Revista de Ciencias Tecnogicas (RECIT). Volumen 3 (1): 10-22
Revista de Ciencias Tecnológicas (RECIT). Universidad Autónoma de Baja California ISSN 2594-1925
Volumen 6 (3): e144. Julio-Septiembre, 2023. https://doi.org/10.37636/recit.v6n3e144
ISSN 2594-1925
1
Research article
Effects of wind speed and temperature on economics
and environmental impact assessment of different
solar PV systems in Malaysia
Efectos de la velocidad del viento y la temperatura en la
economía y la evaluación del impacto ambiental de diferentes
sistemas solares fotovoltaicos en Malasia
Tijani Alhassan Salami , Ariffin Salbiah
School of Mechanical Engineering, College of Engineering, Universiti Teknologi MARA, 40450 Shah Alam,
Selangor, Malaysia
Corresponding author: Tijani Alhassan Salami, School of Mechanical Engineering, College of Engineering,
Universiti Teknologi MARA, 40450 Shah Alam, Selangor, Malaysia. E-mail: alhassanuitm@gmail.com. ORCID:
0000-0002-0954-718X
Received: July 19, 2021 Acepted: July 27, 2023 Published: August 5, 2023
Abstract. This study aims to analyse the effect of temperature and wind speed on the performance of different
types of photovoltaic (PV) systems at a different state in Malaysia and how it affects the economics and
environmental impact assessment in the present year of 2018 as well as future years in 2030 and 2040. Three types
of grid-connected solar PV modules namely Mono-Crystalline, Poly-crystalline, and Thin Film were selected to be
implemented in different cities of Shah Alam, Chuping, Alor Setar, Ipoh and Kota Kinabalu. A mathematical model
was adopted to estimate the performance characteristics of the solar PV modules. Based on the data in the present
year, the highest power output produced by the Mc-Si module for Alor Setar city is given by 33.40 MWh/year while
the lowest amount of power output provided by this PV panel is about 28.18 MWh/year in Shah Alam. Furthermore,
an area of 144 m2 for the Mono-Crystalline PV module can satisfy the total energy requirement by the resident as
it was the most profitable to be implemented compared to Poly-crystalline and Thin Film. The findings of this study
can serve as important information on the economic viability of installing PV systems in the selected cities in
Malaysia.
Keywords: Temperature; Wind speed; Solar radiation; PV performance.
Resumen.- Este estudio tiene como objetivo analizar el efecto de la temperatura y la velocidad del viento en el
rendimiento de diferentes tipos de sistemas fotovoltaicos (PV) en un estado diferente de Malasia y cómo afecta la
evaluación del impacto económico y ambiental en el presente año de 2018, así como en el futuro. años en 2030 y
2040. Se seleccionaron tres tipos de módulos fotovoltaicos solares conectados a la red, a saber, monocristalinos,
policristalinos y de película delgada, para implementarlos en diferentes ciudades de Shah Alam, Chuping, Alor
Setar, Ipoh y Kota Kinabalu. Se adoptó un modelo matemático para estimar las características de rendimiento de
los módulos fotovoltaicos solares. Según los datos del año en curso, la producción de energía más alta producida
por el módulo Mc-Si para la ciudad de Alor Setar es de 33,40 MWh/año, mientras que la producción de energía
más baja proporcionada por este panel fotovoltaico es de aproximadamente 28,18 MWh/año en Shah Alam.
Además, un área de 144 m2 para el módulo fotovoltaico monocristalino puede satisfacer el requerimiento total de
energía del residente, ya que fue el más rentable de implementar en comparación con el policristalino y la película
delgada. Los hallazgos de este estudio pueden servir como información importante sobre la viabilidad económica
de instalar sistemas fotovoltaicos en las ciudades seleccionadas de Malasia.
Palabras clave: Temperatura; Velocidad del viento; Radiación solar; Rendimiento fotovoltaico.
