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International Journal of Trend in Scientific Research and Development (IJTSRD)
Volume 5 Issue 1, November-December 2020 Available Online: www.ijtsrd.com e-ISSN: 2456 – 6470
@ IJTSRD | Unique Paper ID – IJTSRD38019 | Volume – 5 | Issue – 1 | November-December 2020 Page 674
Potentiality of Biogas Production in Mubi
Slaughtering Houses, Northeastern Nigeria
A. S. Umar, N. W. Silikwa
Department of Pure and Applied Physics, Adamawa State University, Mubi, Nigeria
ABSTRACT
Intensive demand heat and electricity by slaughtering houses required an
improve understanding of existing production of biogas in order to increase
their efficiency, productivity, flexibility and to maintain balance of the
ecosystem. It is important for this study to find out how potentially the biogas
production is to be harvested for heat and electricity in Mubi slaughtering
houses. It was found that the estimated volume of biogas, were viable for
harvesting 167.47 KWh/m3 and 83.73 kWh/m3 of heat and electricity
respectively for Mubi North, while 167.47 KWh/m3 and 10.11 kWh/m3 of
heat and electricity for Mubi South daily. Therefore, authors recommends for
further studies, if were implement to achieve maximum yield of biogas.
KEYWORDS: Slaughter; House; Waste; Biogas; Abattoir; Animal
How to cite this paper: A. S. Umar | N. W.
Silikwa "Potentiality of BiogasProduction
in Mubi Slaughtering Houses,
Northeastern
Nigeria" Published in
International Journal
of Trend in Scientific
Research and
Development(ijtsrd),
ISSN: 2456-6470,
Volume-5 | Issue-1,
December 2020, pp.674-677, URL:
www.ijtsrd.com/papers/ijtsrd38019.pdf
Copyright © 2020 by author(s) and
International Journal ofTrendinScientific
Research and Development Journal. This
is an Open Access article distributed
under the terms of
the Creative
CommonsAttribution
License (CC BY 4.0)
(http://creativecommons.org/licenses/by/4.0)
INTRODUCTION
Energy has been recognized as a major factor limiting
economic growth, restricting socio-economic activities and
adversely affecting the quality of life in Nigeria. Food
processing factories, particularly slaughtering houses (SH),
demand a large number of energy intensive processes that
require heat and electricity. Due to the abundant biomass
wastes generated by slaughterhouse, these biomass
resources potential for biogas production by the process of
biomethenation, this process use slaughterhouse waste for
production of biogas [1]. The biogas is an environmentally
friendly and one of the most efficient and effective
renewable energy options [2]. Biogas canbestoredandused
when needed to produce heat or used to generate electricity
for power supply. Benefits of biogas include financial
benefits (i.e; cooking and lighting fuel saving house hold's
health related expenditure), social benefits (i.e; fertilizer
saving, employment generation and poverty reduction),
environmental benefits (i.e; green house gas emission
reduction, reduction of deforestation, improvement of air
quality etc) [3]. The resultant energy in the biogas can be
used directly as fuel to power electrical generator and
cooking by burning it in the presence of oxygen. The
generated energy could also be useful for rendering the
slaughtered animals as a replacement for the current
practice of open fire which can lead to fire disasters,
respiratory problems and carbon monoxide generation [4].
Beside energy supplies, production of biogas eliminate or
reduction of foul odors and harmful insects around SH. With
that, there is no need in SH to seek for external energy for its
usage.
Slaughtering houses (SH) are where animals such as cattle,
goat, sheep and others are slaughtered for the purpose of
food consumptions and it is also known as abattoirs. Most
Nigerian abattoirs are situated close to surface waterbodies
in order to have access to water supply needed for
slaughtered animal processing and to provide a sink for the
run-off from meat processing activities [5]. The waste from
slaughter houses have similar chemical characteristics as
those of domestic sewage but are considerably more
concentrated in general they are almost wholly organic [6].
