Modelling Urban Green Spaces Depletion in Akure, Nigeria
MICHAEL AJIDE OYINLOYE1, CHIAMAKA LOVELYN OLISA2, BABATOPE SUNDAY OLISA3
1,2 Department of Urban and Regional Planning, Federal University of Technology, Akure, NIGERIA.
3Department of Transport Management Technology, Federal University of Technology, Akure, NIGERIA
Abstract: The fast progress of urbanization and the accompanying dominance of concrete spaces over
natural spaces are fundamental to current debates on urban planning and sustainable development in Nigeria
and the world at large. It is worth noting that natural landscapes and greenery are critical to man's quality
of life; yet, the majority of the population are going to reside in urban areas, to the detriment of urban green
spaces, known as the "lungs of the city." A detailed account urban green spaces in Akure. Using Geographic
Information System (GIS) and remote sensing techniques needs to be done. This study examines the status
of urban green spaces in Akure, Nigeria to determine the rate of depletion and encroachment green spaces.
The spatio-temporal analysis of green spaces in Akure was carried out between 1984 and 2022 using
Supervised maximum likelihood classification procedure on Landsat 8 OLI/TIRS, Landsat 7 EMT+ and
Landsat 4-5 TM Imageries. It took cognizance of attributes of vegetative cover at varying degrees such as
Grasses and Shrubs, Light Vegetation, Secondary Vegetation, and Dense Vegetation. The rate of depletion
of green areas, change statistic, socio-economic implication as well as planning implications were
addressed. It is believed that assessing and analyzing its social, economic, and environmental impacts on
urban inhabitants and their livelihoods would serve as a tool to educate and enlighten urban citizens about
the need of including green space scheme into urban designs and planning in Akure.
Keywords: urbanization, green, spaces, depletion, sustainable, encroachment, landscapes
Received: November 25, 2022. Revised: August 21, 2023. Accepted: September 15, 2023. Published: November 7, 2023.
1. Introduction
Global urban discourse is of utmost concern as
regards urbanization and its associated negative
repercussions. With the majority of the world's
population desiring to and yearning to live in
cities, the trend of urbanization is accelerating at
an alarming rate. The global urbanization trend is
accelerating, with cities currently housing the
majority of the world's population. Cities and
their decision-makers face numerous complicated
challenges today in balancing urban expansion
and its environmental impact. Consequently, the
demand for new infrastructure construction is
expected to increase commensurately (Dreiseitl,
Wanschura, Wörlen, Moldaschl, & Wescoat,
2016); in the view of this, land and space
developments in cities have led to complex
challenges that are associated with balancing the
planning and sustainability of landuses
(Enoguanbhor, 2021).
According to Liu et al. (2021), increased landuse
development, particularly in urban areas, has
resulted in a decrease in green spaces;
construction of buildings, roads, transportation
terminals, bridges, land reclamation, and concrete
platforms are taking the place of greens
(vegetation). Complex population changes,
urbanization dynamics, climate change, and
environmental degradation have all become
important challenges that urban planners must
address immediately. In a rising climate, urban
environmental stresses are exacerbated by
population growth and the induced development
of structures such as grey infrastructure, which
typically leaves limited space for green elements
and processes (Sanjana, et al. 2019). The rate of
green spaces depletion and the accelerated rate of
encroachment of urban land use on the urban
green remains a crucial subject matter to physical
developments of urban areas. There is need to
maintain a balance in the land use allocation and
International Journal of Environmental Engineering and Development
DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
134
Volume 1, 2023
planning as city grows and alters its urban
ecosystems.
Omole et al (2018) pointed out that cities in
developing nations like Nigeria are known with a
common trait of uncoordinated development
leading to urban sprawl and while urban centers
are rapidly and haphazardly growing their spatial
planning and management strategies remain
largely underdeveloped (Omole, Enisan,
Adeniran, & Adebisi, 2018). According to
Olanrewaju and Oyinloye asserted that livability
constitutes one of the failures of Nigeria urban
centers and this is blamed on the “process of our
development (Olanrewaju & Oyinloye, 2018).
Rakhshandehroo et al., (2015) divulged that there
is a rapid process of urbanization and subsequent
domination of concrete spaces over natural
spaces; since natural landscape and greenery are
crucially important to our quality of life and the
majority of the population are going to settle
down in urban areas, urban open green spaces as
the ‘lungs of the city’ should be at the center of
the debate on any urban planning and sustainable
development (Rakhshandehroo, Mohdyusof,
Tahirholder, & Yunos, 2015). However, Owoeye
& Ibitoye (2016) revealed that the existing Master
plan of Akure was produced in 1980 and has
become inactive, old, and superseded; they
suggested that a review of the comprehensive
regional plan to guide the development and
spatial growth of the entire region (Owoeye &
Ibitoye, 2016).
