Spatio- Temporal Technology Analysis for Urban Land Use Growth In The Case Of Mekelle City, Tigray, Northern Ethiopia

Hagos F

Published on: 2023-09-04

Abstract

This study aims was to assess the urban land use growth in city using Geo special Technology data, (three satellite images 2006, 2012, and 2018) to determine the extent of urban Land use analysis. After image pre-processing, to classify the images into four land use classes using Maximum Likelihood supervised classification technique. The ground truths found from field survey also used for image classification and to evaluate the accuracy assessment. Accordingly, the overall accuracy was calculated (88.5%). The outcomes of images classifies was in period 2006 – 2018 the total area was covers 32160.72ha. Those areas have four Land use Classes there were, bare lands 5977ha (18.52%), 5573ha (17.33%), and 5342ha (16.61%). In receptively year (2006, 2012 and 2018), urban Land use classes was 5183.45ha (16.12%), 5952ha (18.50%) and 6789.72ha (21.11%) in year (2006, 2012 and 2018), Vegetation covers 20165.35ha (62.70%), 19873ha (61.79%) and 19389.72ha (60.29%) (2006, 2012 and 2018) and water body coverage 854.92ha (2.66%), 762.72ha (2.37%) and 639.5ha (1.99%) (2006, 2012 and 2018) respectively. Due to the urban Land use process was in 2006, 5186.45ha, in 2012 increased to 5952ha and in 2018 the urban Land Use coverages 837.72ha to rapidly growth from the total area of 32160.72ha. Finally, 2006 to 2018 year the area was covered 1606.27ha.

Keywords

Mekelle city; Urban growth; Remote sensing; GIS

Introduction

The distinct utmost source of prosperous creation in history has been conversion of rural land in to urban land represents urbanization. This development occurred at a slower rate in earlier periods, and the shape of the city that resulted was dense. Nowadays, urbanization is more rapid [1]. Currently, urbanization is increasing in both developed and developing countries.

However, rapid urbanization, particularly the growth of large cities and the associated problem of unemployment, poverty and environment degradation pose difficult challenges in many developing countries. Furthermore, urbanization refers to process by which an increasing proportion of population comes to live in cities by growth and migration of population transformed from predominantly rural to urban area and closely associated with the level of economic activities, land-use/land-cover, population distribution and urban facilities [2]. In addition to this, urbanization is an endemic phenomenon that is causing significant town planning and service delivery challenges globally in most developing and emerging economies. According to Abebe [3], urbanization is the major driving force for population growth, modernization, economic growth and other development, there is an increasing concern about the effects of expanding cities and environment.

Urbanization is a process usually expanding and growing to its surrounding areas at the expense of nearby agricultural farmlands, the process of urban expansion involves both the internal reorganization and outward expansion of the physical structure of urban areas. Such process of urban expansion is a worldwide phenomenon, which could see in the history of all urban centres. Similarly, Ethiopia has a long history of urbanization that developed next to the ancient Egyptian civilization in East Africa: like; Axum, Gonder, Lalibela, Harar. Then finally, in the 1880s Addis Ababa has become the capital city of Ethiopia [4].

Currently, Ethiopia, has nine nationally recognized regional states; with each of them having its own capital city. Tigray region is one of these regional states, which is located in the northern part of Ethiopia, and its capital is Mekelle. Mekelle, the capital city (socio-economic and political centre) of Tigray regional state is also dynamic experiencing of rapid urban expansion and population growth. Urban growth is a spatial and demographic process and refers to the increased importance of towns and cities as concentrations of population within a particular economy or society. According to [5], the history of urban growth indicates that urban areas are the most dynamic places on the Earth’s surface. Despite their regional economic importance, urban growth has a considerable impact on the surrounding ecosystem. Most often, the trend of urban growth is towards the urban-rural-fringe where there are less built-up areas, irrigation and other water management systems. The uncontrolled urban growth and migration to the urban areas results in urban sprawl. Whether, the urban growth is good or bad depend on its pattern, process and consequences. Mekelle is one of the fast growing urban centres in the Tigray regional state, Ethiopia. The city has a significant spatial expansion, increasing in population growth, physical sizes and developmental activities such as building, road construction, and many other anthropogenic activities. The basic problem is that the rapid urbanizations have been one of the crucial issues of global change that affect the physical dimension of cities. Moreover, population migration from rural to urban areas is one of the most impacted for urban problems resulted from regional imbalances and causes uncontrolled urban growth. Therefore, understanding the dynamics of urban systems and evaluating the impacts of urban growth on the environment are needed [6]. According to the Municipal of Mekelle city, the future land-use was propose based on detailed investigation of relevant spatial factor, current growth trends of city and functional compatibles between various activities. However, no research has been conducted at Mekelle city with regard to Geo spatial Technology Analysis for urban growth modelling. Therefore, we fill this gap. We have main objective of this research was to detect, analyse and map urban sprawl expansion of Mekelle city by quantify the patterns of urban growth in different period using high resolution Multi-temporal aerial and satellite imageries. To find out the urban trends and magnitude of urban land use changes of years 2006 and 2018.

