ArticlePDF Available

Generating Renewable Electricity from Food Waste

Authors:

Abstract and Figures

Mini biogas power plant (MBPP) was first used and launched in Malaysia by Universiti Sains Malaysia (USM). USM with the collaboration with Enerbon Sdn Bhd had set up this mini biogas power plant as an education and research and development tools to professionals and researchers and at the same time giving opportunities to people who are interested with this system to witness and experience it themselves by looking at how this mini biogas power plant works. There are 2 main objectives of this study being carried out; firstly to determine whether food wastes (canteen and cafeterias wastes) can produce methane gas (biogas) that can generate heat and electricity and secondly to establish how much methane gas (biogas) can be produced with the certain amount of the feedstock. It should be pointed out that this MBPP can generate 600kW electricity per day as this system can generate electricity about 25kW/h. The methane produced per day is approximately 180 cubic metres. The higher the wastes, the higher the amount of methane gas produced. The cow dung is used to increase the bacteria in the tank; the methane gas production will be higher if the bacteria breed.
Content may be subject to copyright.
Generating Renewable Electricity from Food Waste
M.A.O. Mydin1, N.F. Nik Abllah2, N. Md Sani3, N. Ghazali4, N.F. Zahari5
1,2,3,4School of Housing, Building and Planning, Universiti Sains Malaysia, 11800 Penang, Malaysia
5Faculty of Architecture, Planning and Surveying, UiTM Perak, Seri Iskandar Campus, 32610, Seri
Iskandar, Perak, Malaysia
Abstract. Mini biogas power plant (MBPP) was first used and launched in Malaysia by
Universiti Sains Malaysia (USM). USM with the collaboration with Enerbon Sdn Bhd had
set up this mini biogas power plant as an education and research and development tools to
professionals and researchers and at the same time giving opportunities to people who are
interested with this system to witness and experience it themselves by looking at how this
mini biogas power plant works. There are 2 main objectives of this study being carried
out; firstly to determine whether food wastes (canteen and cafeterias wastes) can produce
methane gas (biogas) that can generate heat and electricity and secondly to establish how
much methane gas (biogas) can be produced with the certain amount of the feedstock. It
should be pointed out that this MBPP can generate 600kW electricity per day as this
system can generate electricity about 25kW/h. The methane produced per day is
approximately 180 cubic metres. The higher the wastes, the higher the amount of methane
gas produced. The cow dung is used to increase the bacteria in the tank; the methane gas
production will be higher if the bacteria breed.
1 Introduction
Biogas typically refers to a gas produced by the breakdown of organic matter in the absence of
oxygen. It is a renewable energy source, like solar and wind energy. Furthermore, biogas can be
produced from regionally available raw materials and recycled waste and is environmentally friendly
and CO2 neutral. Biogas is produced by the anaerobic digestion or fermentation of biodegradable
materials such as manure, sewage, municipal waste, green waste, plant material, and crops [1]. Biogas
comprises primarily methane (CH4) and carbon dioxide (CO2) and may have small amounts of
hydrogen sulphide (H2S), moisture and siloxanes. The gases methane, hydrogen, and carbon
monoxide (CO) can be combusted or oxidized with oxygen [2].
This energy release allows biogas to be used as fuel. Biogas can be used as fuel in any country for
heating purposes, such as cooking and more. It can also be used in anaerobic digesters where it is
typically used in a gas engine to convert the energy in the gas into electricity and heat [3]. Biogas can
be compressed, much like natural gas, and used to power motor vehicles. In UK for instance, biogas is
estimated to have the potential to replace about 17% of vehicle fuel. Biogas is a renewable fuel so it
qualifies for renewable energy subsidies in some parts of the world [4]. Biogas can also be cleaned
and upgraded to natural gas standards when it becomes bio methane.
DOI: 10.1051/
C
Owned by the authors, published by EDP Sciences, 2014
,
/201
Web of Conferences (201 )
03
E3S
e sconf
3
30101 4
40101
This is an Open Access article distributed under the terms of the Creative Commons Attribution License 4.0, which permits
unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.
2
2
Article available at http://www.e3s-conferences.org or http://dx.doi.org/10.1051/e3sconf/20140301012
Mini biogas power plant (MBPP) which was first launched in Malaysia at Universiti Sains
Malaysia (USM) is capable of generating 600 kW of electricity daily from food waste in the campus.