Urban Green spaces in Akure took a back seat and
is seldom given required attention due to
competing economic interests and demand on
land for various purposes such as residential,
commercial, industrial and institutional
(Oyinloye, 2013). In the view of this, green
spaces in the city suffer land availability,
distribution, quantity, quality, accessibility, lack
of intended purpose and stakeholder
participation. In this study, green spaces are seen
as publicly accessible and private green space,
natural or incidental green space (remnants of
native vegetation). Examples of these elements
include grassed areas, rain gardens, trees, shrubs,
gallery forest, parks and vegetated waters. The
escalating depletion of urban green spaces is of
global major concern; hence the need for policy
makers and planners in emphasizing and adopting
measures to restore green and natural spaces.
Liu, Xiu, & Song, (2019) opined that earth
systems are urbanized at an unsustainable pace,
ecosystems and biodiversity undergo large-scale
destruction and human well-being is threatened
(Liu, Xiu, & Song, 2019). Due to this
phenomenon, urban areas are experiencing
unprecedented challenges which are the resultant
effects of urbanization progression; in this case
Akure is no exception. The study aims to monitor
the depletion of urban green spaces within Akure
metropolis in order to enhance its preservation,
conservation and effect management which is
germane to livability, resilience and sustainability
of an urban center; which is the core interest of
this study. Thus, idea is critical towards ensuring
the long-term sustainability of nature and people
living in urban area and achieving the Sustainable
Development Goals, especially Goal 11. This
study also assesses the urban green spaces with a
view of developing a model showing changing
patterns of green depletion in Akure metropolis
and determining the rate of green space depletion
in the study area.
The specific objectives of this study are to:
a) assess the spatio-temporal pattern of green
spaces in the study area between 1984 and
2022;
b) examine the rate of depletion of green
spaces in the study area; and
c) ascertain the planning implications of
green spaces depletion in Akure.
2. The Study Area
Akure is the study area of this research work. The
spatio-temporal pattern of green spaces in Akure
International Journal of Environmental Engineering and Development
DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
135
metropolis covered a period of 38 years (between
1984 and 2022). 1984 was chosen as the base year
for this study due to the availability of imagery in
the archive (Landsat Images, United State
Geologic Survey). Akure is a city situated in the
south-western Nigeria, and is the largest city and
capital of Ondo State. Akure is a city in Nigeria
located on longitude 5.081 to 5.487 decimal
degree and latitude 7.078 to 7.436 decimal
degree, with a population of 360,268 persons in
2006 (National Population of Commission, NPC,
2006). The vegetation type of Akure is forest
vegetation, which is categorized as: forests,
Gallery forests and Forest reserves. In these
forests, typical rain forest trees such as
Mahogany, Obeche, Iroko, Afara, etc. are present
and used for timber. Other economic trees include
African pear, Bamboo, Raffia palm, Oil palm,
Orange, Mango and Coconut. The persistent
clearance of the vegetation in and around Akure
has led to the development of derived forest
around the town (Fadairo, 2008).
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Figure 1: Map of Akure in its National Setting
Source: Ondo State Ministry of Physical Planning and Urban Development,
International Journal of Environmental Engineering and Development
DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
136
AKOKO NORTH
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Figure 2: Map of Akure in its regional setting
3. Data Acquisition and
Methodology
The study is interested in modelling the changing
patterns of green space depletion in Akure. The
study deployed method of analysis which include
map analysis involving geo-data collection and
analysis of spatio-temporal pattern of green
spaces. The sources of data used for the study
were secondary sources. Published and
unpublished materials were consulted for the
study. To achieve the study’s goal, Geospatial
data analysis was conducted on the
landuse/Landcover cover change for a period of
38 years (1984-2022). The Satellite imageries of
Akure were acquired for 1984, 1991,2002, 2015
and 2022 and processed. The processes included
image composition, rectification, enhancement
and classification. These satellite imageries
underwent process of image classification in
order to complement the visual analysis of the
image data with quantitative techniques for
automating the identification of features in the
study area. For the purpose of this study, attention
was focused on analysis of greens and non-green
spaces. Supervised maximum likelihood
classification procedure on Landsat 8 OLI/TIRS,
Landsat 7 EMT+ and Landsat 4-5 TM Imageries
was used to determine the green spaces identity
of each pixel in the Landsat imagery as well as its
rate of depletion. A supervised classification with
a Maximum Likelihood analysis was successful
after creating six classes of interest with training
sample area per class. These included: built-up,
bare surface, grasses and shrubs, light vegetation,
Secondary vegetation, and dense vegetation
categories as regions of interest. Descriptive
analysis was done to present change detection
results and other the change statistical data.