This makes its disposal (as shown in Fig. 1) rather difficult
because utilizing it not only lead to loss of potential
environment but also lead to the added and increasing cost
of disposal. A major contributing factor to high volumes of
waste generation and difficulty in waste management at
Nigerian slaughterhouses is the absence of preservation
facilities such cold rooms [4]. Utilizing this waste on a large
scale is the major challenge in urban areas throughout the
world, poses serious health and environmental problems,
due to inappropriate disposal of solid as well as liquid on
landfills or open areas. Where abattoir effluent-polluted
waters are used to grow salad crops and vegetables,
transmission of infections is bound to occur because animal
wastes are known to contain pathogenic organisms, causing
Salmonellosis, Leptospirosis, Tularemia, Foot and mouth
disease and many more [7]-[8]. Environmental problems
have increased with improper management practices being
largely responsible for the gross pollution of the aquatic
environment with parallel increase in water borne diseases
especially typhoid, diarrhoea and dysentery [8]. Modern
research in the field of agricultureandlivestock hasrevealed
IJTSRD38019
International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470
@ IJTSRD | Unique Paper ID – IJTSRD38019 | Volume – 5 | Issue – 1 | November-December 2020 Page 675
shortcomings in the direct use of waste from meat
processing plants withoutappropriatetreatment:thespread
of soil pathogens and the transmission of diseases to
animals, water pollution, and greenhouse gas emissions [9].
The source of raw material required for biogas formation is
the waste from slaughtered animals. The biogas production
process involves multiple related biochemical processes
with microorganisms that work together to achieve the
degradation of organic matter into methane and carbon
dioxide [10]. The first stage is hydrolysis, in which the
complicated components and molecules are converted into
simpler molecules and components [11]. Thesecondstageis
the acidogenic fermentation of organic slurry is an
impressive way to inaugurate valuable intermediate
chemicals [12]. The third stage is acetogenesis. This again
refers to a process of conversion of volatile fatty acids (VFA)
into acetic acid, carbon dioxide and hydrogen which is a
chemical reagent for production ofchemical compound[13].
The last stage is methanogens production of methane from
slurry. In this process acetic acid is converted into methane
having a high potential that can be used for electricity,
cooking food etc [14]
With abundant waste resource in SH, production of biogasis
cheaper, simpler and has been implemented successful with
the advancement technology. Therefore, it is important for
this study to find out how potentially the biogas production
is to be harvested for heat and electricityinMubi.Estimation
in this study was based on the average size of the cattle,
sheep, and goats and expected quantity of biogas, heat and
electricity were adopted from other scholar contexts.
METHODS AND MATERIALS
A. Description of Study Area
Mubi is located at the coordinates of 10°16′N 13°16′E /
10.267°N 13.267°E in Northeastern, Nigeria. The Mubi
consist of 2 local government, including Mubi North and
South. The major tribes of the town are: Gude, Nzanyi, Fali,
Kilba, Marghi, higgi and Fulani. Mubi is the commercial
center of Adamawa State and has an international cattle
market, which biggest in region. Most of their communities
engage in farming, both local and international businesses
and cattle rearing. Their planting crops includes groundnut,
maize, yam, cassava, guinea corn, millet and rice.
Figure 1 Dumped slaughtered waste at Mubi North SH
B. Estimation of Slaughtering Houses Waste
The SH considered in this study are from Mubi North and
South L.G.A in Adamawa state. Animals slaughtered in Mubi
SH include cows, sheep, goat, as shown in Table 1. Primary
data were collected through personal interview with people
who work in main SH (excluding the number of livestock
slaughtered around homes or outside the selected SH).
The potential of biogas volume produced depends on
available waste. Effluent fromslaughterhouseismoderateto
high strength complex wastewater containing about 45%
soluble and 55% coarse suspended organics [6].
Approximately 50–54% of each cow, 52% of each sheep
orgoat, 60–62% of each pig, 68–72% of each chicken, and
78% of each turkey end up as meat consumed by human
beings with the remainder becoming waste after processing
[15]-[16]. According to Rao et al, 1Kg of abattoirs waste can
produce 0.053m3 of Biogas, and the quantity waste in an
average size of animal by [17], was adopted to estimate the
volume of biogas in this study as shown in Table 2. The data
was used to estimate quantity of waste and volume biogas
generated per day, using the following equations:
Slaughtered waste = Number of animals × Quantity of
slaughtered waste per head (Kg) (1)
Volume of biogas (m3) = Quantity waste × 0.053 (m3) (2)
Table 1 The average number of animals slaughtered in
Mubi North and South per day
Stations Cattle Sheeps/goats
Mubi North 26 45
Mubi South 3 7
Table 2 The mass waste per slaughtered animal
according to Aniebo et al, 2009
S/
No
Waste Categories Cow
Sheeps/
Goats
1 Blood per head (kg) 12.6 0.72
2 Intestinal content per head (kg) 8.0 1.25
3 Waste tissue per head (kg) 6.4 0.80
4 Bone per head (kg) 11.8 2.06
Source: Aniebo et al, 2009.