This pioneering project is aimed of building a prototype to be used by internal communities with
problems pertaining obtaining regular electricity supply [5]. Food waste supplied by all cafeterias and
canteens in the campus will be converted into methane which will be generating electricity [6,7]. The
plant has two tanks that can accommodate 1000kg of food and organic waste such as grass, vegetables
waste, leftover rice and leftover fish. The electricity generated could be channelled to the university’s
power supply grid [8,9]. Communities with a lot of organic waste but no connection to the grid would
benefit most from MBPP, in which MBPP per se produces approximately 180 cubic metres of
methane a day from readily available local waste material [10,11].
This paper will focus about feasibility study on mini biogas power plant (MBPP) which is first
developed and operated in Malaysia and launched at Universiti Sains Malaysia (USM). USM with the
collaboration Enerbon Sdn Bhd setup up this mini biogas power plant as an education and research
and development to professionals and researchers and at the same time give opportunity to the people
who are interest with this system to see and experience their self by looking how this mini biogas
power plant works. The objectives of this paper are two-fold; firstly to determine whether food wastes
(canteen and cafeterias wastes) can produce methane gas (biogas) that can generate heat and
electricity and secondly to establish how much methane gas (biogas) can be produced with the certain
amount of the feedstock
2. Setup of Mini Biogas
As mentioned in the previous section, the aim of this study is to distinguish whether this mini
biogas power plant could generate methane gas and produce electricity as much as being produced by
other countries by means of food wastes as the feedstock. Fig. 1 shows the modular concept of the
mini biogas power plant which is in prefabricated design and can be installed easily.
Figure 1: Prefabricated mini biogas power plant
This mini biogas power plant will indicate the amount of methane gas produced with the certain
amount of feedstock used everyday. This machine works 24 hours per day with total amount of
feedstock ranging from 200kg to 1000kg. These mini biogas power plants use anaerobic digestion (no
present of oxygen) and the feedstock is mixed with the cow dung and water. The feedstock came from
canteens and cafeterias waste for example leftover rice, vegetables waste, fish waste, fruits and any
other food leftovers. Fig. 2 demonstrates the room where the temperature and pH value were
controlled.
E3S Web of Conferences
01012-p.2
Figure 2: Temperature and pH value were set and controlled in special room
By using food waste and organic waste from cafeterias and canteens around the campus, this mini
biogas power plant will digest all the waste and turn it into methane in order to produce electricity.
With the total amount of 1000kg of mixed food waste per day, there is about 180 cubic metre of
methane can be produced and about 600kW electricity can be generated. The digesters that are used
for the purpose of production of biogas can be used in mesophilic conditions, which mean a
temperature range of 20 to 25 degrees Celsius to 40 to 45 degrees Celsius. The digesters can also be
run in thermophilic conditions, where the temperature range is from 50 to 55 degrees Celsius to 60 to
65 degrees Celsius. Both these conditions call for separate species of bacteria. It is notedthat the
mesophilic operations are safer and more stable than the thermophilic operations that are capable of
inactivating the parasites of animals and the various pathogens. Through the lab test that has been
conducted in the environmental lab, the temperature of the water in the tank 1 and in the digester are
35.7°C and 37.5°C respectively. Fig. 3 shows samples that were taken from tank and digester.
Figure 3: Samples taken from tank and digester
At the hydrolysis process it is important to make sure that the pH value are 4 to 5 and for the
methanogenesis are 7 to 8. Preparation of feeding substrate for pH value is very important with the
condition no oxygen and darkness is about less than 1%.The heating of digesters is also pretty
important in this regard. The pH of the slurry has to be close to 7. This is pretty much possible
provided that cow dung is employed in the form of a substrate. If favourable conditions may be
provided then as much as sixty litres of biogas may be produced for one kilogram of cow dung.
Through the lab test that has been conducted in the environmental lab, the pH values obtained from
tank 1 and in the digester are 4.78 and 7.11 correspondingly.
Emerging Technology for Sustainable Development Congress (ETSDC 2014)
01012-p.3
3. Results from Hypothetical Case Study
The results obtained from the hypothetical case study, the result is shown in Table 1. The mini
biogas system costs about RM1.0 – RM 1.2 millions including the operational cost which is diesel that
costs RM4 per litre. This mini biogas power plant needs only a battery backup of about 6 hours to add
fuels on the generator or when doing maintenance to the generator. The cost for solar energy system is
higher than biogas system which sums up around RM 4.5 Million due to the cost for battery backup.