4. Results and Discussion
The study uncovered changes in Akure
metropolis' green spaces (vegetative covers) and
built-up regions between 1984 and 2022. The
Figure 3: Map of Akure Township showing network of
waterbodies and major roads; Source: Adapted from
Google Earth Map source (Digitized by the Author, 2022)
International Journal of Environmental Engineering and Development
DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
137
study spanned 38 years, as demonstrated by the
tables1 and maps of 1984, 1991, 2002, 2015, and
2022. However, the total area of each class was
computed. Table 1 shows a breakdown of the
area coverage in terms of percentages of
vegetative cover and built-up area under
consideration.
Table 1: Estimation of area coverage of Green space classes and built-up area between
1984 and 2022.
Classes
Area (sqm)
Area (km2)
Area (%)
1984
Built-Up area
12,531,600
12.5316
6.99
Grasses and Shrubs
36,630,900
36.6309
20.42
Light Vegetation
42,490,800
42.4908
23.68
Secondary Vegetation
18,474,300
18.4743
10.30
Dense Vegetation
68,781,600
68.7816
38.34
Bare Surface
492,300
0.4923
0.27
Total area
179,401,500
179.4015
100.00
1991
Built-Up area
20,871,900
20.8719
11.63
Bare surface
4,504,500
4.5045
2.51
Grasses and Shrubs
17,454,600
17.4546
9.73
Light Vegetation
60,577,200
60.5772
33.77
Secondary Vegetation
13,202,100
13.2021
7.36
Dense Vegetation
62,791,200
62.7912
35.00
Total area
179,401,500
179.4015
100.00
2002
Built-Up area
40,365,000
40.365
22.49981
Bare surface
2,792,700
2.7927
1.556676
Grasses and Shrubs
42,307,200
42.3072
23.58241
Light Vegetation
41,787,000
41.787
23.29245
Secondary Vegetation
44,425,800
44.4258
24.76334
Dense Vegetation
7,723,800
7.7238
4.305315
Total area
179,401,500
179.4015
100.00
2015
Built-Up area
57,412,800
57.4128
32.00
Bare surface
8,393,400
8.3934
4.68
Grasses and Shrubs
80,508,600
80.5086
44.88
Light Vegetation
11,778,300
11.7783
6.57
Secondary Vegetation
18,711,000
18.7110
10.43
Dense Vegetation
2,597,400
2.5974
1.45
Total area
179,401,500
179.4015
100.00
2022
Built-Up area
118,674,900
118.6749
66.15045
Bare surface
29,179,800
29.1798
16.26508
Grasses and Shrubs
3,869,100
3.8691
2.156671
Light Vegetation
9,878,400
9.8784
5.506308
Secondary Vegetation
17,029,800
17.0298
9.492563
Dense Vegetation
769,500
0.7695
0.428926
Total area
179,401,500
179.4015
100.00
Source: Field work, 2022
The total land area of the study is 179.4015sqkm
covering the nine political wards bouudaries in
Akure metropolis. The study is subjected to
capturing the landuse/landcover attributes within
Akure metropolis taking into consideration six
training areas such built-up, bare surface, grasses
and shrubs, light vegetation, Secondary
vegetation, and dense vegetation. The study
revealed that the built-up area was 6.99%
(12.531sqkm) of the total area covered
(179.4sqkm) in 1984; dense vegetation had the
largest percentage land cover with 38.34%
(68.782sqkm), this was followed by light
vegetation with 23.68% (approximately
42.4908sqkm). Grasses/shrubs and secondary
vegetation covered 20.42% (36.631sqkm) and
International Journal of Environmental Engineering and Development
DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
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10.30% (18.474sqkm) of the total landmass of the
study area (Akure) respectively as shown in table
1. Bare surface was 0.27% (0.492sqkm) as at
1984 and this can be attributable to dominance of
vegetative covers in Akure. Akure was found to
be an agrarian region where huge population
depended on farming/agricultural practices. It is
in the history that the engagement of the people
of Akure in cocoa, oil palm and yam farming
were very significant due to their traditions and
culture.