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1. Introduction
Over the last decades, there has been a
significant increase in the demand for fossil
fuels for energy production to meet the
energy requirement for industrial and
domestic applications. The continuous
exploration and ever-growing demand for
these fossil fuels have led to the emission of
toxic materials such as carbon dioxide into
the atmosphere. Consequently, this has led
to global warming [1], [2].
A growing body of literature recognises the
threat posed by the depletion of fossil fuel
such as natural gas, coal, and oil. These
fuels also contribute significantly to global
carbon dioxide and climate change [3], [4].
An obvious solution to curb the escalation
of the ongoing depletion of global fossil fuel
and environmental pollution is to promote
the adoption of sustainable and renewable
energy technologies; this concern has
attracted extensive attention. Renewable
energy can be produced from natural
resources such as solar, wind, biomass and
geothermal [5]. Among these renewable
energy technologies, solar energy is the
fastest-growing technology in Malaysia [3].
The potential application areas of solar
energy are photovoltaic (PV) technology for
electrical power production and solar
thermal energy for thermal energy
production [6], [7]. Solar PV consists of a
semiconducting material such as silicon
which directly converts solar irradiance into
electrical energy [8]. Solar PV offers a
promising technology with several benefits
such as pollution-free and easy installation
it is therefore expected to contribute
significantly to global future sustainable
energy development [9]. It is now well
established from a variety of studies that,
climate change has a considerable effect on
renewable energy resources, for example in
the case of solar energy, wind speed, and
ambient temperature are the most important
parameters of the climate that need
considerable attention [10, 11].
In the new global economy, PV installation
has become a central issue to meet the
global energy demand and reduce emissions
caused by traditional energy resources such
as coal and natural gas [10], [11]. Therefore,
the issue of PV installation and application,
especially for domestic and industrial
applications, has received considerable
critical attention in Malaysia [12], [13]. For
example, the Government of Malaysia has
projected that by the year 2050, 11.5GW of
renewable energy capacity be installed [14].
Recently, researchers have shown an
increased interest in increasing the capacity
of PV installation, for example, the
International Energy Agency (IEA)
estimated to produce 11% of global
electricity demand through photovoltaic
(PV) by the year 2050 and this is expected
to reduce 2.3 Gt of global CO2 emission of
per year [15]. Ambient temperature has
been instrumental in our understanding of
photovoltaic module performance, and its
efficiency reduces when the ambient
temperature increases [16]. Existing
research recognises the critical role played
by ambient temperature in influencing the
performance of photovoltaic modules.
According to [16], Thin Film photovoltaic
modules are better option in hot climates
[17]. Recently investigators have examined
the effects of ambient temperature on
photovoltaic modules under Karabuk
(Turkey) climatic conditions, they conclude
that ambient temperature plays an essential
role in the performance of photovoltaic
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modules [18]. Generally, the solar
photovoltaic modules are manufactured at
standard test conditions (STC) (i.e. 1000
W/m², Air Mass 1.5 and module operating
temperature 25°C), however ambient
temperature and wind speed at a specific
location affect the performance of the
module, especially if its application is for
domestic purpose, hence the photovoltaic
module's performance changes concerning
the actual location and prevailing ambient
conditions to which they are subjected [19]
[21]. Other literature also concluded that
increase in wind speed results in cooling the
PV through convection heat loss to the
ambient and this would increase the PV
module efficiency [22].
Since the government of Malaysia has
planned to increase the capacity of PV
energy production up to about 11% of the
country's total energy demand, it is
important to understand the performance of
PV modules at different ambient
temperatures and wind speeds of the
country. However, even though previous
research related to the performance of PV
module efficiency and economic analysis
for specific locations have been carried out,
a lot more cities have not yet been covered,
especially for domestic applications.
Therefore, this study aims to fill this gap by
investigating the effect of ambient
temperature and wind speed on the
economic and electrical efficiency
performance of different PV modules in
specific cities in Malaysia.
2. Methodology
2.1 Subsection title Proposed residential
house, load consumption and load
profile
Fig. 1 shows the proposed design of the
residential house with a grid connection PV
system and its respective predicted load.