Solar energy system needs battery backup when it is raining or cloudy, that makes the solar panel
unable to receive sunlight. In this situation, solar panel cannot generate any electricity. The cost for
battery backup makes the solar system's cost higher than biogas.
This system can be installed easily due to it being modular which means it is portable and can be
transferred and installed anywhere. The biogas mini power plant only needs food and organic waste to
generate electricity energy and the generator is guaranteed to work 24 hours a day regardless of the
weather. The supply of wastes is continuous as long as there are people that lives in the vicinity;
ensuring that this system will work well. If solar system is used, it may cause a problem during rainy
day because the system will not be able to receive any sunlight and needs battery for backup.
Table 1: The comparison between biogas' and solar system's costs
Types of
energy
Biogas with generator Solar energy with batteries
Source Needs 1000kg/day organic feedstock and
operator
Needs 150 kWp panel capacity with 4-5h
max sun shine plus additional light
Efficiency 600kW and 182m3 Methane Gas per day 4hours sunshine (150kWp x 4) = 600kW
per day
Operational cost Need diesel to run the generator (1 litres
diesel = RM4 ) No need
Battery backup Battery backup for 6 hour only Battery backup for 2 days (for raining and
cloudy day)
Production Gas and electricity Electricity
Cost RM 1.0 – 1.2 Million RM4.5 Million (needed a lot of battery
backup for raining days)
By having an amount of 1000 kg waste per day, the electricity generated will be about 600kW per
day due to the fact that this mini biogas power plant can produce up to 25kWh. About 180 cubic metre
methane gas is produced and will be burned to generate electricity. If there are more wastes, the
electricity energy generated will also increase. The maximum electricity that can be generated by this
mini biogas power plant is 720Kw with the amount of waste of 1200kg per day. The result of the
methane and electricity produced is as shown in Table 2 below.
Table 2: The production of methane gas and electricity per day
Feedstock – Organic active (canteens and cafeterias waste)
Power/tFs (per day) Feedstock substrate CH4/VS and /Feedstock
(m3CH4/kg VS) kWh/d kWh/h
Food Waste 0.196 196.0 646.80 26.95
The production of biogas result indicated that about 26.95 kWh/h electricity can be generated
with the total amount of 1000kg/d of food waste supplied. There is about 646.80kWh/d electricity can
be produced a day. Methane gas that can be produced per day is 196.0 cubic metres. It is proved that
all the foods waste from canteens and cafeterias can generate more methane gas and electricity. The
dry matter content in this mixed waste is about 40% while the volatile solid makes up about 98%. The
result shown was higher from other country's results because this mini biogas power plant has a
change in their design that increases their workability and efficiency.
E3S Web of Conferences
01012-p.4
Table 3 shows the amount of the feedstock used by week. The amount of feedstock is same in
week 1 to week 3 because the bacteria in the tank (cow dung) need at least 3 weeks to multiply the
bacteria. The higher the bacteria, the higher the methane gas production. At the week 4 until week 12
the amount of feedstock place in the tank increase to multiply the bacteria but until 1000kg the
feedstock will remains constant.
Table 3: Table of feedstock used per week
Weeks Amount of feedstock (kg) Amount of methane gas production (m3)
1 200 35.48
2 200 37.23
3 200 39.20
4 400 70.76
5 400 78.40
6 500 98.00
7 600 117.60
8 700 137.20
9 800 156.80
10 900 176.40
11 1000 196.00
12 1000 196.00
0
200
400
600
800
1000
1200
123456 789101112
We e k s
Amount of feedstock (kg)
Figure 4: The amount of feedstock used by week
Based on Fig. 4, it is shows the increasing of the number of the feedstock by the weeks. This
MBPP already function about 3 months, and at the week 11 to week 12 the number of feedstock’s are
remain constant. On the other hand, according to Fig. 5 shows the amount of methane gas produced
per week where the production of methane gas production increases when the feedstock increases. At
the beginning, the number of feedstock is 200kg and the number of methane gas produced is around
35.48, 37.32 and 39.20 respectively.
Emerging Technology for Sustainable Development Congress (ETSDC 2014)
01012-p.5
0
50
100
150
200
250
123456789101112
We e k s
Methane Gas Production (m
3
)
Figure 5: The amount of methane gas produced per week
Fig. 6 shows the number of electric generated increase by weeks is remains constant at the
week 11 and 12 with the amount of 646.80kW. It clearly visualised that the amount of electric power
increase by weeks.
