discussion

  • Comparison between the 10m SPOT5 MS and the 2.5m SPOT panmerged images used in Characterizing Woody cover and density
  • Relationship between SPOT5 multispectral vegetation indices and sampled Woody Variables
  • Image Texture Vs Woody Vegetation Cover and density Estimation
  • Modeling woody vegetation cover
  • Evaluation of the methods
  • Remote sensing and Geostatistics for Savanna Woody Vegetation Estimation

In this regard, the pan-merged SPOT image is a better predictor of the woody vegetation cover in the homogeneous mopane forest savannah, as shown in this study. In this regard, the high correlation observed for band 3 can be attributed to the multiscattering in band 3 for both SPOT multispectral and SPOT panmerged images. In this study, results obtained from linear correlation analysis for field-sampled woody vegetation parameters and SPOT5-derived vegetation indices at 10-meter resolution showed significant correlation coefficients (Table 4.2).

In this study, the assumption that resolution can influence the performance of the raw multispectral bands as well as the vegetation indices is based on high correlation obtained for 2.5 m resolution SPOT panmerged data compared to 10 m resolution SPOT5 multispectral data. In this study, analysis of SPOT5 multispectral satellite imagery at 10 m resolution has shown significant correlation coefficients with field-tested tree parameters as shown in Chapter Four and further discussed in Section 6.1. And in this study, texture measurements calculated on 10 m resolution SPOT5 multispectral image gave the highest correlation with the field observations.

Thus, Cokriging yielded the highest accuracy of estimating the primary variable (i.e. woody vegetation parameter) in this study.

Conclusion

  • Aim and Objectives re-examined
  • Limitations and Recommendations
  • Concluding Remarks

The results showed that the use of semivariogram to sample image data for cokriging offers great potential for future studies in this remote sensing niche to accurately estimate and map the spatial distribution of woody vegetation resources. The results showed that SPOT panmerged data with a resolution of 2.5 m is a better predictor of woody vegetation variables sampled in the field. Predict woody vegetation cover using geostatistical techniques (especially cokriging) with the best SPOT-derived spectral vegetation data or image texture measure.

This study has demonstrated that the utility of a combination of better vegetation data and geostatistics derived from SPOT via cokriging improves the estimation accuracy in woody savanna vegetation and spatial distribution. The differences in the strength of the correlation analysis between the 10m and 2.5m images with woody vegetation cover and density has shown to what extent the effect of spatial resolution can determine the spatial correlation or relationship between vegetation and its reflectance. To explore the full potential of the 10 m SPOT5 multispectral image data for assessing the relationship between woody vegetation and its reflectance data, different image transformation techniques are needed in addition to the use of raw spectral bands.

The implication of this study showed that combination of remote sensing and geostatistics for woody vegetation density and cover estimation can offer great potential for improving semi-arid savanna biophysical resources assessment as well as providing ways to monitor wildlife habitat.

Detecting structure and growth changes in forests and woodlands: the remote sensing challenge and the role of geometric-optical modeling. Shimoda (Eds.), The use of remote sensing in the modeling of forest productivity Dordrecht: Kluwer Academic Publishing., pp. Integrating remote sensing and spatial statistics to model herbaceous biomass distribution a tropical savanna International Journal of Remote Sensing.

An assessment of the potential for remote sensing of bark beetle-infested areas during a leafhopper attack: a literature review In: Department of Geography Working Paper University of Victoria Victoria, B.C. Remote sensing of nitrogen and lignin in Mediterranean vegetation from AVIRIS data: biochemical decomposition from structural signals. Using Remote Sensing Image Texture to Study Habitat Use Patterns: A Case Study Using the Polymorphic White-throated Sparrow (Zonotrichia albicollis).

Characterizing the Spatial Structure of Vegetation Communities in the Mojave Desert Using Geostatistical Techniques Computers and Geosciences.

Appendices

Woody Tree/Shrub Data Collection Form

Measure the skewness of the data set, if the skewness is 0, the histogram is equal about the mean (Materka & Stralecki 1998). Where xij is the digital number of the pixel( )i,j, and n is the number of pixels in the moving window (ERDAS, 1997). Contrast is a measure of the overall amount of local variation in a window (i.e. it is .. proportional to the range of gray levels) (Yuan et al. 1991).

A small value of the second moment indicates contrast in the texture of the image, while a large value of the second moment indicates that the image is quite homogeneous (Yuan et al. 1991). It can be used as a measure of the absence of distinct structure or organization of image patterns (Yuan et al. It takes into account the variability of the spectral response of pixels, but considers pairwise combinations of variability.

The correlation texture algorithm measures the linear dependence of the gray level within the image (Kaitakire et al.

Gambar

Figure 1.1: Flowchart for methods followed in this research  RS = remote sensing
Figure 1.2: Location of the Study Area in the Kruger National Park (KNP)- South Africa
Figure 3.1: Field Design and Data Collection
Table 3.1: List of materials  No.  Type of material  1.    Altimeter
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