Figure 4 shows the image classification of green
space attributes and their spatial distribution in
the study area (Akure) in 1984. The figure depicts
a concentric picture of image classes having the
built-up area at center surrounded by
grasses/shrubs, light vegetation, secondary and
dense vegetation consistently; with few bare
surface areas. The image indicated high
prevalence of green spaces in Akure as at 1984.
Figure 4: The image classification and chart green space attributes and built-up areas of Akure in 1984
Source: Author, 2022
Findings revealed a 66.6% increase in the area
covered by the built-up class within a period of 7
years. As shown in table 1 as at December, 1991.
Built-up area had covered 11.63% (20.87sqkm)
of the total area of the Akure metropolis. This
showed a significant reduction of grasses and
shrubs area coverage, light vegetation and
secondary vegetation. Figure 5 shows appearance
of more bare surface area with 2.1.51%
(4.51sqkm); dense vegetation had a slight
reduction from 38.34% (68.78sqkm) in 1984 to
35% (62.79sqkm) in 1991. The massive loss of
area coverage in the light vegetation was gained
to light vegetation; hence, secondary vegetation
lost some square kilometres of land to the light
vegetation.
12,5316
0,4923
36,6309
42,4908
18,4743
68,7816
6,99
0,27
20,42
23,68
10,3
38,34
020 40 60 80
Built-Up area
Bare Surface
Grasses and Shrubs
Light Vegetation
Secondary Vegetation
Dense Vegetation
% Area (sqkm)
International Journal of Environmental Engineering and Development
DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
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Grasses and shrub class lost some coverage of
land to built-up area; Secondary vegetation lost
large portions of landcover to the light vegetation;
this shows a significant drift and encroachment
into vegetation reserves (dense and secondary
vegetation). However, this can be attributed to
increase in physical development being triggered
by urbanization and population density. The
figure 5 shows the extent of built-up
encroachment and the depletion of green spaces
in the study area. The built-up area had a
significant spread onto the grasses and shrubs as
well as light vegetation areas initiating
appearance of bare surface areas such as open
grounds, rock outcrops and stones features in red
color as shown in figure 5. The chart indicates
significant variations in the previous years’ data
result and the year 1991 findings where light
vegetation lost substantial land cover.
Figure 5: The image classification and chart green space attributes and built-up areas of Akure in 1991
Source: Author, 2022
As shown in table 1, built-up area in the year 2002
increased significantly with 93.4% rise. The area
coverage of built-up area as at 2002 was 22.5%
(40.365sqkm) of 179.401sqkm. This study
showed that there were substantial loss of
vegetation covers and their status within a span of
eleven years. Dense vegetation which the largest
area coverage in 1984 and 1991 lost its status with
an extreme reduction to 4.31% of total area of the
study area (Akure). This shift was taken over by
secondary vegetation, light vegetation and
grasses and shrubs with 24.7% (44.4sqkm),
23.3% (41.787sqkm) and 23.6% (42.307sqkm)
respectively. Between 1991 and 2002, there was
20,8719
4,5045
17,4546
60,5772
13,2021
62,7912
11,63
2,51
9,73
33,77
7,36
35
020 40 60 80
Built-Up
area
Bare surface
Grasses and
Shrubs
Light
Vegetation
Secondary
Vegetation
Dense
Vegetation
% Area (sqkm)
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influx of people into farming practices due to
stress on the economy, thus, dense vegetation was
encroached into, tall and canopy trees were
destroyed, as well as cocoa plantation and
replaced with arable farm crops. Light vegetation
expanded and spread into secondary vegetation,
while the secondary vegetation also enlarged into
the dense vegetation. However, due to land
clearance, physical development and cultivation,
rock outcrops and bare land surface were exposed
leading to appearance of bare surface class area
coverage with 1.56% (2.78sqkm). Dense
vegetation reduced from 38.34% (68.782sqkm) in
1984 to 4.31% (7.724sqkm) in 2002. The massive
loss of area coverage in the dense vegetation was
gained to secondary vegetation; hence, secondary
vegetation lost some square kilometres of land to
the light vegetation.
Even though the class of grasses and shrubs lost
some land to built-up area in 2002, a bigger
portion of land space was reclaimed from light
vegetation; while light vegetation had a drift and
encroachment onto forest reserves (dense and
secondary vegetation). However, this can be
attributed to increase in physical development
triggered by urbanization and population density.
The rate of vegetation loss in Akure is significant,
which necessitates investigation by those with a
stake in the matter. Figure 6 shows graphical and
spatial representations of the amount of the loss
of green spaces as well as the factors that have
contributed to this loss. It demonstrates the
degree of invasion by the built environment and
the reduction of green spaces in the study area.
