ABSTRACT
This study was carried out to investigate the microorganisms associated with the co-digestion of cassava peel, pig dung and cow rumen fluid for the production of biogas. These wastes were collected between July and August 2018 while the experimental studies were carried out between September and October 2018. The animal wastes were used as collected without further treatment. The blending ratio was 1:1:1 (10kg of each) and was initially mixed with water in the ratio of 1:2 (10kg of waste 20kg of water) and fed into a 15 liters laboratory scale anaerobic digester using improved rubber water dispensers (35cm diameter, 55cm high). The anaerobic digestion process was batch operated for 30 days under room temperature conditions. In order to achieve homogeneity of the slurry and discourage scum formation in the system, daily stirring was carried out using the inbuilt manual stirring mechanism in the digester. The physicochemical and microbial parameters of the slurry samples analyzed using prescribed equipments and standard methods. Daily biogas production was monitored and volume of gas measured using downward displacement method. The maximum biogas production was 1.90 Ld-1 for total anaerobic count of 3.61 x 106 cfu/mL and mean fungal count of 2.11 x 106 cfu/mL observed at the 16th day of biodigestion. The results indicate the incidence of Clostridium sp; Streptococcus sp, Lactobacillus sp; Bacillus sp, Micrococcus sp, Pseudomonas sp, Enterobacter sp, Fusarium sp, Aspergillus sp and Mucor sp were isolated and identified in slurry of the codigestion of a cassava peel, pig dung and cow rumen fluid.
TABLE OF CONTENTS
Title Page i
Certification ii
Dedication iii
Acknowledgements iv
Table of Contents v
List of Tables vii
List of figures viii
Abstract ix
CHAPTER 1
INTRODUCTION
1.1 Aim and Objectives of the Study 3
CHAPTER 2
LITERATURE REVIEW
2.1 History of Anaerobic Digestion (AD) 5
2.2 Anaerobic Co-digestion of Organic Wastes 7
2.3 Anaerobic Digestion Technology 8
2.3.1 Types of anaerobic digesters 9
2.3.2 System of anaerobic digesters 9
2.3.3 Modes of anaerobic digester 10
2.4 Maximizing Biogas Production through
Co-digestion 11
2.4.1 Factors Affecting Anaerobic Digestion
Efficiency 13
2.4.1.1 pH Level
13
2.4.1.2 Temperature
13
2.4.1.3 Mixing 14
2.4.1.3 Total Solid (TS) 15
2.4.1.4 Carbon to Nitrogen Ratio (C/N) 15
2.4.2 Advantages of Anaerobic Digestion to the
Society 16
2.4.2.1
Odour Control 16
2.5 Literature Study on Various Feedstock 16
CHAPTER 3
MATERIALS AND METHODS
3.1 Study Area and Sample Collection 19
3.2 Materials 19
3.3 Methods 19
3.4 Microbial Analysis 20
3.4.1 Biochemical Tests 21
3.5 Physicochemical Analysis 23
3.6 Determination of Biogas Production 26
3.7 Data Analysis and Confirmation of Results 27
CHAPTER 4
RESULTS AND DISCUSSION
4.1
RESULTS 28
4.2 DISCUSSION 33
CHAPTER 5
5.1 CONCLUSION 35
REFERENCE
APPENDIX I
APPENDIX II
LIST OF TABLES
Table
4.1 Substrate and Microbial Composition 29
Table
4.2 Mean Anaerobic and Fungal Count 30
Table
4.3 Physicochemical Characteristics of Slurry For 30 Days 31
Table
4.4: Mean Volume Of The Biogas Produced 32
CHAPTER 1
INTRODUCTION
There
is an increasing interest in biogas and bioenergy production across the world
for environmental and economic reasons. The production of biogas contributes to
the production of renewable and sustainable energy since biogas works as a
flexible and predictable alternative for fossil fuel (Igoni et al., 2008).