The system comprises PV panels, DC/AC
inverter, Fuse boards, loads, and the PV
meter. As the solar radiation falls on the PV
panels, DC current is produced. The DC
current can, however, be converted into AC
current by means of an inverter which is
used to match AC requirements in
residential appliances. Any excess electrical
power that is produced can be sent to
Tenaga Nasional Berhad (TNB) grid.
Figure 1. Proposed design of residential house with
a grid-connected PV system.
All the estimated load and power
consumption by the residential house were
obtained based on the selected cities of this
study, namely, Shah Alam, Chuping, Alor
Setar, Ipoh and Kota Kinabalu. The detailed
geographical location of the chosen cities is
shown in Table 1.
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Table 1. Parameters for the selected cities
From the data collected, the total energy
consumed by the resident per day is 27.432
kWh (refer to Table 2) while 822.96 kWh
energy consumed monthly by the resident.
Fig. 2 shows the hourly energy load profile
of a residential house. It can be observed
that the maximum hourly power
consumption is 3.725 kW, which requires
the PV system to produce at least
89.4kWh/day (3.725 kW 24 hours) of
energy in order to support the power
consumed by the load. Thus, the PV system
should yield at least 32.631 MWh/year
(89.4 kWh365 days). Therefore, base on
the preliminary study, 23 kWp of PV
capacity system has been chosen based on
the size of the PV panel available in the
market that is expected to produce annual
energy of 36.364 MWh/year.
Figure 2. The hourly energy load profile
Table 2. Predicted load and power consumption
No.
Equipment
Quantity
Power rating (W)
Energy (Wh)
1.
Ceiling Fan
5
75
975
2.
Television
1
150
1200
3.
Air Conditioner
1
3500
17500
4.
Washing Machine
1
500
500
5.
Refrigerators
1
150
3600
6.
Rice Cooker
1
627
627
7.
Electric kettle
1
480
480
8.
Fluorescent Lamp
10
100
1400
9.
Laptop
3
75
150
10.
Electric Iron
1
1000
1000
Average total daily power consumption
27432
Selected Cities
Latitude
(N)
Longitude
(E)
Altitude
(m a.s.l)
Time Zone
(UTC)
Shah Alam
3.0733
101.5185
45
8
Chuping
6.4985
100.2580
105
8
Alor Setar
6.1248
100.3678
60
8
Ipoh
4.5975
101.0901
195
8
Kota Kinabalu
5.9804
116.0735
0
8
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3. Model equations and simulation
Most previous studies have shown that solar
cells' performance varies with temperature
changes [23]. Therefore, to determine the
performance of all the three (3) types of PV
module in this study
(Monocrystalline/Polycrystalline /Thin
film), the cell temperature was estimated
using the NOCT-Standard formula as
shown below [24], [25].
( )
tI
T
TT NOCT
ac
+= 800
20
(1)
Where Tc is the PV cell temperature, Ta is
the ambient temperature, TNOCT is Nominal
Operating Cell Temperature. The solar
radiation, I(t) is measured at 1000W/m2
while the irradiance is fixed at 800W/m2.
Once the PV cell temperature is obtained, it
can be used to determine the efficiency of
the solar PV modules [27, 28].
( )
refcrefrefc TT =
1
(2)
All the parameters of ref, βref and Tref are
provided by the PV manufacturer [24].
Equation (3) can be used to determine the
wind speed, where vw= 1 m/s is the local
wind speed close to the module while vf is
the wind speed measured 10 meters above
the ground [24].
5.068.0 = fw vv
(3)
The nominal power of the PV panel has
been set at 23 kWp as available in the
market. Other parameters that were used for
the simulation are shown in Table 3.
Table 3. Constant parameter required
No.