The built-up area had a significant spread onto the
grasses and shrubs as well as light vegetation
areas instigating appearance of bare surface areas
such as open grounds, rock outcrops and stones
features in red color as shown in figure 6. The
chart indicates significant variations in the area
coverages of the classes of vegetation and built-
up area.
Figure 6: The image classification and chart green space attributes and built-up areas of Akure in 2002
Source: Author, 2022
40,365
2,7927
42,3072
41,787
44,4258
7,7238
22,50
1,56
23,58
23,29
24,76
4,31
010 20 30 40 50
Built-Up area
Bare surface
Grasses and Shrubs
Light Vegetation
Secondary Vegetation
Dense Vegetation
% Area (sqkm)
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In the year 2015, it was recorded that the built-up
area had a significant change in term of spatial
expansion into light vegetation as well as areas
covered by grasses and shrubs. Cultivated land
are being replaced with building and
construction. Anthropogenic activities caused
disappearance of lots of vegetation cover in the
study area as shown in the figure 7. The built-up
area in brown color became obvious on the
image; though, the figure shows a dominance of
green spaces being grasses/shrubs and light
vegetation. The chart in the figure 7 indicated an
intensification of land exposure to bare surface
with 4.68% (8.393sqkm) and a substantial
increase in the Built-up area with 37%
(57.413sqkm) out of 179.4045sqkm. The
degradation of natural vegetation cover in Akure
is attributable to population growth and urban
sprawl resulting to anthropogenic activities most
especially on the species of plants and trees in the
forest. It is important to note that the current pace
of vegetative extinction caused by humans is
believed to be higher than the background rate of
extinction that was likely caused by farming and
cultivation methods in the past. This is in
agreement with Adel Moatamed (2021), who
claimed that urbanization caused by economic
development and accelerated population growth
puts pressure on the populated land areas and thus
determines the pattern, direction, and rate of
change influencing the green spaces/landscapes.
Construction of concrete projects, mining in the
forest, and deforestation projects all contribute to
this enormous degradation of natural vegetative
components. This claim, however, is
corroborated by the distribution of green areas on
the spatiotemporal classified image for 2015 (see
figure 7).
Figure 7: The image classification and chart green space attributes and built-up areas of Akure in 2015
Source: Author, 2022
57,4128
8,3934
80,5086
11,7783
18,711
2,5974
32
4,68
44,88
6,57
10,43
1,45
050 100
Built-Up area
Bare surface
Grasses and Shrubs
Light Vegetation
Secondary Vegetation
Dense Vegetation
% Area (sqkm)
International Journal of Environmental Engineering and Development
DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
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Babatope Sunday Olisa
E-ISSN: 2945-1159
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Figure 8 and Table 1 revealed extensive
dominance of built-up area and ample
disappearance of dense and secondary vegetation
in Akure metropolis as at year 2022. Findings
revealed that significant amount of urban green
spaces was lost to built-up area between 2015 and
2022; built-up area had 106.7% increase in area
coverage. Grasses and shrubs, light, secondary
and dense vegetation showed a colossal loss in
land coverage. This loss is evident in dense
vegetation revealing ample disappearance to
0.43% of the total land area of Akure metropolis.
As shown in Figure 6, Secondary and
grasses/shrub which had a substantial land
coverage of 51.91% and 28.63% of the total land
area of 179.4015sqkm respectively as at 1984;
was left with 9.49% and 2.16%. The dominance
of Built-up area in brown color is conspicuous on
the 2022 image classification indicating the
magnitude of the spread of physical development
in Akure. This calls for attention of urban
planners, politician, decision makers and all
stakeholders in the sector to assuage the
disappearance of green spaces in Akure.
Figure 8: The image classification and chart green space attributes and built-up areas of Akure in 2022
Source: Author, 2022
This study reveals the extent of depletion in all
classes of urban green spaces within a confined
border of Akure metropolis. This was done to see
and know what is lost and what is left of the urban
green spaces of Akure metropolis. The chart and
image below indicated that bareland surface
increased as more rock outcrops and land are
exposed due to anthropogenic activities in Akure
with 16.27% (29.18sqkm) area covered. The
chart below indicates the pattern of skewness of
built-up area and green space distribution. The
rise in the magnitude of frequency coverage is
skewed to the side of built-up area.
