ASSESSMENT OF HEAVY METALS IN WILD AND FARMED AFRICAN CATFISH CLARIAS GARIEPINUS (BURCHELL, 1822) IN SELECTED RIVERS AND FISH FARMS | Blazingprojects Postgraduate Thesis
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ASSESSMENT OF HEAVY METALS IN WILD AND FARMED AFRICAN CATFISH CLARIAS GARIEPINUS (BURCHELL, 1822) IN SELECTED RIVERS AND FISH FARMS

 

Table Of Contents


Chapter ONE

INTRODUCTION

  • 1.1Introduction
  • 1.2Background of Study
  • 1.3Problem Statement
  • 1.4Objective of Study
  • 1.5Limitation of Study
  • 1.6Scope of Study
  • 1.7Significance of Study
  • 1.8Structure of the Research
  • 1.9Definition of Terms

Chapter TWO

LITERATURE REVIEW

  • 2.1Overview of Heavy Metals
  • 2.2Sources of Heavy Metal Contamination
  • 2.3Effects of Heavy Metals on Aquatic Life
  • 2.4Heavy Metals Uptake and Accumulation in Fish
  • 2.5Monitoring and Regulation of Heavy Metals
  • 2.6Studies on Heavy Metals in Clarias gariepinus
  • 2.7Comparison of Wild vs. Farmed Fish Heavy Metal Levels
  • 2.8Methods for Heavy Metal Analysis
  • 2.9Techniques for Heavy Metal Removal
  • 2.10Current Research Gaps in Heavy Metal Assessment

Chapter THREE

RESEARCH METHODOLOGY

  • 3.1Research Design
  • 3.2Sampling Techniques
  • 3.3Data Collection Methods
  • 3.4Experimental Setup
  • 3.5Statistical Analysis
  • 3.6Quality Control Measures
  • 3.7Ethical Considerations
  • 3.8Research Limitations

Chapter FOUR

DATA PRESENTATION AND ANALYSIS

  • 4.1Analysis of Heavy Metal Concentrations
  • 4.2Comparison of Wild vs. Farmed Catfish
  • 4.3Seasonal Variations in Heavy Metal Levels
  • 4.4Correlation Analysis of Heavy Metals
  • 4.5Health Implications of Detected Heavy Metals
  • 4.6Discussion on Regulatory Standards
  • 4.7Mitigation Strategies for Heavy Metal Pollution
  • 4.8Future Research Directions

Chapter FIVE

SUMMARY, CONCLUSION AND RECOMMENDATIONS

  • 5.1Summary of Findings
  • 5.2Conclusions
  • 5.3Implications for Aquatic Health
  • 5.4Recommendations for Policy and Practice
  • 5.5Contribution to Scientific Knowledge

Thesis Abstract

ABSTRACT

The presence and bioaccumulation pattern of some heavy metal concentrations in wild and

farmed African catfish, Clarias gariepinus (Burchell, 1822) muscles collected from selected

rivers and fish farms in Kaduna State, Nigeria, were assessed. Fish and water samples used for

the assessment were collected during the wet and dry seasons from River Kaduna, River

Galma in Zaria; and from two fish farms in Sabon Tasha, Kaduna and Dakace, Zaria. Physico-

chemical parameters, such as Puissance Hydrogen (pH), temperature, Turbidity etc., were also

analysed. The analyses of heavy metals, Iron (Fe), Lead (Pb), Nickel (Ni), Cadmium (Cd) and

Mercury (Hg), in all water and Clarias gariepinus muscle samples was carried out in the

Multi-User Science Research Laboratory, Department of Chemistry, Ahmadu Bello

University, Zaria, using Thermo-element Solar S4 Atomic Absorption Spectrophotometer

(AAS), while the Varian Generation Accessory (VGA 77) with closed end cell was used for

Hg determination. The results obtained were subjected to t-test analysis to determine the level

of significance (p < 0.05) between the means, while Pearson correlation coefficient was

employed to determine the relationships. pH was highest in River Kaduna during the wet

season, in the upstream (7.04), while there was a dip in the downstream (6.67) during the dry

season. Seasonal variations in temperature were evident, as the ranges obtained in the rivers

were from 27.03°C – 30.68°C and the farms ranged from 23.76°C – 27.42°C, which were

within World Health Organization (WHO) recommended threshold (30°C – 36°C). Dissolved