Parameters
Value
1
Nominal power
23kWp
2
Module type
Standard
3
PV panel Technology
Monocrystalline/Po
lycrystalline/Thin
film
4
Mounting Disposition
Facade or tilt roof
5
Ventilation property
Ventilated
6
Tilt Angle
30˚
7
Azimuth Angle
3.1 Economics and Environmental Impact
Assessment
3.1.1 Economics models
Based on this case study, the economic
profitability of the PV systems can be
calculated by using three key indicators
namely, Payback Period (PP), Net Present
Value (NPV) and Life Cycle Cost (LCC).
i. Payback period
The payback period is the number of years
it takes for the energy-cost saving to recover
the initial investment costs of a system [26].
periodperflowinCash
investmentCapital
PeriodPayback =
(4)
ii. Net Present Value (NPV)
Net present value is the difference between
the present value of cash flows into and
from a project [29, 30]. Thus, the higher the
amount of NPV obtained, the greater is the
financial advantages.
( ) ( ) ( )
N
N
i
Q
I
Q
i
Q
SNPV +
++
+
+
+
+= 1
.....
1
12
21
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( )
=+
+= N
jj
J
i
Q
S11
(5)
From the equation, Q is the net cash flow, S
is the cost of the PV system and N is the life
cycle of the PV panel that is estimated to be
21 years [27].
iii. Life Cycle Cost (LCC) Analysis
Life Cycle Cost (LCC) is an analysis used
to determine the cost involved in the project
that includes the cost of maintaining,
operating, owning and the project disposing
of cost.
LCC=CPV+Cinv+Cins+CO&M (6)
Where CPV represents cost of PV modules,
Cinv is the inverter cost, Cins is the
installation cost, and the CO&M is the
operating and maintaining cost. Annualised
LCC analysis of the PV systems can be
calculated by the equation (7) below.
+
+
+
+
=
d
i
d
i
LCCALCC N
1
1
1
1
1
1
(7)
Where i represents inflation rate, N is PV
lifetime that is 21 years, and d indicates the
discount rate. Lastly, equation (8) can be
used to determine the actual cost invested by
the owner to produce 1kWh of energy.
Unit electrical cost =
LOAD
E
ALCC
365
(8)
3.1.2 Environmental Model
Estimating environmental impacts
assessment of energy technologies in the
early design stage is critical [26] to address
global warming issues. United Nations
report that CO2 intensity of electricity
generation needs to drop by 80%, by 2050
[32-34]. The result from the environmental
impact assessment of PV systems can be
used to establish a comparison on how
much deployment of PV modules can save
the amount of GHG emission and predict
the potential for all cities in the future.
Table 4 shows the GHG emission factors
used in this stud
Table 4. The GHG emission factors
GHG gases product from coal power plants
Emission Factors (kg/kWh)
CO2
0.97
SO2
0.00124
NOx
0.00259
Ash
0.068
4. Results and Discussion
4.1 Solar radiation data for temperature
Fig. 3 shows the effect of solar radiation on
ambient temperature for the five selected
cities. The simulation was conducted to
forecast the solar radiation for all the cities
in the present year (2018) and the future
year of 2030 and 2040 [35, 36]. Based on
Fig. 3, it can be said that high global
radiation leads to high ambient temperature.
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The amount of global radiation received by
the PV panel in 2018, 2030 and 2040 is
relatively the same with only a slight
difference. As the year keep increasing, the
ambient temperature also increases with
increases in global radiation. The city that
gained the highest global radiation is
Chuping as shown in Fig. 3(b). In the
present year and year 2030, Chuping
acquired about 180W/m2 of global radiation
monthly with ambient temperatures of
29.5C and 29.7C, respectively). In 2040,
an ambient temperature of 29.8C that
corresponds to global radiation of 181W/m2
is expected. It can also be observed from
Fig. 3(a) that Shah Alam obtained the
lowest amount of monthly global radiation
of 117W/m2 in the present year and future
year of 2030 and 2040, this corresponds to a
progressive increase in ambient temperature
from 26.8C (2018) to 27C (2030) and to
28.2C (2040) respectively.
Figure 3. Global radiation versus ambient temperature.