0
100
200
300
400
500
600
700
123456789101112
We e k s
Electric Power (kW)
Figure 6: The number of electric power generated per week
4. Conclusions
The most suitable power plant system to be installed at remote area is mini biogas power plant
compared to solar energy system because of several reasons. First of all, this mini biogas power plant
is easy to set-up because it is made in a modular system that could be installed or uninstalled and
transferred easily everywhere and anywhere. When there is a human, there will be waste. It is not hard
to collect the wastes to be used in generating the energy rather than waiting for the sunlight that is
dependable on the weather. If it is raining season, they villagers will not suffer to stay in dark at night
E3S Web of Conferences
01012-p.6
and feeling hot during the day. The generator will work 24 hours to generate electricity as long as
there are wastes and the generator have enough fuels to work.
If there is 1000kg waste per day, the mini biogas power plant can generate about 180 cubic metre
methane gas and 600kW electricity per day. The waste produced should be enough to support this
system. It is acceptable if the waste is lower than 1000kg per day, as long as it could support all the
needs that the people demand at their place. The higher the amount of wastes could produce the higher
the amount of electricity.
References
1. Corral, M., M. Argelia, 2007. Biogas production via anaerobic digestion of high solids livestock
manures, PhD thesis, New Mexico State University, 593-599
2. Babel, S., J. Sae-Tang, A. Pecharaply, 2009. Anaerobic co-digestion of sewage and brewery
sludge for biogas production and land application. International Journal of Environmental Science
and Technology, 6 (1): 131-140.
3. Ilaboya, I.R., F.F. Asekhame, M.O. Ezugwu, A.A. Erameh, F.E. Omofuma, 2010. Studies on
Biogas Generation from Agricultural Waste; Analysis of the Effects of Alkaline on Gas
Generation. World Applied Sciences Journal 9 (5): 537-545
4. Wiley, P.E., J. Campbell, B. McKuin, 2011. Water Environment Research, Production of
Biodiesel and Biogas from Algae: A Review of Process Train Options. Water Environment
Research, 83 (4): 326-338
5. Ofori-Boateng, C., E.M. Kwofie, 2009. Water Scrubbing: A Better Option for Biogas Purification
for Effective Storage. World Applied Sciences Journal 5 (Special Issue for Environment), 122-
125
6. Ilyas, S.Z., 2006. A Case Study to Bottle the Biogas in Cylinders as Source of Power for Rural
Industries Development in Pakistan. World Applied Sciences Journal, 1 (2): 127-130
7. Rapport, J.L., 2011. Large scale anaerobic digestion of food processing waste and pre-treatment
of agricultural residue for enhancement of biogas production, 12: 23-29
8. Waqar Bhatti, M., 2012. Mini biogas plant reducing dependence on the firewood, International
The News, Karachi, 54: 42-53
9. Ahn, H.K., M.C. Smith, S.L. Kondrad, J.W. White, 2012. Evaluation of Biogas Production
Potential by Dry Anaerobic Digestion of Switch grass–Animal Manure Mixtures, Applied
Biochemistry and Biotechnology, 160 (4): 965-975
10. 10. Najafi, Z. N. Jaafarzadeh, 2007. Biogas Production From Animal Manure And Vegetable
Wastes, The Social Contex, 48 (2): 52-54
11. Manikam, N.S.T., 2012. Report of Biogas Production From The Municipal Waste, B.Sc final year
project, Faculty of Engineering and Science, Universiti Tunku Abdul Rahman, 432-437
Emerging Technology for Sustainable Development Congress (ETSDC 2014)
01012-p.7
... The case study of a mini biogas power plant installed in a remote area found that the electric power generated was 600 kW, and 182 m 3 of methane gas was produced daily with food waste input of 1000 kg per day. This energy system could provide 24-hour electrification if the waste supply is continuous and the generator does not run out of biogas [42]. Another Australian case study estimated biogas yields and assessed the feasibility of utilising biogas, total conversion of food waste can reduce greenhouse gas emissions (GHG) by up to 5,07,434 tonnes per year and generate $52.38 million. ...