Research Materials And Methodology

Description of the Study Area

Mekelle is the capital city and commercial centre of the Tigray National Regional State in the northern Ethiopia. The city Mekelle was established as a national capital during Emperor Atse Yohannes the 4th era in 1864 E.C and got its urban structure during his region [7]. The altitude of Mekelle is between 1965 m and 2220 m above sea level. The city is located between latitude 13°24′ 30"-13°36′ 52'' N and Longitude 39°25′30"-39°38′ 33" E is situated in the central highlands of Ethiopia (Figure:1). Mekelle is a city in Ethiopia located at 784km drive north of national capital city, Addis Ababa. The area of the study covered about 32601.72 ha.

Figure 1: Study Area.

Research Data Collection And Analysis

Data Collection

Primary Data

Ground truth points, as an input for image classification and accuracy assessment, were we collected using Global Positioning System (GPS) from the ground. In addition, open and close ended questionnaire and field observations.

Landsat Imageries Data

For urban growth Land use modelling studies, appropriate selection of imagery acquisition dates is an integral component of the urban growth analysis. Consequently, cloud free Landsat data (2000-2018) with 30mx30m resolution downloaded from United States Geological Survey (http://earthexplorer.usgs.gov/) free after registration. The Landsat imagery of the study area includes Landsat Enhanced Thematic Mapper plus (ETM+) for 2006, 2012 and Landsat 8 (OLI) for 2018. In addition, Landsat 8 Operational Land Imager (OLI) consists of eleven spectral bands with a spatial resolution of 30 meters for Bands 1 to 7 and 9 for the year 2018 were included in the analysis.

Data Analysis

Image Classification and Urban Land-Use Mapping

Classification is a technique of developing interpreted maps from remotely sensed imagers, which requires a classification algorithms and scheme. The necessities for understanding urban sprawl are doing well urban land-use change detection. The amount of urban land-use changes as loss and gain were investigated by mapping the area for all study years through the process of classification. The urban land-use classes applied in this study were adapted urban land-use classification scheme which is widely applied in East African Countries [8] Moreover, land-use/land-cover classification scheme and visual interpretation, the following land-use class (Table: 1) are described for the study area considering the urban land use diversity.

Table 1: Urban Land Use Name and Descriptions.

No

                      Class Name                               

Description

1

Bare land

bare soil, Bare lands, vacant spaces etc.

2

Urban Area

Residential, industrials, Administration office etc.

3

Vegetation

farming area, Natural grasslands, forest, shrubs, wood lands etc.

4

Water Body

rivers, artificial Lake, ponds and marcher

Image Classification

GIS and remote sensing focusing on image classification has attracted the attention of many researchers and come to a number of studies have been carry out using different classification algorithms. However, image classification is the development of assigning pixels of continuous raster image to predefined urban land-use/land-cover classes. It should be noted that the valuable surface information extraction and analysis is also well-performed using image classification. It is time consuming and complex development, and the product of classification is likely to be affected by different factors such as algorithm, classification methods and nature of input data. Moreover, in order to improve the classification accuracy, selection of appropriate classification method is required. This would also enable analyst to detect changes successfully.

Supervised classification

Supervised classification was used, in this study, to cluster pixels in data sets in to classes corresponding to user defined training classes. This classification type requires selecting training area for use as the basis classification of the most common supervised classification techniques, maximum likelihood classifier for parametric rule was applies. Having prior acquaintance with the study area, in the present study, urban land use classes during the field visited.

Image Classification and Validation Techniques

Investigation of a number of the literature reviewed and the analyst's personal knowledge revealed that pixel-based classification produces consistent output. Image analysis technique that considers both the measured reflectance values and neighborhood relations (pixel-based analysis) are available in ERDAS Imagine and ArcGIS software packages. Such pixel-based schemes are essential for urban growth studies respectively.

Image Classification Validation

Accuracy assessment is significant for usual photographic remote sensing techniques, with the arrival of more advanced digital satellite remote sensing the necessity and possibility of performing advanced accuracy assessment have received new interest. According to [5], accuracy assessment is a development used to validate the accuracy of image classification by comparing the classified map with a reference data. Eventually, accuracy assessment was considered as an integral part of any image classification. This is because image classification using different classification algorithms may classify pixels or group of pixels to the wrong classes.