(a): Shah Alam
(b): Chuping
(c): Alor Setar
(d): Ipoh
(e): Kota Kinabalu
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4.2 Solar radiation data for wind speed
Figure 4 shows the forecasted data for global
radiation that is expected to be received by the PV
panel at various wind speeds. The forecasted data of
global radiation for the present year, the year 2030
and the year
2040 for all five (5) cities were obtained through
simulation. It can be observed from Figure 4 that
there is a fluctuation in the amount of global
radiation acquired as the wind speed increases for all
the cities. Among all the selected cities, however,
Chuping is the city that received the highest amount
of global radiation of 180W/m2 in the present year
and year 2030, while in the year 2040, the amount of
global radiation increased slightly to 181W/m2 at the
same wind speed of 1.7 m/s. Besides, Shah Alam also
recorded the lowest monthly global radiation of only
117W/m2 at 2.6 m/s wind speed for all the present
year and future years of 2030 and 2040 as shown in
Fig. 4(a). Therefore, it can be concluded that the
higher wind speed received corresponds to the least
amount of global radiation.
(a): Shah Alam
(b): Chuping
(c): Alor Setar
(d): Ipoh
(e): Kota Kinabalu
Figure 4. Global radiation versus wind speed
4.3 Effect of temperature on the PV
performance
Figure 5. PV module temperature versus ambient
temperature
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Figure 5 shows that, there is direct correlation
between the ambient temperature and the PV module
temperature, as the ambient temperature increases,
the PV module temperature also increases. The thin
film module obtained the highest module
temperature compared to polycrystalline and mono-
crystalline modules. The efficiency of the PV
module has been estimated using equation (2). It is
shown that, as the module temperature increases, it
results in a decrease in PV module efficiency (Refer
to Fig. 6). The monocrystalline PV panel produced
the highest efficiency compared to the other two (2)
types. For example, at PV module temperature of 48
C, the efficiency of monocrystalline, polycrystalline
and thin film modules are 18.60%, 13.19% and
8.29% respectively.
Figure 6. PV efficiency versus module temperature.
4.4 System simulation result
The performance of each PV module,
namely, Monocrystalline Silicon (Mc-Si),
Polycrystalline Silicone (PC-Si) and Thin
Film technologies, was determined to
identify which one is suitable to be installed
at the rooftop by residents based on the
cities selected. Each of the PV modules
produces different efficiency and power
output with respect to the global radiation
received at the location of the cities. As
shown in Fig.7, it can be clearly seen that
the mono-crystalline silicon PV panel
produces the highest power output for each
of the five selected cities throughout the
year 2018. Based on the data in the present
year, the highest power output produced by
the Mc-Si module for Alor Setar city is
given by 33.40 MWh/year while the lowest
amount of power output provided by this PV
panel is about 28.18 MWh/year in Shah
Alam. For Pc-Si module, the highest power
output for Alor Setar city is 31.52
MWh/year and the lowest power output of
26.68 MWh/year was recorded for Shah
Alam, whereas the highest power output for
thin-film module is 17.71 MWh/year which
corresponds to Chuping city, however, Shah
Alam still produced the least power output
with only 1.25 MWh/year.
Figure 7. Annual PV Panels output of each sites for
present year.
The forecasted data for the year 2030 and
2040 can be seen in Fig. 8 and Fig. 9
respectively. Both years indicate that
Chuping has the potential to produce the
highest PV power output for the Mc-Si, Pc-
Si and Thin Film PV module while Shah
Alam provided the least amount of power
output throughout the year. From the
present year until 2040, all of the output
power for the three types of PV systems
continued to increase in all of the cities
except for Ipoh and Kota Kinabalu. The
annual power output for Mc-Si panel in Ipoh
decreased slightly by about 0.04 MWh/year,
which is from 30.72 MWh/year in 2018 to
30.68 MWh/year in 2030 before it rises
back to 30.79 MWh/year with an increase in
power output of 0.11 MWh/year in 2040.