Oxygen (DO) varied widely in the rivers (5.11mg/l – 7.04mg/l) as well as in the farms

(9.29mg/l – 10.74mg/l). Total dissolved solids (TDS)obtained in this study were all very high

(Rivers 54.91mg/l – 82.09mg/l, Farms 28.43mg/l – 42.03mg/l), but were all lower than the

WHO standardindicativeofportability (1000 – 1600mg/l). Heavy metal concentrations in

water samples and heavy metal bio-accumulation in both wild and farmed C. gariepinus

muscles showed irregular distributions with descending order ofFe >Pb>Hg>Ni > Cd. Fe

vii


levels were the highest in both rivers water samples (3.23mg/l), closely followed by Pb (0.78)

and Hg (0.69mg/l), while the farms also had Fe as the dominant element (1.31mg/l), with Pb

(0.26mg/l) and Hg (0.09mg/l), respectively. Both water bodies had Ni concentration (0.2mg/l)

higher than the WHO limits of 0.02mg/l, while the farms‟ concentration (0.03mg/l) was

slightly higher than WHO threshold limit. In the muscle of C. gariepinus, Fe concentrations

were also high in rivers (3.53mg/kg), while the Farms was 1.44mg/kg, all above the FAO

recommended limit (0.5mg/kg) in fish. Generally, only Cd didnot exceed the maximum

permissible limits in the tissues ofC. gariepinus. However, with Fe, Hg, Pb and Ni all higher

than the acceptable limits, most especially in the rivers, this could pose a serioushealth risk to

consumers. Thus, a close periodical and regular monitoring of heavy metal pollution in the

water bodies is strongly advocated.


Thesis Overview

<p> </p><div><p><strong>1.0</strong>&nbsp; &nbsp; &nbsp; &nbsp;<strong>INTRODUCTION</strong></p><p><strong>1.1</strong>&nbsp; &nbsp; &nbsp; &nbsp;<strong>Background</strong>&nbsp;<strong>of</strong>&nbsp;<strong>the</strong>&nbsp;<strong>Study</strong></p><p>In recent years the concentrations of toxic metals in many ecosystems are reaching</p><p>unprecedented levels. The increasing use of metals in industry and mining activities have led</p><p>to serious environmental pollution through effluents and emanations (Güven <em>et</em>&nbsp;<em>al.,</em>&nbsp;1999).</p><p>Under certain environmental conditions, heavy metals may accumulate and cause serious</p><p>ecological damage. The aquatic ecosystem is often seen as the ultimate recipient of almost</p><p>everything including heavy metals (Ogoyi <em>et</em>&nbsp;<em>al.,</em>&nbsp;2011). Pollution of heavy metals in aquatic</p><p>environment is a growing problem worldwide and currently it has reached an alarming rate.</p><p>There are various sources of heavy metals; some originates from anthropogenic activities like</p><p>draining of sewage, dumping of hospital wastes and recreational activities. Conversely,</p><p>metals also occur in small amounts naturally and may enter into aquatic system through</p><p>leaching of rocks, airborne dust, forest fires and vegetation (Fernandez and Olalla, 2000). As</p><p>heavy metals cannot be degraded, they are continuously being deposited and incorporated in</p><p>water, sediment and aquatic organisms (Linnik and Zubenko, 2000), thus causing heavy</p><p>metal pollution in water bodies.</p><p>Heavy metal is any metallic chemical element that has a relatively high density and is toxic or</p><p>poisonous at low concentrations (Ngumbu, 2014). Examples of heavy metal include mercury,</p><p>cadmium, arsenic chromium, thallium and lead. As trace elements, some heavy metals (e.g.</p><p>copper, iron, zinc, manganese and selenium) are essential to maintain the metabolism of the</p><p>human body. However, at higher concentrations they can lead to poisoning (Lenntech, 2014).</p><p>Heavy metals can enter the human food through water, air, soil, plants and animals. The</p><p>pollution of the environment by heavy metals is viewed as an international problem because</p><p>1</p></div><p><br></p><div><p>of its effects. In recent years, the pollution of aquatic environment with heavy metals has</p><p>become a worldwide problem because of their potential toxic effect and also most of them</p><p>accumulate in tissues and organs of aquatic organism (Goldstein and Hewitt,</p><p>1990andGledhill <em>et</em>&nbsp;<em>al.,</em>&nbsp;1997).</p></div> <br><p></p>

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