The Slaughtered waste was a combination of all animals
including blood, intestinal content and waste tissues. This
study did not include bone, because itisuseful forsomething
else ( not waste). Therefore, it was estimated thattheweight
of average cow and sheep/goat slaughtered waste were
respectively 27 and 2.77Kg.
C. Estimation of Energy From Biogas
The potential energy from slaughtering waste were
determined through energy analysis. Energy analysis was
used to examined how much energy is available for
utilization of biogas exhausted ingeneratinga unitofenergy.
According to [18] the net energy analysis indicatedthatboth
the thermal and electrical demandoftheslaughteringfacility
could be met from the energy generatedthroughcombustion
of the biogas in a CHP unit with electrical and thermal
efficiencies of 41% and 49% respectively.Ultimately,85%of
the waste accumulated during the slaughter
process is converted into2700MWhthermal and3200MWh
electrical energy in a biogascombinedheatandpower(CHP)
plant [19]. However, in this study conversion of biogas into
electric and heat energy are estimated, according to [20],
where 1 m3 of biogas can result in the production of 1.9 kWh
of electricity and 3.8 KWh of heat, as shown in equation (3)
and (4).
International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470
@ IJTSRD | Unique Paper ID – IJTSRD38019 | Volume – 5 | Issue – 1 | November-December 2020 Page 676
Electricity (KWh/year) = biogas (m3/year) × 1.9 KWh/m3
(3)
Heat (KWh/year) = biogas (m3/year) × 3.8 KWh/m3
(4)
RESULT AND DISCUSSION
The purpose of this section is to discuss the results obtained
from the Slaughtered waste in the SH, by considering the
volume of biogas and expected energy output.
Table 3 Quantity of waste and volume of biogas
generated in Mubi North and South SH per day
Parameters
Waste
(Kg)
Biogas
(m3)
Stations Cows
Sheeps/
goats
Cows
Sheep/
goats
Mubi North 702 129.47 37.21 6.86
Mubi South 81 19.39 4.29 1.03
From Table 3, the estimated daily slaughteredwasteofcows
and sheep/goats, are responsible for producing 702 and
129.47 Kg respectively in Mubi North, and 81 and 19.29 Kg
for Mubi South. While an estimated daily biogas generated
are 37.21 and 6.86 m3 for Mubi North and 4.29 and 1.03 m3
Mubi South respectively. The result also shows that the
number of slaughtered sheep/goats were high in the Mubi
SH compare to cows. However, the availability of this
resource ensures the continuous supply of biogas, as far as
the SH is existing.
Table 4 Estimated energy from biogas generated per
day
Stations
Total
Slaughtered
waste (Kg)
Total
Volume
of
biogas
(m3)
Heat
Generated
Energy
(KWh/m3)
Electric
Generated
Energy
(KWh/m3)
Mubi
North
831.47 44.07 167.47 83.73
Mubi
South
100.39 5.32 20.22 10.11
Table 4 represent the daily estimated quantity of waste,
volumes of biogas, and expected energy output. The results
shows that, 44.07 m3 biogas can yield of heat and electricity
respectively per day for Mubi North, while 5.32 m3 of biogas
yield 167.47 KWh/m3 and 10.11 kWh/m3 of heat and
electricity per day for Mubi South.
This expected amount of biogas estimated could run the
generator to produce heat and electricity. The utilisation
pathway consisted of the combustion of the raw biogas with
a Lower Heating Value (LHV) of 37 MJ/m3 CH4 in a CHP unit
with a total net efficiency of 90%, 41% generated as
electricity and 49% as heat [21]. Also, the energy generated
by the biogas CHP-plant can cover a significant share of the
energy requirement of the abattoir correspondingto50%of
heat and 60% of electric demand, respectively [19].