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Lastly, for Kota Kinabalu, the Pc-Si module
shows an increase of 0.07 MWh/year from
2018 to 2030 before it decreases to 0.11
MWh/year in 2040 whereas the thin film
panel shows a rapid increase from 1.44
MWh/year in the present year to 17.31
MWh/year in 2030 before it slightly
decrease to 17.25 MWh/year in 2040. To
recapitulate, the mono-crystalline silicon
system is the most efficient PV panel as it
produced the highest PV power output
compared to the other PV system. Thus,
Chuping proved to be the best location to
install the PV panel as it received the highest
amount of solar radiation throughout the
present year and in the future also. It can be
concluded that an increase in solar radiation
will increase the PV power output and thus
results in a better performance.
Figure 8. Annual PV Panels output of each sites for
the year 2030.
Figure 9. Annual PV Panels output of each site for
the year 2040.
4.5 Economics impact Assessment result
4.5.1 Payback Period (PP)
Figure 10. Payback period of the selected cities
The payback period is the number of years
the energy-cost saving takes to recover the
initial investment costs of a system [26].
This payback period has been determined
using equation (4). The initial investment
cost for the monocrystalline is Malaysian
Ringit (RM), RM 193,750.00, and RM
190,952.80 for polycrystalline while the
cost for thin-film is RM 180,430.00. The
shortest time taken to regain the initial cost
is about 5 years for monocrystalline panels
in the city of Chuping and Alor Setar as
shown in Fig. 10 above. Both cities
provide the highest amount of PV power
output and thus the time required to pay
back the investment cost will be shorter.
Plus, the thin-film panel results in the
longest time taken to obtain the initial
investment cost for all five cities. Based on
the graph, it takes 11 years to get back the
installation cost for Shah Alam city as it
proves that the PV power output of thin-
film module provides the least amount
compared to monocrystalline and
polycrystalline silicon modules. The
payback calculation for the present year
and for 2030 and 2040 results in almost the
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same amount with relatively small
changes which does not significantly
affect the payback time and thus only the
present year data is shown in Fig.10 above.
Through this payback calculation, the
residents can predict the time taken to
regain their investment cost and choose the
suitable PV module to be implemented at
their location whether it is beneficial or not
for them to invest.
Table 3. Net Present Value (NPV) for all of the selected cities.
Site
Year
Monocrystalline
Polycrystalline
Thin Film
Shah Alam
present
RM 141,177.83
RM1 26,113.30
RM 31,432.52
2030
RM 143,419.58
RM 128,228.14
RM 440.81
2040
RM 143,990.01
RM 128,767.17
RM 79.96
Chuping
present
RM 200,551.42
RM 182,312.98
RM 30,060.34
2030
RM 202,744.77
RM 184,400.24
RM 31,235.48
2040
RM 203,172.60
RM 184,793.89
RM 31,457.89
Alor Setar
present
RM 201,953.31
RM 183,645.82
RM 4,393.87
2030
RM 201,261.69
RM 182,994.10
RM 30,442.54
2040
RM 202,288.40
RM 183,961.05
RM 30,987.30
Ipoh
present
RM 171,352.31
RM 154,676.31
RM 18,012.99
2030
RM 170,828.97
RM 154,181.52
RM 14,195.13
2040
RM 172,155.22
RM 155,442.19
RM 14,905.31
Kota Kinabalu
present
RM 190,615.92
RM 172,913.13
RM 9,442.25
2030
RM 191,549.99
RM 173,803.05
RM 25,258.75
2040
RM 190,195.21
RM 172,519.57
RM 24,535.65
On the other hand, the thin film module
was not preferred and therefore not
suitable to be invested into by the resident
since the NPV results shown are very
small which indicated that this PV module
produced a very low value of the cash flow
for 21 years. Thus, from this analysis, it
can be said that the forecasted data for the
three (3) PV systems is expected to
increase in the year 2030 and 2040 except
that for Ipoh and Kota Kinabalu where
there is a slightly increase and decrease
trend.