Biogas
can be produced from various organic wastes types. Besides energy production,
the degradation of organic waste through anaerobic digestion offers other
advantages such as the prevention of odor release and decrease of pathogens
(Derbal et al., 2008). Moreover the
nutrient rich digested residues can be utilized as fertilizer for recycling the
nutrients back to the fields.The production of biogas via anaerobic digestion
of large quantities of agricultural residues and organic waste benefit the
society by providing clean fuel from renewable sources and help end energy
poverty. As a renewable high quality fuel biogas can be utilized for various
energy services. This would reduce
dependence on fossil derived energy and reduce environmental impact including
global warming and pollution, improve sanitation and provide high quality
fertilizer. It has been evaluated as one of the most energy efficient
technology for bioenergy production (Fehrenbach et al., 2008). It can reduce green house gas emissions compared to
fossil fuels by utilization of locally available resources (Olowolafe, 2008).
Anaerobic
digestion consists of several interdependent complex, sequential and parallel
biological reactions during which the products from one group of microorganisms
serve as the substrates for the next resulting in the transformation of
organics mainly into a mixture of methane and carbon dioxide with minor
quantities of nitrogen, hydrogen, ammonia and hydrogen sulphide (Olayiwola et al., 2011).
Anaerobic
fermentation of organic wastes is a complex process which can be divided into
four phases, hydrolysis, acidogenesis, acetogenesis/dehydrogenation and
methanation. The individual fermentation steps are carried out by different
consortia of microorganisms which mostly stand in syntrophic interrelation and
place different requirements on the environment (Angelidak et al., 1993). Hydrolyzing microorganisms are responsible for the
initial attack on organic polymers and reduce mainly acetate, hydrogen and
varying amounts of volatile fatty acids into acetate and hydrogen, completing
acidiogenesis acetogenesis and dehydrogenation. At the end of the degradation
chain methanogens produce methane from acetate or hydrogen and carbondioxide
(Angelidak et al., 1999). The whole
anaerobic fermentation for biogas production is difficult to describe by
reliable kinetics since hydrolysis, acidogenesis, acetogenesis and gas
production through complex insoluble substrate depends on many different
parameters such as size, production of enzymes pH and temperature.
All
types of organic waste can be used as substrate for biogas production as long
as it contains carbohydrate, proteins, fats, cellulose and hemicelluloses as
constituents. The composition of biogas yield depends on the organic substrate,
the digestion system and retention/incubation time (Charles et al., 2009).
Anaerobic
digestion has mainly been associated with the treatment of animal manure and
sewage sludge from aerobic wastewater treatment. Today, most biogas production
plants digest waste from pigs, cow and other animals with the addition
co-substrates to increase the content of organic materials for achieving a
higher gas yield. Typical co-substrates are plants residues e.g. peels, leaves
of food crops, organic wastes food waste and energy crops. The biogas yield of
the individual substrates varies considerably dependent on their origin content
of organic substance and substrate composition, fats provide the highest biogas
yield but require a long retention time due to their poor bioavailability
carbohydrates and proteins show much faster conversion rates but lower gas
yields. The contents of nutrients respectively the carbon/nitrogen ratio should
be well balanced to avoid process failure by ammonia accumulation. The
carbon/nitrogen (C/N) ratio should be in the range between 15 and 30 (Ward et al., 2008). In Nigeria identified
feedstock substrate for feasible biogas production include water lettuce, water
hyacinth, dung, cassava leaves and processing wastes, urban refuse, solid waste
agricultural waste, residues and sewage. It has been estimated that Nigeria
produce about 227,500 tons of fresh animal waste daily. Since 1kg of fresh
animal waste produces about 6.8 million m3 of biogas everyday from
animal waste only (Akinbami, et al., 2001).
In
order to fill some gaps existing in previous studies of the codigestion of
cassava peel with other waste types, there is the need to study the effect of
the addition of cow rumen fluid into the feed stock blends in a 1:1:1 mix ratio
with cassava peels and pig dung. However the microbial diversity and especially
possible the interactions between the microbial communities in waste blends of
cassava peels, cow rumen fluid and pig
dung has not yet received much attention. This knowledge however is required to
identify the key microorganisms of use for efficient organic degradation and
biogas production.
1.1 Aim
and Objectives of the Study
This
research work aims at investigating the microorganisms associated with the
co-digestion of cassava peel, cow rumen fluid and pig dung for the production
of biogas.
The
objectives of the study include:
· To
isolate, identify and characterize the microorganisms involved in the anaerobic
co-digestion of the substrates.
· To
determine the mean anaerobic and fungal load of the substrate slurry for 30
days.
· To
analyse the physicochemical characteristics of substrates during digestion.
· To
measure the daily biogas volume produced.
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