Article
Full-text available
The effort of electrifying Sarawak also comes with challenges mainly caused by geographic and demographic factors. Sarawak’s population scatters over a wide spatial area, where families inhabit small villages located in areas of challenging terrains and thick jungles. As a result, electrification through grid connection becomes infeasible and uneconomic. Biogas has immense potential to contribute to energy supply, especially in rural areas. It not only reduces waste but can also be used in generating electricity and subsequently reduces the dependency on fossil fuels. Approximately 993,000 hectares of Sarawak land were planted with oil palm in 2019. The predicted biogas generation from palm oil mill effluent (POME) could create enough electricity to power nearly 2 million rural Sarawak households, in which the Sarawak population in 2020 was 2.9 million. The lagoon system and continuous stirred tank reactor are common technologies used in biogas production. Other technologies used in biogas production are the fixed dome reactor from the Chinese model and the floating dome reactor from the Indian model. The standard technology involves the combustion of biogas in a heat engine called an internal combustion engine to produce heat to generate steam that drives a turbine for electricity generation. This work studied a new biogas utilisation method, fuel cell technology. Solid oxide fuel cell (SOFC) has high efficiency of up to 60% and is generally more prominent than conventional combustion of biogas in a gas engine to generate electricity. With the continual development of biogas fuel cells, a great prospect is predicted for rural areas of Sarawak in biogas production and utilisation. Thus, biogas could contribute a larger role in contributing to a higher renewable energy mix and rural electrification in Sarawak.
... Also, in Mydin et al. (2018) it was found that mini biogas power plant installed in Universiti Sains Malaysia can generate about 180 cubic meter methane gas and 600KW electricity per day when the food waste collected from cafeterias and canteens is 1000 kg/day and in Thi et al. (2016) found that the cost of energy produced using food waste is very low as compared to other renewable energy sources such as solar and wind energy. ...
Chapter
Full-text available
In this chapter, a solar-based multigeneration system is examined in terms of heating, cooling and electricity generation capacity, as well as energy and exergy efficiencies. Through this sun-powered system, multiple useful outputs are obtained and utilized for a sustainable community. Moreover, two molten storage tanks with higher and lower temperatures are used to minimize energy imbalances in the system. While the energy required for the system is supplied from the solar tower, electricity and heat are produced to the community with the Brayton-Rankine combine cycle. Furthermore, the desired cooling is obtained with the absorption refrigeration system powered by the rejected heat from the Brayton cycle. The overall energy and exergy efficiencies of the system are found to be 69.33% and 41.81%, respectively.KeywordsSolar energyEnergyExergyEfficiencyTrigenerationSustainable community
... Leftovers (SF) is the main component of FW and a potential source of environment-friendly biodegradable materials, which is rich in starch, cellulose, fat and other organic substances [12]. Therefore, in recent years, SF has gradually been used to prepare hydrogels [12], bioplastics [13] and biogas [10,14,15]. Controlled-release fertilizers (CRFs) had been widely applied in many plants over the past decades, as they increased fertilizer efficiency and crop yield, and minimized environmental pollution resulting from lost fertilizers [16][17][18]. ...
Article
Full-text available
In this work, a novel bio-based polyurethane (PU) was synthesized by using a leftovers (SF)-based polyol and isocyanate for controlled release fertilizers (CRFs). Its chemical structure, surface elemental compositions and distribution were examined by Fourier transform infrared (FTIR), energy dispersive spectroscopy (EDX) and a multifunctional imaging electron spectrometer (XPS). The microstructure morphology of CRFs were examined by SEM. The nutrient release behaviors of CRFs were observed in water. The results demonstrated that SF-based PU-coated urea (FPU) had a denser structure and better nutrient releasing ability. Findings from this work indicated that the use of SF as a coating material of environment-friendly CRFs had great potential, and would hopefully be used for horticultural and agricultural applications.
... The bioenergy potential from FW, according to USEPA, is found to be about 376 m 3 of biogas that can be generated by 1000 kg FW (US-EPA 2017). Guerrero et al. (2013) and Mydin et al. (2014) estimated that the same quantity of FW could produce 247 and 180 m 3 of methane, respectively. Whereas, Thi et al. (2016) reported that 220 kWh of electricity could be generated through AD from 1 ton of FW. ...
Article
Full-text available
The energy crisis has always hampered economic growth in Pakistan. This is largely caused by poor management, policy deiciencies, and low interest towards non-conventional sources of energy. Pakistan’s current energy generation capacity is approximately 14,000–16,000 MW by combining all generation sources, such as hydro, thermal, and nuclear. In contrast, the demand is about 20,000–22,000 MW. This discrepancy results in a shortfall of 4000–6,000 MW. To ill this gap, renewable energy sources must be used to produce additional energy. Hence, this paper evaluates the bioenergy potential from food waste (FW) through anaerobic digestion (AD). In eight mega-cities in Pakistan, the current FW generation is about 9.8 metric tons per day and this would reach as high as 14.8 metric tons by the year 2030. In ideal conditions, this quantity of FW could produce 1.96 million m3 and 2.96 million m3 of biogas each day by 2017 and 2030, respectively. Furthermore, the paper discusses the aspects regarding electricity generation as well as the economic beneits that can be obtained by the energy recovery of FW.