5. Comparative Analysis of Green
space depletion
Comparing the vegetative cover of Akure in 1984
(the base year for the study) with the built-up
area, it can be inferred that vegetative cover had
a complete dominance of 92.74% of the total
landmass of Akure over the built-up area and bare
118,6749
29,1798
3,8691
9,8784
17,0298
0,7695
66,15
16,27
2,16
5,51
9,49
0,43
050 100 150
Built-Up area
Bare surface
Grasses and Shrubs
Light Vegetation
Secondary Vegetation
Dense Vegetation
% Area (sqkm)
International Journal of Environmental Engineering and Development
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Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
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surface. In 1984, Akure was eight years old as the
capital city of Ondo state; physical developments
were still in the early stages, with the majority of
the resident engaged in subsistence farming and
cocoa cultivation in the light and secondary
forest. There were high degree and agricultural
practices despite low population density. Akure
population was dominated by farmers and civil
servants who also engage in farming. Farming
beside and at backyards of residences were most
prevalent. However, trend analysis revealed that
the Akure metropolis' built-up area began to
expand and rise in density over decades, while its
green spaces depleted significantly at a
decreasing rate. Landuse developments and
expansion in Akure metropolis are taking place at
the detriment of green spaces. The considerable
and rapid loss in dense, secondary, and light
vegetation, as well as grasses and shrubs, around
the concentric boundaries of Akure metropolis'
built-up area has put strain on the city's natural
ecosystems. Rapid urbanization, combined with
the absence of and/or poor planning by planning
authorities and green space
champions/practitioners, leads to the extinction
and degradation of vulnerable environmental
factors such as flora vegetation and water bodies.
Saghir and Santoro (2018) have found similar
results also found similar result in their study.
Due to its significant density and encroachment
on the adjacent green spaces in Akure metropolis,
built-up expansion is a remarkable indicator
revealing the rate of green space depletion. In
1984, it was estimated that built-up area covered
12.5316 sq km. In 1991, it increased, rising to
20.8719 sq km, which is approximately 66.6%
more. This rise continued without no fluctuation
till the year 2022; for 2002, 2015 and 2022 it was
estimated to be 40.365sqkm, 57.413sqkm and
118.675sqkm respectively. The surrounding light
vegetation (grasses, shrubs, galleries forest, and
riparian vegetation) will suffer as a result of this
expansion, which will have a commensurate
impact on the secondary and dense vegetation.
Figure 9 shows that the area covered by dense
vegetation (natural vegetation) significantly
decreased at an exponential rate from 68.782
square kilometers in 1984 to 62.791 square
kilometers in 1991. The area continued to
decrease, reaching 0.7695 sq km in 2022, which
is approximately 8938.48% less than in 1984.
The analysis of the satellite image from 2002
revealed that the contraction had worsened
significantly since 1991, with urban green spaces
(grasses, shrubs, light vegetation, secondary
vegetation, and dense vegetation) significantly
degraded as a result of various landuse
developments in Akure metropolis.
Table 2: Percentage distribution of Green space depletion and Built-up areas between 1984 and 2022
in Akure Metropolis
Classes
Area Coverage (Sqkm)
1984
%
1991
%
2002
%
2015
%
2022
%
Built-Up
area
12.5316
20.8719
40.3650
57.4128
32
118.6749
66.15
Bare
Surface
0.4923
4.5045
2.7927
8.3934
4.68
29.1798
16.27
Grasses
and Shrubs
36.6309
17.4546
42.3072
80.5086
44.88
3.8691
2.16
Light
Vegetation
42.4908
60.5772
41.787
11.7783
6.57
9.8784
5.51
Secondary
Vegetation
18.4743
13.2021
44.4258
18.7110
10.43
17.0298
9.49
Dense
Vegetation
68.7816
62.7912
7.7238
2.5974
1.45
0.7695
0.43
Total
179.4015
179.4015
179.4015
179.4015
100.00
179.4015
100.00
Source: Author, 2023
International Journal of Environmental Engineering and Development
DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
144
Figure 9: Trend Analysis of Green space depletion and Built-up area Source: Author, 2023
6. Planning Implication of Green
space depletion in Akure
It is worth noting that Akure has experienced
remarkable physical development since 1976,
when it became the capital city of Ondo state. The
administrative status induced a population influx
into Akure because it provided job opportunities
and social amenities; and with urbanization
comes an increase in building construction,
industrial activities, economic and mining
activities; cutting down of trees (Omodehin,
2015) and encroachment into adjoining
vegetation covers in order to meet the demand of
urbanization, thereby damaging fragile natural
green and landscape components. According to
Owoeye and Ibitoye (2016), the depletion of
these vegetative resources and deterioration of
the environment are the result of landuse
expansion accompanied by incompatible changes
in landuse patterns and uncontrolled urban
development. Some sites designated for open
space development have been converted to
commercial or residential uses. Ilula recreation
centre in Oshinle area was an example of this; the
center had previously been sold out for a Petrol
station facility. It took the intervention of the
community's members and the government to
return it to its original open space development.