4.5.2 Net Present Value (NPV)
The Net Present Value (NPV) results for
the cash flow were estimated using Excel
and the calculation was done using
equation (5). Cash flow takes into account
the total amount of incomings and
outgoings cash of the operating activities
of an organisation. Table 3 below shows
the NPV for the three (3) types of PV
systems used in this study, the NPV is used
to determine the profitability of the three
(3) PV systems at each of the selected
cities. Based on the tabulated data shown,
the monocrystalline PV panel gives the
highest amount of NPV for all five (5)
selected cities. Thus, monocrystalline is
the best PV module to be installed
especially at Chuping, this is because the
higher the amount of NPV obtained the
higher the profit margin which eventually
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translates into a greater financial benefit
for the residents.
4.5.3 Life Cycle Cost Analysis (LCCA)
Life Cycle Cost (LCC) is an analysis that
is used in order to determine the cost
involved in the project which includes cost
of maintaining, operating, owning and the
project disposing cost. By using equation
(6) and the related parameter needed, the
life cycle cost (LCC) for all three (3) types
of PV systems were obtained as tabulated
in Table 4. The highest life cycle cost
(LCC) is the Monocrystalline PV Panel
with RM 193,750.00, followed by the
Polycrystalline PV panel which is RM
190,952.80 whereas the LCC for Thin
Film PV Panel is RM 180,430.00. Next, to
find the annualised LCC (ALCC) value,
equation (7) was used. The ALCC for
Monocrystalline PV Panel is RM
15,335.08 while for Polycrystalline PV
Panel is RM 15,113.68 and for Thin Film
PV Panel is RM 14,280.81. Lastly,
equation (8) is the formula that was used
to calculate the unit cost of electricity for
1kWh. From this calculation, the actual
cost invested by the owner to produce 1
kWh of energy can be estimated. Based on
the result of the analysis, the actual cost for
producing 1 kWh of electricity for
Monocrystalline is RM 1.00 and
Polycrystalline is RM 0.99 while for Thin-
film is RM0.93. Even though the Thin
Film PV Panel provides a higher profit
margin, however, it is still not
recommended for the residents to
implement the thin-film module because
of its higher NPV value.
Table 4. The cost involved in the Life Cycle Cost Analysis (LCCA).
No
Parameters
Mc-Si
Pc-Si
Thin Film
Cost
Cost for
23 kWp
(RM)
Cost
Cost for
23 kWp
(RM)
Cost
Cost for
23 kWp
(RM)
1
PV Panel
RM 13.90
/Wp
166,800
RM 13.90 /Wp
164,280
RM13.90 /Wp
154,800
2
Installation
10% PV cost
16,680
10% PV cost
16,428
10% PV cost
15,480
3
Inverter
RM 3.91 /W
8602
RM 3.91 /W
8602
RM 3.91 /W
8602
4
Operation &
maintenance
cost
1% PV Cost
1668
1% PV Cost
1642.80
1% PV Cost
1548
TOTAL
RM 193 750
RM 190 952.80
RM 180 430
4.6 Environmental Impact Assessment
Result
The environmental impact assessment is
very important for the owner to consider in
the investment of PV systems to make a
comparison on the amount of GHG
emission that can be saved with the
deployment of solar PV and to predict the
potential for all the cities in the future. The
analysis shown in Fig. 12 shows that Alor
Setar city has the potential to save a
considerable amount of GHG emission per
year followed by Chuping, Kota Kinabalu,
and Ipoh while Shah Alam saves the least
amount. It can be seen that the
Monocrystalline is the best PV panel to be
chosen by the residents as it can save the
highest amount of GHG emission compared
to the other PV types.