... The bioenergy potential from FW, according to USEPA, is found to be about 376 m 3 of biogas that can be generated by 1000 kg FW (US-EPA 2017). Guerrero et al. (2013) and Mydin et al. (2014) estimated that the same quantity of FW could produce 247 and 180 m 3 of methane, respectively. Whereas, Thi et al. (2016) reported that 220 kWh of electricity could be generated through AD from 1 ton of FW. ...
Conference Paper
The energy crisis have always hampered the economic growth in Pakistan. This is majorly caused by improper management, policy lacks, and non seriousness towards the non conventional resources of energy. Pakistan’s current energy generation is about to 16,000MW by combining all sources such as hydro, thermal, and nuclear. Whereas the demand is about 20,000MW leaving the shortfall of 4,000MW. To meet this gap efficiently, the renewable energy resources must be tapped and extracted the energy. In Europe and many other countries have reformed their energy curriculum and included the exploitation of energy from renewable resources. In this paper, the energy potential from renewable energy sources is highlighted. Furthermore, organic fraction of municipal solid waste (OFMSW) is focused and its current and future prospectus of bioenergy (i.e. biogas) potential is discussed. This study also concludes that, the electricity generation from the renewable biogas energy through anaerobic digestion (AD) could be possible way to fill the gap.
Chapter
The reduction of greenhouse gases (GHG) and Carbon foot prints are the main objectives decided by the organizations worldwide working for the clean and pollution free environment and sustainability for the future generations. This can only be achieved if the dependency on fossil fuels is reduced and the clean energy is used instead. The usage of renewable energy resources is the need of the time. In this chapter we discuss the bioenergy technologies and how the biowaste produced in the universities can be successfully utilized to produce clean energy. The educational institutes such as colleges and universities can not only be used to educate the future generations regarding the sustainability but in fact can put their contribution in clean and renewable energies by research and development. The concept of Green Campuses can be used as a practical implementation of new clean technologies besides research and development of the new renewable energy resources. The current engineering technologies that can be used to convert campus food waste into bio energy are provided for the production of bio energy that can help the university campus reduce the dependency on the fossil fuels by using the produced energy not only for making food for students but as a source of fuel for on campus transportation, electric and heating requirements. Also, different case studies have been presented from the campuses around the world regarding production of bio energy and conversion of this energy into electricity and gas using Anaerobic Digesters and combined heat and power plants. These case studies show the effectiveness of the bioenergy production concept implementations.KeywordsRenewable energy resourcesSustainabilityFood energyBio energyCombined heat powerWaste to energyEnvironmentFood management
Article
Full-text available
This study investigates the digestion of cow dung (CD) for biogas production at laboratory scales. The study was carried out through anaerobic fermentation using cow dung as substrate. The digester was operated at ambient temperatures of 39.5 °C for a period of 10 days. The effect of iron powder in controlling the production of hydrogen sulfide (H2S) has been tested. The optimum concentration of iron powder was 4g/L with the highest biogas production. A Q – swatch Nd:YAG laser has been used to mix and homogenize the components of one of the six digesters and accelerate digestion. At the end of digestion, all digestions effluent was subjected to 5 laser pulses with 250mJ/pules to dispose waste biomass.
Chapter
Food processing is a major thriving industry globally and provides livelihood to millions of workers. Food processing is an energy intensive process and often has an impact on the environment which remains undiagnosed and hence not quantified. Food processing industry comprises the organized as well as unorganized sector with varying levels of energy requirement and therefore the carbon foot prints also significantly vary. Higher energy use is often related to higher greenhouse gas (GHG) emission which is responsible for global warming and climate change. Carbon footprint (CFP) of food industry is an estimate of the energy use and GHG emissions caused due to the processing and delivery of food items to the consumer and also disposal of packaging. Recently there is a growing interest in estimating the carbon footprint of food industries to know how improved technologies can be used to make food processing less energy and carbon intensive. In this book chapter we would like to provide an overview of energy use and carbon footprint of different types of food industries. Quantification of CFP is generally done using Life Cycle Assessment (LCA) in which GHG emissions are measured from the very beginning of the production process to its final use and disposal. GHG emission from a food industry will include both direct emissions as well as indirect emissions. The CFP of different sectors like fruit and beverage industry, sugar production, dairy sector, fisheries, meat and poultry supply chains are presented. Apart from this, research gaps and possible steps to minimize the carbon footprint will be mentioned. Assessing the CFP of food industries can help in identifying the GHG sources and can be useful in developing alternative technologies which are more energy efficient and reduces GHG emission. Further, change in dietary pattern also contributes immensely to reduce the environmental impact of food consumption.