A few instances of landuse conversion in the
Akure area are the Omoluorogbo Grammar
School farm, which was transformed into a
Mother and Child Hospital, and the green
conservation area behind the State Secretariat,
which was converted into the Akure International
Cultural and Event Centre (The Dome). The
implication of these developments is the trade-off
of green spaces for heated surfaces. Extreme heat
poses an increasing threat to public health,
particularly in areas with high urbanization and
development.
A notable driver of the observed changes in
Akure urban green spaces is the growth in the
city’s economic, industrial, political, educational,
national and administrative functions. Diversity
in the job industry particularly light industries
such as sawmill factories, block industries;
service industries, manufacturing, construction,
trade, among others coupled with social
amenities, high property value, development
policy and being the state capital attract
population from other regions across the state and
migrants (especially rural-urban) into the city.
However, the study results show significant
y = -17,713x + 91,897
R² = 0,5505
-40
-20
0
20
40
60
80
100
120
140
Built-Up area Bare Surface Grasses and
Shrubs
Light Vegetation Secondary
Vegetation
Dense Vegetation
1984 1991 2002 2015 2022
Γραμμική (2022)
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DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
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changes in the landscape of Akure metropolis
especially in the peripheries; places like
Ijoka/Igisogba, New Town district/Oba
Afunbiowo estates, Ajipowo/Olokuta districts,
Oke-Odu/Ilere, Olu-foam/Igoba, Federal
Secretariat/Alagbaka extension and Apatapiti-
FUTA/Ipinsa area were all covered with greens in
the form of secondary and dense vegetation in
1984 (see figure 4). These classes of vegetative
covers have given way for built-up areas in
different directions and patterns as shown in
figure 8. These areas known for farming of
perennial crops like cocoa, rubbers plantations,
and dominated by diverse forest resources are
being converted to residential, private and public
institution landuses; this has also exerted pressure
on available urban lands.
Urban habitat is meant to be shaped and planned
to offer a livable, habitable and sustainable
environment to live and work. The survival of any
living entity, whether human, animal, or other
living organism, in any ecosystem is dependent
on the condition of the particular ecosystem in
which they exist. According to Cheng et al.
(2017), the survival of one-fifth of the world's
population is fully dependent on the ecosystem
services given by both rural and urban
landscapes. By engaging in sustainable urban and
environmental planning, man has the ability to
influence, select and control what their
environment delivers. Urban landscape growth is
essential, yet unchecked development at the
expense of essential environmental elements may
cause unneeded environmental issues. Lack of
green space protection legislation, ignorance of
the potential and benefits of green space,
ineffective development control enforcement,
government compulsory land acquisition for
public uses at the expense of urban agricultural
lands and open spaces, demand for land for
commercial uses (neighbourhood markets), and
conversion of organized open space and
incidental open spaces to other uses are the main
causes of the loss of green space in Akure
metropolis. However, this has led to land
degradation, loss of ecosystems and destruction
of fragile resources within and outside Akure
urban landscape. This is reflected in the figure 9
indicating decreasing trends in green vegetation
classes.
According to the study, dense vegetation area
dominated by forest vegetative species of tall,
big, and canopy trees has disappeared to the tune
of 0.43% of total land coverage in Akure
metropolis due to pressure from landuse
development, resulting in parcelization and
fragmentation of land. Individual/family owners
have cut enormous areas of forest land for
industrial and residential plan developments.
According to this study, deforestation was
substantial in Akure between 1984 and 2002;
dense forest land (vegetation) coverage was
68.7816sqkm in 1984, but it decreased to
7.7238sqkm in 18 years (2002). This was a huge
loss to local, national and global ecosystem.
Fragmentation occurs when the forest canopy is
cut up for houses, lawns, roadways, and other
infrastructure. The increased presence of people
increases the likelihood of destruction of fragile
floral species. According to a study, the amount
of land covered by forests worldwide has
decreased by 2 million square miles (3.1 million
square kilometers) since 1990. As "carbon sinks,"
forests absorb in CO2 and convert it into the
oxygen we breathe. More than one billion acres
of forest have been removed to make space for
strip mining, cattle grazing, and industrial sprawl,
it further emphasized. Deforestation is one of the
main causes of rising greenhouse gas emissions.