The expected heat is used for preparing meat (as shown in
Fig. 2, where mostly they are use to firewood, charcoal and
used car tyre to prepare meat and skin, locally called pomo),
while electricity is mainly used in the cold rooms,officesand
the lighting of the SH. With that, SH waste has the potential
to partly replace its energy demand by converting
slaughtered waste into heat and electricity. Hence, the
remaining subtract is also useful as organic fertilizer. The
application of such an organic fertilizer improves the
physical condition of the soil, increasingthesoil porosityand
reducing the bulk density, which allows for smooth root
penetration and growth in the soil [22]. Thus, implementing
bio-digester in Mubi SH will fetch considerable profit in
terms of energy savings, air quality, agriculture, potable
water supplies, and aquatic life.
CONCLUSION
The outlook for this study is to find out how potentially the
biogas production is to be harvested for heat and electricity.
Accordingly, Mubi can potentially benefit from installations
of 44.07 m3 and 5.32 m3 daily biogas production fed with
slaugtererd animals waste of 831.47 and 100.39 Kg
respectively for Mubi North and South. Thereby, harvesting
daily 167.47 KWh/m3 and 83.73 kWh/m3 of heat and
electricity for Mubi North SH, while 167.47 KWh/m3 and
10.11 kWh/m3 of heat and electricity for Mubi South SH.
Implementing this will go a long way towards solving their
energy demand. It is, however, strongly recommended for
further details study and to seek for skilled labour and
experienced experts, if were to implement to achieve
maximum yield of biogas.
REFERENCES
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International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470
@ IJTSRD | Unique Paper ID – IJTSRD38019 | Volume – 5 | Issue – 1 | November-December 2020 Page 677
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production in Uruguay. Renewable and Sustainable
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Potentiality of Biogas Production in Mubi Slaughtering Houses, Northeastern Nigeria

  • 1. International Journal of Trend in Scientific Research and Development (IJTSRD) Volume 5 Issue 1, November-December 2020 Available Online: www.ijtsrd.com e-ISSN: 2456 – 6470 @ IJTSRD | Unique Paper ID – IJTSRD38019 | Volume – 5 | Issue – 1 | November-December 2020 Page 674 Potentiality of Biogas Production in Mubi Slaughtering Houses, Northeastern Nigeria A. S. Umar, N. W. Silikwa Department of Pure and Applied Physics, Adamawa State University, Mubi, Nigeria ABSTRACT Intensive demand heat and electricity by slaughtering houses required an improve understanding of existing production of biogas in order to increase their efficiency, productivity, flexibility and to maintain balance of the ecosystem. It is important for this study to find out how potentially the biogas production is to be harvested for heat and electricity in Mubi slaughtering houses. It was found that the estimated volume of biogas, were viable for harvesting 167.47 KWh/m3 and 83.73 kWh/m3 of heat and electricity respectively for Mubi North, while 167.47 KWh/m3 and 10.11 kWh/m3 of heat and electricity for Mubi South daily. Therefore, authors recommends for further studies, if were implement to achieve maximum yield of biogas. KEYWORDS: Slaughter; House; Waste; Biogas; Abattoir; Animal How to cite this paper: A. S. Umar | N. W. Silikwa "Potentiality of BiogasProduction in Mubi Slaughtering Houses, Northeastern Nigeria" Published in International Journal of Trend in Scientific Research and Development(ijtsrd), ISSN: 2456-6470, Volume-5 | Issue-1, December 2020, pp.674-677, URL: www.ijtsrd.com/papers/ijtsrd38019.pdf Copyright © 2020 by author(s) and International Journal ofTrendinScientific Research and Development Journal. This is an Open Access article distributed under the terms of the Creative CommonsAttribution License (CC BY 4.0) (http://creativecommons.org/licenses/by/4.0) INTRODUCTION Energy has been recognized as a major factor limiting economic growth, restricting socio-economic activities and adversely affecting the quality of life in Nigeria. Food processing factories, particularly slaughtering houses (SH), demand a large number of energy intensive processes that require heat and electricity. Due to the abundant