Producer’s Accuracy

Producer's accuracy is the possibility of a reference pixel being classified correctly. It was achieved by dividing the number of correctly classified pixels in the category by the total number of pixels of the category in the reference data. It also known as omission error because it only gives the proportion of the correctly classified pixels.

Overall Accuracy

Overall accuracy computed by dividing the total correct number of pixels summation of the diagonal to the total number of pixels in the matrix [9]. Various standard threshold levels were applied to the lower and higher tail of each distribution, in order to find the threshold value that produced the highest change classification accuracy. For this study, results shows that the achieved overall accuracy is the total classification accuracy, which is computed by dividing the total number of pixels summation of the diagonal, to the total number of pixels in matrix or grand total.

User's Accuracy

User's accuracy is the possibility of the pixels in the classified map characterizes that class on the ground [2]. It is achieve by dividing the total number of correctly classified pixels in the category by the total number of pixels on the classified data. Illustrates that the value of both the producer and user accuracies of each land-use/land-cover class for the three specified times.

Kappa Coefficient

Kappa Coefficient is an evaluated agreement used to evaluate the classification accuracy. According to [5], it was expresses the proportionate reduction in error generated by a classification process compared with the error of a completely random. The assessment of the study area was carry out using google earth and ground truth points from field observations the major sources of reference data. A set of reference points has to be generate to evaluated accuracy and stratified random points for each derived classes. These points were very the collected GCP data from the reference of ground area. The study also evaluated the accuracy of the 2006-2018 image classifications. The total points were 75 (40 for Urban area, 13 for Vegetation, 12 for bare lands, 10 for water body) truth ground data were taken and their land-cover were defined from field visual interpretation. The points were scattered throughout the study areas.

Urban Land-Use Change Analysis

After classified the Landsat images using supervised techniques; and measuring the classification accuracy, land use land cover change analysis was carried out. Change statistics was computed by comparing image values for the periods 2006–2012, 2012–2018, and 2004–2014 using the equation below.

Where: Area is extent/ coverage of the urban land use. Positive values suggest an increased whereas the negative values imply a decrease in extent.

Figure 2: General Methodology Flow Chart.

Results And Discussion

The Detecting Urban Land-Use/Land-Cover Change Detection Pattern

The classification of the Landsat satellite images for the three different times of 2006, 2012 and 2018 has resulted in a highly simplified and abstracted representation of the study area. The maps was presented a clear pattern of increased urban land use extending from the centre to all directions. However, growth is limited in the east direction because it was bounded by mountain choma. The study started out from classification, both land-use/land-cover classes (Bare lands, urban Area, Vegetation and Water bodies) have different spectral reflectance property and pattern. The bare lands area covers none of farming area, Urban Area also including all build up, road area, vegetation area is farming area, grass area, and green area includes and the water bodies cover the water areas.

Figure 3: Urban Land Use Maps for 2006 and 2012.

Figure 4: Urban Land Use for 2018.

Accordingly the urban land use classification show in (figure2 – figure3), above and Table1 blow the total area of the study was covers 32160.72ha the land use land cover have those bare lands 5977.00ha (18.52%), 5573ha (17.33%), and 5342ha(16.61%).

In receptively year (2006, 2012 and 2018), urban Land use classes was 5183.45ha (16.12%), 5952ha (18.50%) and 6789.72ha (21.11%) in year (2006, 2012 and 2018), Vegetation covers 20165.35ha (62.70%), 19873ha (61.79%) and 19389.72ha (60.29%) (2006, 2012 and 2018) and water body coverage 854.92ha (2.66%), 762.72ha (2.37%) and 639.5ha (1.99%) (2006, 2012 and 2018) respectively.

Table 2: Table: Urban Land-Use Area In Year 2006-2018.


