dc.contributor.advisor |
Combrinck, Ludwig |
|
dc.contributor.coadvisor |
Botai, J.O. (Joel Ongego) |
|
dc.contributor.postgraduate |
Mbwia, Lisa Nyadzua |
|
dc.date.accessioned |
2018-12-05T08:04:59Z |
|
dc.date.available |
2018-12-05T08:04:59Z |
|
dc.date.created |
2009/04/18 |
|
dc.date.issued |
2018 |
|
dc.description |
Dissertation (MSc)--University of Pretoria, 2018. |
|
dc.description.abstract |
The focus of this research was to determine the multi-temporal land cover changes (LCC) of the Hartebeesthoek Radio Astronomy Observatory (HartRAO) environment over 5 decades. The HartRAO site is a strategic point in the mapping system of South Africa and acts as fundamental reference node in the International Terrestrial Reference Frame (ITRF). In this study, the conducted field assessments determined the land cover type of the study area and its environment. The use of aerial photographs, Google Earth images, satellite images and climate data were platforms to assess the LCC of the area and surroundings. The ENVI 5.1 software package was used to determine the LCC of the area from the Landsat TM and Landsat OLI satellites using image analysis. In addition, ArcGIS 10.2 was used to determine the hydrology of the area from the SRTM DEM file, provide a platform to view aerial photographs, and map out LC images determined from ENVI 5.1. Field assessments and demarcation of the study area were conducted using Google Earth images. The e-Water TREND software proved useful in determining the statistical significance of climate data over 5 the decade period. Microsoft Excel software was used to tabulate, generate graphs and charts from satellite image and climate data analysis.
According to the first objective the delineation of land cover types in the area was done using aerial photographs and field assessments of the study provided pictorial information to interpret land cover changes over the years of the study. Analysis of satellite data for the last 19 years also showed the changes in the land cover type and this was used to delineate land cover types. This was followed by satellite image processing and analysis over the last 19 years involving: image ratioing, image classification, change detection and accuracy assessment. Trends in rainfall and temperature of the area over period in the study area were determined using climatic data. Combining primary and secondary data to provide visual interpretation on the changes in land cover type and the seasonal variability were tools identified for the study. Hence there is a note that there is an increase in woody vegetation within HartRAO and changes in land cover and land use activity which does affect the changes in climate and land cover type.
Image processing: image ratioing of the Landsat TM and Landsat OLI images, the EVI, NDVI, NDBI and NDBaI spectral indices were used to give an overview of the land cover type and coverage in the area using the ENVI 5.1 software. A supervised image classification technique (pixel-based) was the ideal method for the Landsat images in this study this is because of the variability of the land cover type and when analysing will depend on spectral information. The second and third objective focuses on remote sensing techniques, where there is an importance in removing biasness when comparing of classification algorithms to determine the most suitable algorithm for image classification. Therefore in the study maximum-likelihood (parametric) and support vector machine (non-parametric) classification algorithms were used to determine the extent of the land cover type in the area. Change detection in the study was used to determine the level of changes within and between the land cover type in the area of study. The aim of accuracy assessment is to determine the performance of the classification algorithms based on the land cover type. This proved that both performed well but SVM had a slightly higher accuracy with most land cover types and as part of the study, classification algorithms can be used individually while assessing specific land cover types.
By combining the first three objectives together, the results and discussion draw us to the fourth objective which brings us to what the changes in the land cover are caused by, and the rate of changes. In the results and discussion chapter by interpreting aerial photographs, Google Earth images and field assessment images and data illustrate there is an increase of vegetation within the immediate HartRAO environment. Surrounding areas of HartRAO indicate an increase in the proportion of agricultural land, and an increase of bare-lands due to mining activities within the surrounding areas. Outcomes from climatic data analysis conducted through the Mann-Kendall test using the e-Water TREND software indicated an increasing trend (mean annual temperatures) for the first normal of the years in the study. Climate data analysis of the second normal indicates that MATmax has an increasing trend. While MATmin and TAR are decreasing with a statistical significance at 95% confidence interval of Z = -2.194 and -1.998 respectively.
Utilizing satellite image analysis, image ratioing shows that there is an increase in vegetation ratio results in both NDVI and EVI. The NDVI images have higher values than EVI images for the Landsat TM while EVI have higher values in Landsat OLI as recognized in the summer images and winter images. The NDBI is higher which does not depict what the area is, as the built-up index reflects the milky-quartz rocks as built-up structures. The NDBaI is lower in the study. From the image classification results, the ML classification algorithm classifies forests and grasslands well. In SVM the scattered vegetation and grasslands are classified well. Both classification algorithms provide poor results for the milky-quartz with scattered vegetation and shale-rock with scattered vegetation. In relation to the accuracy of the ML and SVM classification, both had higher accuracies when classifying the Landsat summer images with values above 90% and overall accuracy for winter images was between 82% - 90%. However, the July 2007 satellite images had the lowest overall accuracies for both ML and SVM classification algorithms. There is a negative annual rate of change for all the land cover types throughout the years (1960 - 2017) the study covers. A higher negative value from the rate of change is illustrated from the grassland cover type for all summer and winter images used in the study. The forestland cover and built-up land cover type has an increase in negative change noted from the classification of the winter images. Comparison of both classification algorithms using Chi-square test illustrate no statistical significance, which concludes that both perform equally well in terms of overall accuracy and land cover. |
|
dc.description.availability |
Unrestricted |
|
dc.description.degree |
MSc |
|
dc.description.department |
Geography, Geoinformatics and Meteorology |
|
dc.identifier.citation |
Mbwia, LN 2018, Analysis of land cover changes of the Hartebeesthoek Radio Astronomy Observatory environment over five decades, MSc Dissertation, University of Pretoria, Pretoria, viewed yymmdd <http://hdl.handle.net/2263/67803> |
|
dc.identifier.other |
S2018 |
|
dc.identifier.uri |
http://hdl.handle.net/2263/67803 |
|
dc.language.iso |
en |
|
dc.publisher |
University of Pretoria |
|
dc.rights |
© 2018 University of Pretoria. All rights reserved. The copyright in this work vests in the University of Pretoria. No part of this work may be reproduced or transmitted in any form or by any means, without the prior written permission of the University of Pretoria. |
|
dc.subject |
Unrestricted |
|
dc.subject |
UCTD |
|
dc.title |
Analysis of land cover changes of the Hartebeesthoek Radio Astronomy Observatory environment over five decades |
|
dc.type |
Dissertation |
|