biomass wastes generated by slaughterhouse, these biomass resources potential for biogas production by the process of biomethenation, this process use slaughterhouse waste for production of biogas [1]. The biogas is an environmentally friendly and one of the most efficient and effective renewable energy options [2]. Biogas canbestoredandused when needed to produce heat or used to generate electricity for power supply. Benefits of biogas include financial benefits (i.e; cooking and lighting fuel saving house hold's health related expenditure), social benefits (i.e; fertilizer saving, employment generation and poverty reduction), environmental benefits (i.e; green house gas emission reduction, reduction of deforestation, improvement of air quality etc) [3]. The resultant energy in the biogas can be used directly as fuel to power electrical generator and cooking by burning it in the presence of oxygen. The generated energy could also be useful for rendering the slaughtered animals as a replacement for the current practice of open fire which can lead to fire disasters, respiratory problems and carbon monoxide generation [4]. Beside energy supplies, production of biogas eliminate or reduction of foul odors and harmful insects around SH. With that, there is no need in SH to seek for external energy for its usage. Slaughtering houses (SH) are where animals such as cattle, goat, sheep and others are slaughtered for the purpose of food consumptions and it is also known as abattoirs. Most Nigerian abattoirs are situated close to surface waterbodies in order to have access to water supply needed for slaughtered animal processing and to provide a sink for the run-off from meat processing activities [5]. The waste from slaughter houses have similar chemical characteristics as those of domestic sewage but are considerably more concentrated in general they are almost wholly organic [6]. This makes its disposal (as shown in Fig. 1) rather difficult because utilizing it not only lead to loss of potential environment but also lead to the added and increasing cost of disposal. A major contributing factor to high volumes of waste generation and difficulty in waste management at Nigerian slaughterhouses is the absence of preservation facilities such cold rooms [4]. Utilizing this waste on a large scale is the major challenge in urban areas throughout the world, poses serious health and environmental problems, due to inappropriate disposal of solid as well as liquid on landfills or open areas. Where abattoir effluent-polluted waters are used to grow salad crops and vegetables, transmission of infections is bound to occur because animal wastes are known to contain pathogenic organisms, causing Salmonellosis, Leptospirosis, Tularemia, Foot and mouth disease and many more [7]-[8]. Environmental problems have increased with improper management practices being largely responsible for the gross pollution of the aquatic environment with parallel increase in water borne diseases especially typhoid, diarrhoea and dysentery [8]. Modern research in the field of agricultureandlivestock hasrevealed IJTSRD38019
  • 2. International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470 @ IJTSRD | Unique Paper ID – IJTSRD38019 | Volume – 5 | Issue – 1 | November-December 2020 Page 675 shortcomings in the direct use of waste from meat processing plants withoutappropriatetreatment:thespread of soil pathogens and the transmission of diseases to animals, water pollution, and greenhouse gas emissions [9]. The source of raw material required for biogas formation is the waste from slaughtered animals. The biogas production process involves multiple related biochemical processes with microorganisms that work together to achieve the degradation of organic matter into methane and carbon dioxide [10]. The first stage is hydrolysis, in which the complicated components and molecules are converted into simpler molecules and components [11]. Thesecondstageis the acidogenic fermentation of organic slurry is an impressive way to inaugurate valuable intermediate chemicals [12]. The third stage is acetogenesis. This again refers to a process of conversion of volatile fatty acids (VFA) into acetic acid, carbon dioxide and hydrogen which is a chemical reagent for production ofchemical compound[13]. The