Urban Land Use Area in Ha in 2006 -2018

 

2006

2012

2018

Class Name

Area (ha)

%

Area (ha)

%

Area (ha)

%

Bare lads

5957.00

18.52

5573

17.33

5342

16.61

Urban Area

5183.45

16.12

5952

18.50

6789.72

21.11

Vegetation

20165.35

62.70

19873

61.79

19389.5

60.29

Water body

854.92

2.66

762.72

2.37

639.5

1.99

Accuracy Assessment of Urban Land-Use Classification

The accuracy is essentially a measure of how many ground truth pixels was classify correctly. An error report containing the error matrix and accuracy report summarizing the agreement and disagreement were produce. The ground truth data were utilize the classification report as the independent data set from which the classification accuracy was compare. An overall accuracy of 86.0%, 87.32% and 89.50% achieved with a Kappa coefficient of 0.77, 0.84, and 0.85 for the three satellite images. The overall accuracy is a similar average with the accuracy of each class weighted by the population of test samples for that class in the total training or testing sets. Thus, the overall accuracy is a more accurate estimate of accuracy. The Kappa coefficient represents the proportion of agreement obtained after removing the proportion of agreement that expected to occur by chance. The kappa coefficient lies typically on a scale between 0 and 1, where the latter indicates complete agreement, and is often multiplied by 100 to give a percentage measure of classification accuracy.

Table 3: Over All Accuracy Assessment for Urban Land Use Classification in 2006, 2012 And 2018.

Years

Overall Accuracy

Kappa

2006

86.0%

0.77

2012

87.32%

0.84

2018

89.50

0.85

Urban Land use Change Analysis

The significant aspect of change detection is to determine what is actually changing and which land use class is changing to the other. This information was served as an essential tool in decisions makers. Change detection is the process of identifying differences in the state of an object or phenomenon by observing it at different times [10]. Change detection is an important process in monitoring and managing natural resources and urban development because it provides quantitative analysis of the spatial distribution of the activities of interest. The results of urban land use changes was shown in (Table 4) in the period's 2012-2018.

Table 4: Table Urban Land Use Classes and Rate of Change 2006 – 2018.

Urban Land use change 2006 -2018 in ha (%)

 

2006- 2012

2012 - 2018

2006 -2018

Class Name

Area (ha)

% coverage

Area (ha)

% coverage

Area (ha)

% coverage

Bare lads

-384

-1.19

-231

-0.72

-615

-1.91

Urban Area

768.55

2.39

837.72

2.6

1606.27

499

Vegetation

-292.35

-0.91

-483.5

-1.5

-775.85

-2.41

Water body

-92.2

-0.29

-123.22

-0.38

-215.42

-0.67

Total Area

32160.72

100

32160.72

100

32160.72

100

Urban Land Use classes Rate in Hectares

The rate of urban land use classes for the specified period calculated using the method devised by [9], the rate of urban expansion from 2006-2012, 2012-2018, and 2006-2018 is respectively. From this result, we can accomplish the rate of urban land use from 2006 to 2018 with an interval of 6 years. Through the analysis capabilities the GIS, we were calculated approximate Hectares for urban Land use Classes from 2006 to 2018year. In year of 2006, the Urban Land use covers 5186.45 hectares from the total area for the bounders. In year 2012 the urban Land use also increasing to 5952 hectares and or the year of 2018 the Land Use coverages 837.72 hectares from the total area of 32160.72 hectares and finally 2006 to 2018 years has covered 1606.27 hectares. Therefore, the urban land use increased from time to time sow in table below. 

Table 5: Urban Land Use Classes in Hectares.

Year

Urban Land Classes

Rate Of Urban Land Use Classes In Hectares

2006

5183.45

2006 –2012

 2012–2018

2006–2018

2012

5952

768.55ha

 

 

2018

6789.72

 

837.72ha

 

Change in ha/year

 

 

 

1606.27ha

Conclusion

The study was carry out to investigate the overall urban land-use changes occurred from 2006 to 2018 year. As the purpose of the study was to look at urban land-use map visualized and extracted. The Landsat image classified, a remarkable the urban land use trends was observe in Mekelle city.  Rapid trend was between 2006 to 2018 year. The results of images classifies from 2012-2018 urban Land Use classes was increasing from 2.39%, 2.60% (2012 and 2018), Bare lands was decreased from time to time -1.19%, -0.72% and -1.91% (2006, 2012 and 2018), Vegetation areas was also decreased in percentage from the total coverages -91%, - 1.50% and -.42% (2006, 2012 and 2018) and the water body was decline -0.29%, -0.38% and -0.67%. Finally, it was observed that the analysis of urban land-use development using remote sensing data is accurate, rapid, and cheap and release with repetitive coverage. Therefore, the strategy advocates the implementation of higher residential densities. The urban growth is a development strategy that serves the community, economy and the environment. The study may help for decision makers, Land Administrator and planners to consider the impacts of disorganized urban development by identifying the current trend of urban land-use growth potentiality.

Acknowledgements

I am thankful to municipality of Mekelle city, urban land development and urban planning, for their kind and collaborative effort in providing the needed document to my thesis. My heartfelt thanks go to my friends and colleagues; Last, I would like to thank all my family who helped me in various ways to make the writing my thesis possible.

References