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Revista de Ciencias Tecnológicas (RECIT). Volumen 6 (3): e144
(a): Shah Alam
(b): Chuping
(c): Alor Setar
(d): Ipoh
(e): Kota Kinabalu
Figure 11. Total avoided amount of GHG emission
for all selected cities
Fig. 11(c) confirms that, in relation to the
present year and by using Monocrystalline
PV panel, Alor Setar City can save up to
about 34.69 tonne (34689.81 kg) of GHG
followed by Polycrystalline PV panel which
can also save up to 32.84tonne (32839.65
kg) of GHG while the Thin Film can save
15.43 tonne (15432.42 kg) of GHG. The
forecasted data for the future year 2030,
showed that there is a slight decrease in the
amount of GHG emission that can be saved
by the Mc-Si module which is about 0.061
tonne (60.63 kg) from 34.69 tonne to 34.63
tonne. However, the Pc-Si module showed
a rapid decrease of about 14.18 tonne
(14180.47 kg) from 32.84 tonne (32839.65
kg) to 18.66 tonne (18659.18 kg) GHG
emission while the thin-film module
resulted in an increasing amount of GHG
emission that can save about 3.054tonne
(3053.98 kg) from 18486.4 kg in 2018 to
15432.42 kg in 2030. In the year 2040, both
Alor Setar and Chuping cities are predicted
to save the highest amount of GHG
emissions for all three types of PV panels.
The Mc-Si, Pc-Si and thin-film panels each
can save up to about 34.72 tonne (34719.19
kg) 32.87 tonne (32867.28 kg)
and18.53tonne (18534.16 kg) GHG
emission respectively. The city with the
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least amount of avoidable GHG emissions
per year is Shah Alam as shown in Figure 9
(a). In the present year of 2018, all three (3)
types of PV panels for Shah Alam save the
least amount of GHG emission compared to
the other cities. However, the amount of
GHG emission that can be avoided by each
of the PV Panels keeps increasing from the
present year to 2030 until 2040. This
showed that, as the year increases, the
amount of GHG emission saved by all the
PV panels in Shah Alam will also increase.
At last, it can be said that the site of Chuping
and Alor Setar is the best location compared
to the other cities as they can avoid the
highest level of GHG emission in the
present year and also in the future year.
5. Conclusion and Recommendation
Throughout this study, the effect of
temperature and wind speed on the
performance of the three (3) types of PV
panels has been analysed. It shows that an
increase in temperature decreases the
efficiency of the PV module. The increase
in PV panel temperature was due to high
solar radiation that leads to high ambient
temperature with low wind speed. This
paper also has simulated the economics and
environmental impact assessment for all
three (3) types of PV systems at the five (5)
selected cities in Malaysia. Based on the
research, it was found that Monocrystalline
silicon PV panel is suitable to be invested in
by the residents especially as it provides the
best result for all the selected cities
compared to the other PV panels. Although
the initial investment cost for a
Monocrystalline module is a bit higher,
however, it proves to produce the highest
annual PV power output and the time taken
to regain the initial cost also is the shortest
compared to the other two (2) systems.
Furthermore, the Monocrystalline PV
module only required an area of 144 m2 to
satisfy the total energy requirement by the
resident compared to 153 m2 area needed by
the Polycrystalline panel while Thin Film
PV panel required about 166 m2 area.
Of all of the five (5) selected cities, Chuping
has been the city with the highest potential
to install the PV system whether in the
present year or even in the future year since
the city received the highest amount of
global radiation, and it gives the best result
in terms of environmental and economic
impact assessments. As a recommendation,
many environmental factors affect the
performance of solar PV panels apart from
temperature and wind speed. Thus, the
study related to other factors such as
humidity and dust deposition effects should
be considered in more detail so that the solar
PV panel can provide the highest efficiency.
Also, many approaches such as
mathematical, statistical modelling and
experimental can be used for the analysis.
Acknowledgements
There was no financial support for this
work, though the Authors are grateful to
Faculty of Mechanical Engineering,
Universiti Teknologi Mara for providing
facilities to carry out the research.
6. Authorship acknowledgements
Tijani Alhassan Salami: Original Idea;
conceptualization; Methodology; Review
first draft; Review and editing; Project
administration; Review final draft. Ariffin
Salbiah: Investigation; simulation;
Analysis of data; Writing first draft; Review
final draft.
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Revista de Ciencias Tecnológicas (RECIT). Volumen 6 (3): e144
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