last stage is methanogens production of methane from slurry. In this process acetic acid is converted into methane having a high potential that can be used for electricity, cooking food etc [14] With abundant waste resource in SH, production of biogasis cheaper, simpler and has been implemented successful with the advancement technology. Therefore, it is important for this study to find out how potentially the biogas production is to be harvested for heat and electricityinMubi.Estimation in this study was based on the average size of the cattle, sheep, and goats and expected quantity of biogas, heat and electricity were adopted from other scholar contexts. METHODS AND MATERIALS A. Description of Study Area Mubi is located at the coordinates of 10°16′N 13°16′E / 10.267°N 13.267°E in Northeastern, Nigeria. The Mubi consist of 2 local government, including Mubi North and South. The major tribes of the town are: Gude, Nzanyi, Fali, Kilba, Marghi, higgi and Fulani. Mubi is the commercial center of Adamawa State and has an international cattle market, which biggest in region. Most of their communities engage in farming, both local and international businesses and cattle rearing. Their planting crops includes groundnut, maize, yam, cassava, guinea corn, millet and rice. Figure 1 Dumped slaughtered waste at Mubi North SH B. Estimation of Slaughtering Houses Waste The SH considered in this study are from Mubi North and South L.G.A in Adamawa state. Animals slaughtered in Mubi SH include cows, sheep, goat, as shown in Table 1. Primary data were collected through personal interview with people who work in main SH (excluding the number of livestock slaughtered around homes or outside the selected SH). The potential of biogas volume produced depends on available waste. Effluent fromslaughterhouseismoderateto high strength complex wastewater containing about 45% soluble and 55% coarse suspended organics [6]. Approximately 50–54% of each cow, 52% of each sheep orgoat, 60–62% of each pig, 68–72% of each chicken, and 78% of each turkey end up as meat consumed by human beings with the remainder becoming waste after processing [15]-[16]. According to Rao et al, 1Kg of abattoirs waste can produce 0.053m3 of Biogas, and the quantity waste in an average size of animal by [17], was adopted to estimate the volume of biogas in this study as shown in Table 2. The data was used to estimate quantity of waste and volume biogas generated per day, using the following equations: Slaughtered waste = Number of animals × Quantity of slaughtered waste per head (Kg) (1) Volume of biogas (m3) = Quantity waste × 0.053 (m3) (2) Table 1 The average number of animals slaughtered in Mubi North and South per day Stations Cattle Sheeps/goats Mubi North 26 45 Mubi South 3 7 Table 2 The mass waste per slaughtered animal according to Aniebo et al, 2009 S/ No Waste Categories Cow Sheeps/ Goats 1 Blood per head (kg) 12.6 0.72 2 Intestinal content per head (kg) 8.0 1.25 3 Waste tissue per head (kg) 6.4 0.80 4 Bone per head (kg) 11.8 2.06 Source: Aniebo et al, 2009. The Slaughtered waste was a combination of all animals including blood, intestinal content and waste tissues. This study did not include bone, because itisuseful forsomething else ( not waste). Therefore, it was estimated thattheweight of average cow and sheep/goat slaughtered waste were respectively 27 and 2.77Kg. C. Estimation of Energy From Biogas The potential energy from slaughtering waste were determined through energy analysis. Energy analysis was used to examined how much energy is available for utilization of biogas exhausted ingeneratinga unitofenergy. According to [18] the net energy analysis indicatedthatboth the thermal and electrical demandoftheslaughteringfacility could be met from the energy generatedthroughcombustion of the biogas in a CHP unit with electrical and thermal efficiencies of 41% and 49% respectively.Ultimately,85%of the waste accumulated during the slaughter process is converted into2700MWhthermal and3200MWh electrical energy in a biogascombinedheatandpower(CHP) plant [19]. However, in this study conversion of biogas into electric and heat energy are estimated, according to [20], where 1 m3 of biogas can result in the production of 1.9 kWh of electricity and 3.8 KWh of heat, as shown in equation (3) and (4).