Additionally, the destruction of green spaces like
grasses, shrubs, light, secondary, and dense
vegetation has exacerbated erosion to varying
degrees in Akure metropolis, leading to erosion
of exposed fragile soils and lands, earthen roads,
and building foundations of the majority of
traditional buildings, especially in the core area
of Akure metropolis. The loss of ecological
values of the study area's green space component
is a critical implication of green space depletion.
According to the study, the constituents of green
spaces, such as floral components, provide
medical benefits by supplying medicinal plants
(herbs) for healing and treatment, as well as
ornamental trees and flowers for urbanites. Cities'
beauty and aesthetic values can be enhanced by
providing a unique, balanced, and
environmentally friendly place to live and work.
Children's playgrounds, recreational centers,
parks, and gardens provide places for leisure,
recreation, and relaxation, helping to alleviate
International Journal of Environmental Engineering and Development
DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
146
boredom, mental stress and anxiety, boost
emotions, and reduce aggression levels.
However, given the rate at which green spaces are
depleting in the study region, the Akure urban
environment is at risk of losing its beneficial
social and ecological values
7. Conclusion and Recommendation
The finding revealed significant changes in the
proportion of green spaces in the city's central
business district. High levels of deforestation are
occurring in the periphery in order to make way
for new residential housing developments
without planned open areas. In 1984, the city of
Akure had an equitable distribution of vegetation
(grasses and bushes, light, secondary, and dense
vegetation), with considerable green space
designation concentrations everywhere
throughout the city. Green space coverage started
to decline in 1991, and it continued to decline
until 2022, losing ground to bare ground and
built-up areas. This is in agreement with Gaisie et
al., (2019), as it is obvious that green spaces in
the study area were lost and degraded in favor of
built-up areas as a result of urban pressure from a
growing population and increased densification.
Human activities are mostly to blame for the
depletion found in the study area. The most
powerful elements leading to the degradation of
the study area's urban green spaces include
population growth, changing socio-economic
characteristics of the people, building
construction, administrative policies and
regulations. Population increase necessitates the
development of new residential and commercial
areas, as well as public services and modes of
transportation. Also, urbanization necessitates an
alteration in the original use of green spaces such
as forest areas, agricultural lands, and fragile
soils, resulting in changes in both land use pattern
and patterns of green spaces in the city. This is in
agreement with Rahman (2016) who asserted that
degradation of natural vegetation is attributed to
uncontrolled landuse expansion and urbanization.
The study estimates a continual depletion of
green areas in Akure metropolitan as of 2022, and
this is likely to continue as demand for land rises
owing to urbanisation and accompanying
activities. It is worth noting that if not mitigated,
the depletion of urban green spaces (vegetative
covers) will have a substantial detrimental impact
on the functioning and integrity of urban natural
ecosystems, as well as sustainable urban
development. It is recommended however, that
planning authorities ensure the inclusion and
implementation of green space schemes in the
city's masterplan; introduce requirement of green
spaces in all new developments in the city; create
awareness of the benefits and potential of green
spaces in their environment; develop and improve
community education engagement, education and
outreach programmes on the planting,
conservation and preservation of green spaces
within and around their environment. This is in
agreement with Janssen et al., 2012, who stated
that growing and preserving more street trees in
the Metropolis should be a fundamental part of its
planning process due to their multiple social and
ecological values in establishing sustainable
cities and communities (Janssen et al., 2012).
It is also essential to ensure better coordination at
all levels of government, a broader range of
funding, and the establishment of more urban
recreation parks and gardens at the
neighbourhood, district, and city levels. Green
space elements, without a doubt, play an essential
part in regulating and balancing ecosystem
patterns, promoting human health, providing food
security, and blessing the environment for living
organisms. As a result, there is a need to
encourage more green space champions and
practitioners in the industry; encourage a
continued research into processes and
functionality of green space developments. Also,
it is important to continuously monitor the status
and patterns of change overtime, impact and
challenges of urban green spaces in Akure
metropolis due to pressures from urban
landscapes.
International Journal of Environmental Engineering and Development
DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
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Contribution of Individual Authors to the
Creation of a Scientific Article (Ghostwriting
Policy)
The authors equally contributed in the present
research, at all stages from the formulation of the
problem to the final findings and solution.
Sources of Funding for Research Presented in a
Scientific Article or Scientific Article Itself
No funding was received for conducting this study.
Conflict of Interest
The authors have no conflicts of interest to declare
that are relevant to the content of this article.
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International Journal of Environmental Engineering and Development
DOI: 10.37394/232033.2023.1.16
Michael Ajide Oyinloye,
Chiamaka Lovelyn Olisa,
Babatope Sunday Olisa
E-ISSN: 2945-1159
149