ABSTRACT
This study evaluated the isolation and identification of biodegrading fungal species. The sites (Umudike mechanic workshop and Imo lane mechanic workshop) used for this study are designated areas for automobile repairs, petrol/diesel pump sites and generator repairs. Samples collected were cultured on Sabouraud Dextrose Agar using both streak and pour plate techniques. Two (2) fungal species, namely Penicillium spp, and Rhizopus spp were isolated and identified based on Morphological and cultural features from engine oil–contaminated soil in this study as responsible for the biodegradation of the engine oil. The presence of these fungi in soil samples indicated that the isolates were able to exist in the oil contaminated environment while those that could not survive in this environment being eliminated by the unfavorable conditions caused by the oil. The results from the Zone Diameter Produced on Modified 1% Condemned Oil Agar showed that Penicillium spp had higher ability to degrade the engine oil as the day of incubation increased. Rhizopus spp also exhibited the ability to utilize the engine oil as its sole source of energy at day 6 but had lesser zone of inhibition compared to Penicillium spp. Therefore, it was seen that the rate of engine oil degradation by Penicillium spp. was faster as the days increased compared to the rate of degradation of engine oil by Rhizopus spp and mixture of Penicillium spp. and Rhizopus spp. Therefore, the study has also shown that fungi play a role in the biodegradation of oil contaminating soils in the environment. Studies have indicated that biodegradation by fungi could be due to their massive growth and enzyme production responses during their growth phases. Thus in future they can be effectively utilized for the degradation of oil and petroleum products as well as for biodegradation of soil already polluted with oil.
TABLE OF CONTENTS
Title Page i
Certification iii
Dedication iv
Acknowledgements v
Table of Contents vi
List of Tables vii
Abstract ix
CHAPTER ONE
1.0 Introduction 1
1.1 Aim of Study 4
1.2 Specific Objectives 4
CHAPTER TWO
2.0 Literature Review 5
2.1 Oil
Pollution 5
2.2 Bioremediation
Strategies Oil Contaminated Surfaces 6
2.3 Micro
Organisms Important for Petroleum Product Biodegradation 8
2.4 Factors
Affecting Biodegradation of Hydrocarbon 8
2.4.1 Temperature
9
2.4.2 Nutrients
9
2.4.3 Oxygen
9
2.4.4 pH 10
2.5 Mechanism
of Hydrocarbon Degradation 10
2.5.1 Degradation
Pathway for Aliphatic Compounds 10
2.5.2 Degradation
Pathway for Aromatic Compounds 10
2.6 Isolation and Identification of Some
Micro Organisms from Polluted Soil with
Diesel around Powered Generators 11
2.7 Isolation of Oil Degrading
Microorganisms, Identification of Catechol
Gene and Its Biogas Production 12
2.8 Isolation Identification and
Characterization of Potential Oil Degrading
Bacteria from Oil Contaminated Sites 14
2.8.1 Enrichment of Microorganisms and Screening
of Microorganisms 14
CHAPTER THREE
3.0 Materials and Methods 16
3.1 Study Area 16
3.2 Source of Sample/Collection 16
3.3 Sterilization of Materials 16
3.4 Media Preparation 16
3.5 Fungal Evaluation 17
3.6 Sample Preparation and Isolation of Fungi 17
3.6.1 Sample Inoculation/Serial Dilution 17
3.6.2 Isolation and Culturing of Fungi 17
3.6.3 Isolation of Fungi 18
3.6.4 Purification of Fungi Isolates 18
3.6.5 Test for Biodegradation of Fungi spp From
Contaminated Soil of Spent Oil 18
3.7 Identification of the Fungi Isolates 19
3.8 Morphological Identification 19
3.8.2 Colonial Morphology 19
3.8.1 Cultural Characteristics 19
CHAPTER FOUR
4.0 Results 20
CHAPTER FIVE
5.0 Discussion, Conclusion and
Recommendations 23
5.1 Discussion 23
5.2 Conclusion 25
5.3 Recommendation 25
References
LIST OF TABLES
S/N
|
TITLE
|
PAGE NO
|
1
|
Microorganisms Reported
For Degradation of Petroleum Hydrocarbon
|
8
|
2
|
Cultural Morphology and
Microscopic Characteristics of Fungal Isolates from
Engine Oil Contaminated
Soil Samples
|
21
|
3
|
Zone Diameter Produced
On Modified 1% Condemned Oil Agar
|
22
|
CHAPTER ONE
1.0 INTRODUCTION
In
Nigeria, it is common among motor mechanics to dispose spent engine oil into
gutters, water drains and soil (Okonokhua et al., 2007). Used engine oil
is defined as used lubricating oils obtained after servicing and subsequently
draining from automobile and generator engines. Spent oils contain high
percentage of aromatic and aliphatic hydrocarbons, nitrogen and sulphur
compounds and metals (Mg, Ca, Zn, Pb) than fresh oils. These metals are
introduced into the oil as a result of wear and tear of the engine (Mohd et
al., 2011). Used engine oil causes great damage to soil and soil
microflora. It creates unsatisfactory condition for life in the soil due to
poor aeration, immobilization of soil nutrients and lowering of soil pH (Ugoh
and Moneke, 2011). It has been shown that marked changes in properties occur in
soil contaminated with hydrocarbon; this affects the physical, chemical and
microbiological properties of the soil (Okonokhua et al., 2007). At low
concentrations, some of these heavy metals are essential micronutrients for
plants, but they can cause metabolic disorders and growth inhibition when the
concentration is high. Therefore, there is the need for bioremediation of
hydrocarbon contaminated soil.