  • 3. International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470 @ IJTSRD | Unique Paper ID – IJTSRD38019 | Volume – 5 | Issue – 1 | November-December 2020 Page 676 Electricity (KWh/year) = biogas (m3/year) × 1.9 KWh/m3 (3) Heat (KWh/year) = biogas (m3/year) × 3.8 KWh/m3 (4) RESULT AND DISCUSSION The purpose of this section is to discuss the results obtained from the Slaughtered waste in the SH, by considering the volume of biogas and expected energy output. Table 3 Quantity of waste and volume of biogas generated in Mubi North and South SH per day Parameters Waste (Kg) Biogas (m3) Stations Cows Sheeps/ goats Cows Sheep/ goats Mubi North 702 129.47 37.21 6.86 Mubi South 81 19.39 4.29 1.03 From Table 3, the estimated daily slaughteredwasteofcows and sheep/goats, are responsible for producing 702 and 129.47 Kg respectively in Mubi North, and 81 and 19.29 Kg for Mubi South. While an estimated daily biogas generated are 37.21 and 6.86 m3 for Mubi North and 4.29 and 1.03 m3 Mubi South respectively. The result also shows that the number of slaughtered sheep/goats were high in the Mubi SH compare to cows. However, the availability of this resource ensures the continuous supply of biogas, as far as the SH is existing. Table 4 Estimated energy from biogas generated per day Stations Total Slaughtered waste (Kg) Total Volume of biogas (m3) Heat Generated Energy (KWh/m3) Electric Generated Energy (KWh/m3) Mubi North 831.47 44.07 167.47 83.73 Mubi South 100.39 5.32 20.22 10.11 Table 4 represent the daily estimated quantity of waste, volumes of biogas, and expected energy output. The results shows that, 44.07 m3 biogas can yield of heat and electricity respectively per day for Mubi North, while 5.32 m3 of biogas yield 167.47 KWh/m3 and 10.11 kWh/m3 of heat and electricity per day for Mubi South. This expected amount of biogas estimated could run the generator to produce heat and electricity. The utilisation pathway consisted of the combustion of the raw biogas with a Lower Heating Value (LHV) of 37 MJ/m3 CH4 in a CHP unit with a total net efficiency of 90%, 41% generated as electricity and 49% as heat [21]. Also, the energy generated by the biogas CHP-plant can cover a significant share of the energy requirement of the abattoir correspondingto50%of heat and 60% of electric demand, respectively [19]. The expected heat is used for preparing meat (as shown in Fig. 2, where mostly they are use to firewood, charcoal and used car tyre to prepare meat and skin, locally called pomo), while electricity is mainly used in the cold rooms,officesand the lighting of the SH. With that, SH waste has the potential to partly replace its energy demand by converting slaughtered waste into heat and electricity. Hence, the remaining subtract is also useful as organic fertilizer. The application of such an organic fertilizer improves the physical condition of the soil, increasingthesoil porosityand reducing the bulk density, which allows for smooth root penetration and growth in the soil [22]. Thus, implementing bio-digester in Mubi SH will fetch considerable profit in terms of energy savings, air quality, agriculture, potable water supplies, and aquatic life. CONCLUSION The outlook for this study is to find out how potentially the biogas production is to be harvested for heat and electricity. Accordingly, Mubi can potentially benefit from installations of 44.07 m3 and 5.32 m3 daily biogas production fed with slaugtererd animals waste of 831.47 and 100.39 Kg respectively for Mubi North and South. Thereby, harvesting daily 167.47 KWh/m3 and 83.73 kWh/m3 of heat and electricity for Mubi North SH, while 167.47 KWh/m3 and 10.11 kWh/m3 of heat and electricity for Mubi South SH. Implementing this will go a long way towards solving their energy demand. It is, however, strongly recommended for further details study and to seek for skilled labour and experienced experts, if were to implement to achieve maximum yield of biogas. REFERENCES [1] Malav OP, Birla R, Virk KS, Sandhu HS, Mehta N, Kumar P, Wagh R. V. (2018): Safe Disposal of Slaughter House Waste. Appro Poult Dairy & Vet Sci. Vol. 2(4): 171-173. APDV.000542. 2018. DOI: 10.31031/APDV.2018.02.000542. [2] Janczak, D., Mazurkiewicz, J., Czekała, W., M., Kozłowski, K.,Jeżowska, A. (2019): A Possibility of Functioning Biogas Plant at a Poultry Farm. Journalof Ecological Engineering. Vol. 20(11): 225–231. https://doi.org/10.12911/22998993/114090. [3] Rouf, M. A., Islam, M. S., Rabeya, T., Mondal, A. K., Khanam, M., Samadder, P.R., and Ara, Y. (2016): Biogas from slaughter house waste and optimization of the process. Bangladesh J. Sci. Ind. Res. 51(3): 203- 214. [4] Omole, D. O. and Ogbiye, A. S. (2013):AnEvaluationof Slaughterhouse Wastes in South-West Nigeria. 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