Article
Full-text available
This study investigates the digestion of cow dung (CD) for biogas production at laboratory scales. The study was carried out through anaerobic fermentation using cow dung as substrate. The digester was operated at ambient temperatures of 39.5 °C for a period of 10 days. The effect of iron powder in controlling the production of hydrogen sulfide (H2S) has been tested. The optimum concentration of iron powder was 4g/L with the highest biogas production. A Q – swatch Nd:YAG laser has been used to mix and homogenize the components of one of the six digesters and accelerate digestion. At the end of digestion, all digestions effluent was subjected to 5 laser pulses with 250mJ/pules to dispose waste biomass.
Article
Full-text available
This study investigates the digestion of cow dung (CD) for biogas production at laboratory scales. The study was carried out through anaerobic fermentation using cow dung as substrate. The digester was operated at ambient temperatures of 39.5 °C for a period of 10 days. The effect of iron powder in controlling the production of hydrogen sulfide (H2S) has been tested. The optimum concentration of iron powder was 4g/L with the highest biogas production. A Q – swatch Nd:YAG laser has been used to mix and homogenize the components of one of the six digesters and accelerate digestion. At the end of digestion, all digestions effluent was subjected to 5 laser pulses with 250mJ/pules to dispose waste biomass.
Article
Full-text available
Concerns over the environment and the rising costs for energy and wastewater treatment have caused a resurgence of interest in anaerobic treatment and subsequent use of the biogas produced during this treatment of organic wastes as fuel. Biogas from faecal and landfill wastes has become a potential renewable energy source for both domestic and commercial usage especially in Ghana where a 50MW capacity waste-to-power plant is undergoing construction. In addition, an average total capacity of about 95MW biogas plants is in operation in other parts of the country. Due to the presence of carbon dioxide (CO) and hydrogen 2 sulphide (H S) in biogas, it has become extremely difficult to transport and store it effectively especially where 2 it's produced in commercial quantities. Thus the need emerges for a unified approach for scrubbing, compression and subsequent storage of biogas for wider applications. This paper presents the developments in biogas purification and storage into steel propane and butane tanks (requiring a medium pressure of 1.05-1.97bar) for easy and cost effective transportation and utilization. The paper also presents water scrubbing as a better option for biogas purification in Ghana.
Article
Full-text available
Pakistan is one of the developing countries with very low energy consumption, correspondingly low standard of living and high population growth. The country is trying to improve its living standards by increasing its energy consumption and establishing appropriate industries. It has immense hydropower potential, which is almost untapped at the present time. Employment generation and poverty alleviation are the two main issues related with rural development. These issues can be tackled by rural industrialization using local resources and appropriate technologies. However, sufficient number of industries can not be set up in rural areas so far due to scarcity of energy supply i.e. electricity, diesel etc. Biogas, a renewable fuel may be able to fill the gap in energy availability in the rural areas. Biogas can supply energy near to biogas plant which makes it hindrance in its wide spread application and therefore mobility of biogas is must, which is achieved by bottling of biogas. Here a model is conceptualized to bottle the biogas in cylinders and then use it to power the rural industries. It is found that use of bottled biogas can save diesel of the worth US $ 147 in 12 hours and also generate employment for 12 persons.