Engine
oil could also be simply referred to as a thick mineral liquid applied in a
machine or engine so as to reduce friction between the moving parts of the
machine (Whitefield, 2002). Used engine oil as the name implies represent oil
that has undergone destructive changes in property when subjected to oxygen,
combustion gases and high temperature. The said oil also undergoes viscosity
change as well as additive depletion and oxidation, these occur to degrade oil
(Mark et al., 2002).
Microorganisms
such as fungi are extremely diverse and can adapt to survive in inhospitable
environments. Microbes are capable of breaking down many complex molecules by
adaptation of their degradative enzyme system (Boonchan et al., 2000). The survival of these microbes in altered
environment depends on their ability to produce endospore and vegetative cell,
which can stand harsh and unfavorable environment. These changes affect plants
adversely and the amount of damage depends on the size of the area involved and
the degree of saturation by the pollutant (Isinguzo and Bello, 2005).
Used
oil is defined by the US Environmental Protection Agency as oil that has been refined
from crude oil or any synthetic oil; that has been used and as a result of such
use, it has been contaminated by chemical impurities which contribute to
chronic hazards; including: mutagenicity and carcinogenicity as well as environmental
hazard with global ramifications (Blodgette, 2001). Bioremediation has become
an alternative way to remedy oil polluted sites, where the addition of specific
microorganism (bacteria, cyanobacteria, algae, fungi, protozoa) or enhancement
of microorganism already present, can improve biodegradation efficiency (Hagwell
et al., 1992). These
microorganisms can degrade a wide range of target constituents present in oil sludge
(Mishra et al., 2001). A large
number of pseudomonas strains capable of degrading polycyclic aromatic
hydrocarbons have been isolated from soil (Johnson et al., 1996).
Other
petroleum hydrocarbon degraders include Yokenella spp., Alcaligenes spp.,
Roseomanas spp., Sreanotrophomanas spp., Acinetobacter spp.,
Flavobacter spp., cyanobacterium spp., capnocytophage spp.,
Moraxella spp. and Bacillus spp. (Bhattacharya et al., 2002). Other microorganism such
as fungi is also capable of degrading the hydrocarbons in engine oil to a
certain extent. However, they take longer period of time to grow compared to
their bacterial counterparts (Prenafeta-Boldu et al., 2001). Petroleum products such as engine oil, petrol,
diesel and kerosene are used daily in various forms in mechanic workshops.
These products tend to harden and change the colour of the soil, which may have
untold health hazard on the technicians and artisans. Their soles tend to
harden, which may alter their movement.
Soil
contamination is the presence of unwanted impure materials from human
activities. It can also be the distortion of the soil environment by human
activities. Soil is the habitat for variety of organisms, including; fungi,
bacteria, protozoa, insects, nematodes, worms, and many other animals. Viruses
are also present in soils. This complex biological community contributes to the
formation, maintenance, and in some situations, the degradation and
disappearance of soils (Prescott et al.,
2005).
Biodegradation
plays an important ecological role as it contributes to bioremediation.
Nowadays, the role of fungi has been extensively studied to be the most
potential degraders of oil and petroleum products than other traditional
bioremediation techniques (Sood and Lal, 2009). Filamentous fungi are
considered to be better degraders of oil and petroleum than bacteria, because they can degrade high
molecular weight polycyclic aromatic hydrocarbons whereas bacteria degrade
smaller molecules (Whang et al.,
2009). Another reason which enables them as good potential agents of degradation
is to produce extracellular enzymes for the digestion of complex carbohydrates
which further causes the degradation of hydrocarbon pollutants (Whang et al., 2009). Another advantage is that
they can easily be grown in fermenters for large scale productions. Besides all
these, the separation of fungal biomass is easy by filtration; due to its
filamentous structure. They also have capability to under environmentally
stress conditions like low pH, poor nutrition, low water activity (Whang et al., 2009) and are less sensitive towards
variations in aeration and temperature. Raipur, the capital city of C.G state
is now considered to be the third worst city in India on the list of top twenty
polluted cities in the world, when it comes to air pollution. Central pollution
control board (CPCB) recently declared it as the country’s most polluted city.
Several factors are responsible to make it as the most polluted city among
which higher concentration of PAHs in the air may be one. The utilization of
bioremediation techniques through microorganisms, to clean up pollutants is viable
and has economic values (Mnif et al.,
2009). Microorganisms possess enzymatic systems for degradation and utilization
of oil as a source of carbon and energy (Ilori et al., 2008). Growth and proliferation of oil utilizing
microorganisms in oil contaminated soil is greatly influenced by the presence
of nutrients and their hydrocarbonoclastic property (Chakraborty and Mukherji,
2010).
1.1 AIM
OF STUDY
To
isolate and identify biodegrading fungi species from used engine oil
contaminated soil in rural areas
1.2 SPECIFIC
OBJECTIVES
1. To
isolate fungi species present in used engine oil contaminated soil.
2. To
identify and characterize fungal isolates using colonial morphology and
microscopic appearance.
3. To
determine the oil degrading ability of the fungi species.
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