Article
Full-text available
In Thailand, sewage sludge production from the Bangkok metropolitan area can reach up to 63,000 ton/y by 2010. The Beer-Thai Company, Thailand, produces beer and generates lots of sludge as waste. Sewage sludge and brewery sludge can be used to generate energy which could be saved on the fossil fuels conventionally used as a source of energy. The possibility was explored to mix brewery sludge with sewage sludge at different mixing ratios for anaerobic digestion so that the energy can be generated as biogas and at the same time, digested sewage sludge can be used as fertilizer for agricultural applications. A batch anaerobic reactor under mesophilic condition for a digestion period of 40 days was used in the laboratory. The acrylic reactor was cylindrical with a working weight of 12 kg. The diameter was 23.7 cm and the height was 34.5 cm. Sludge mixtures at different ratios were fed into the reactors and the optimum mixing ratio was determined. Experimental results showed that the sludge mixture at ratio of 25:75 % by weight (sewage:brewery) yielded higher biogas production. A reduction in heavy metals and pathogens was observed at this ratio after the digestion indicating its safe use as fertilizer. Nitrogen content was about 4.95 % which is well above the commercial fertilizers. At optimum mixing ratio of 25:75, the amount of the generated biogas is 1.15x106 m3/y. This large amount of biogas is equivalent to 1.44 million kWh/y of electricity, 561,000 L/y of diesel oil and 936,000 L/y of vehicle gasoline.
Article
Full-text available
Anaerobic digestion is a biological method used to convert organic wastes into a stable product for land application with reduced environmental impacts. The biogas produced can be used as an alternative renewable energy source. Dry anaerobic digestion [>15% total solid (TS)] has an advantage over wet digestion (<10% TS) because it allows for the use of a smaller volume of reactor and because it reduces wastewater production. In addition, it produces a fertilizer that is easier to transport. Performance of anaerobic digestion of animal manure-switchgrass mixture was evaluated under dry (15% TS) and thermophilic conditions (55 degrees C). Three different mixtures of animal manure (swine, poultry, and dairy) and switchgrass were digested using batch-operated 1-L reactors. The swine manure test units showed 52.9% volatile solids (VS) removal during the 62-day trial, while dairy and poultry manure test units showed 9.3% and 20.2%, respectively. Over the 62 day digestion, the swine manure test units yielded the highest amount of methane 0.337 L CH4/g VS, while the dairy and poultry manure test units showed very poor methane yield 0.028 L CH4/g VS and 0.002 L CH4/g VS, respectively. Although dairy and poultry manure performed poorly, they may still have high potential as biomass for dry anaerobic digestion if appropriate designs are developed to prevent significant volatile fatty acid (VFA) accumulation and pH drop.
Article
Two types of anaerobic biogas production units, floating gas holder and fixed dome are applied in pilot scales using a combination of manure and vegetable wastes as raw materials in the reactor. Feedstocks are mixed and loaded into the biogas reactors. Tests were conducted on humidity, pH, phosphorus, sulfur, nitrogen, electrical conductivity, total solids, total dissolvable and nondissolvable solids and fecal coliform. Results showed that more than 70% of produced gas is methane and that the fixed dome Chinese reactor is more efficient than the Indian type.
Article
Algae are an attractive biofuel feedstock because of their fast growth rates and improved land use efficiency when compared with terrestrial crops. Process train components needed to produce algal biofuels include (1) cultivation, (2) harvesting, and (3) conversion into usable fuel. This paper compares various process train options and identifies knowledge gaps presently restricting the production of algal biodiesel and algae-derived biogas. This analysis identified energy-intensive processing and the inability to cultivate large quantities of lipid-rich algal biomass as major obstacles inhibiting algal biodiesel production. Anaerobic digestion of algal biomass requires fewer process train components and occurs regardless of lipid content. In either scenario, the use of wastewater effluent as a cultivation medium seems necessary to reduce greenhouse gas emissions and maximize water use efficiency. Furthermore, anaerobically digesting algal biomass generated from low-technology wastewater treatment processes represents an appropriate technology approach to algal biofuels that is poorly investigated. Coupling these processes can improve global health by improving sanitation, while providing a cleaner burning biogas alternative to indoor biomass cooking systems typical of less-developed areas.
Article
Thesis (Ph. D.)--New Mexico State University, 2007. Includes vita. Includes bibliographical references (leaves 263-289).
Report of Biogas Production From The Municipal Waste, B.Sc final year project
  • N S T Manikam
Manikam, N.S.T., 2012. Report of Biogas Production From The Municipal Waste, B.Sc final year project, Faculty of Engineering and Science, Universiti Tunku Abdul Rahman, 432-437
Large scale anaerobic digestion of food processing waste and pre-treatment of agricultural residue for enhancement of biogas production
  • J L Rapport
Rapport, J.L., 2011. Large scale anaerobic digestion of food processing waste and pre-treatment of agricultural residue for enhancement of biogas production, 12: 23-29