ABSTRACT
This study assessed heavy metal contamination in watermelon (Citrullus lanatus) produced in the irrigation area of Kiyawa Local Government Area (LGA), Jigawa State. The primary objective was to determine the concentrations of lead (Pb), cadmium (Cd), and chromium (Cr) in watermelon fruits, evaluating their compliance with international safety standards. Samples were collected from multiple farms, prepared through washing; peeling, homogenizing, and acid digestion, then analyzed using UV-Visible spectrophotometry. The findings showed detectable levels of Pb, Cd, and Cr in all samples, with Pb and Cd concentrations exceeding the World Health Organization (WHO) and Food and Agriculture Organization (FAO) permissible limits in several instances, indicating potential health risks. Chromium levels remained within acceptable limits. Variability among samples suggested localized contamination influenced by irrigation water quality, soil characteristics, and farming practices. The study highlights the significant risk posed by heavy metal accumulation in watermelon. There is need to strengthen and enforce regulations governing the use of agrochemicals to minimize heavy metal inputs into agricultural ecosystems, Establish routine heavy metal monitoring programs for food crops, utilizing accessible and cost-effective analytical methods such as UV-Vis spectrophotometry and Conduct larger-scale studies involving more watermelon farms and additional sampling periods to assess temporal and seasonal variations in heavy metal contamination.
TABLE OF
CONTENTS
Table of Contents
DECLARATION.. iii
DEDICATION.. iv
CERTIFICATION.. v
APPROVAL PAGE.. vi
ACKNOWLEDGEMENTS. vii
TABLE OF CONTENTS. viii
LIST OF TABLES. xii
CHAPTER ONE: INTRODUCTION.. 1
1.1 Background of the Study. 1
1.2 Statement of the research problem.. 3
1.3 Research Questions / Hypothesis. 4
1.4 Aim and Objectives. 4
1.4.1 Aim.. 4
1.4.2 Objectives. 4
1.5 Scope and Delimitation of the Study. 5
1.6 Significance of the Study. 5
1.7 Justification of the Study. 5
1.8 Limitations of the Study. 6
CHAPTER TWO: LITERATURE REVIEW... 7
2.1 Introduction. 7
2.2 Conceptual framework. 7
2.2.1 Definition of the heavy metal 7
2.2.2 Major heavy metals of toxicological importance. 8
2.2.2.1 Lead. 8
2.2.2.2 Cadmium (Cd) 10
2.2.2.3 Chromium (Cr) 12
2.2.2.4 Zinc (Zn) 14
2.2.2.5 Nickel (Ni) 16
2.2.2.6 Mercury (Hg) 18
2.2.2.7 Arsenic (As) 20
2.2.3 Bioaccumulation and Transfer of Heavy Metals
from Soil and Water to Plants. 22
2.2.4 Human Health Implications of Heavy Metal
Consumption via Food. 23
2.3 Theoretical Framework. 24
2.3.1 Environmental Toxicology Theories Related to
Heavy Metal Uptake. 24
2.3.2 Risk Assessment Models for Dietary Exposure to
Heavy Metals. 25
2.4 Review of Related Literature. 26
2.4.1 Soil and Water Contamination by Heavy Metals. 26
2.4.2 Heavy Metal Uptake in Watermelon and Other
Fruits. 28
2.4.3 Human Health Risks from Heavy Metals in
Watermelon. 30
2.5 Gaps in Knowledge. 31
CHAPTER THREE: MATERIALS AND METHODS. 32
3.1 Introduction. 32
3.2 Study Area. 32
3.2.1 Historical Background of the Study Area. 32
3.2.2 Location of the Study Area. 32
3.3.3 Extent of the Study Area. 33
3.4.4 Environmental Features of the Study Area. 33
3.4.4.1 Climate. 33
3.4.4.2 Geology. 33
3.4.4.3 Relief. 33
3.4.4.4 Drainage. 33
3.4.4.5 Soils. 33
3.4.4.6 Vegetation. 34
3.4.5 Socio-Economic Setting of the Study Area. 34
3.4.5.1 Ethnography. 34
3.4.5.2 Population. 34
3.4.5.3 Land Use. 34
3.4.5.4 Agriculture. 34
3.4.5.5 Commerce and Industry. 34
3.4.5.6 Tourism.. 34
3.3 Types of Data. 35
3.3.1 Objective 1. 35
3.3.2 Objective 2. 35
3.3.3 Objective 3. 35
3.4 Sources of Data. 35
3.4.1 Objective 1. 35
3.4.2 Objective 2. 35
3.4.3 Objective 3. 35
3.5 Methods. 36
3.5.1 Experimental Design. 36
3.5.2 Materials/Apparatus/Reagents. 36
3.5.3 Laboratory/Analysis Procedures. 36
3.5.3.1 Sample Collection. 36
3.5.3.2 Sample Preparation and Digestion. 37
3.5.3.3 Heavy Metal Determination. 37
3.6 Method of Data Presentation. 37
3.6.1 Objective 1: Heavy Metal Concentrations. 37
3.6.2 Objective 2: Comparison between Watermelon
Samples. 37
3.6.3 Objective 3: Comparison with WHO/FAO Standards. 38
CHAPTER FOUR: RESULT AND DISCUSSION.. 39
4.1 Introduction. 39
4.2 Heavy Metal Concentrations in Watermelon Samples. 39
4.3 Comparison of Heavy Metal Concentrations between
Watermelon Samples. 40
4.4 Comparison of Concentrations with WHO/FAO
Standards. 41
CHAPTER FIVE: SUMMARY, CONCLUSION AND RECOMMENDATIONS. 43
5.1 Introduction. 43
5.2 Summary. 43
5.3 Conclusion. 44
5.4 Recommendations. 45
5.4.1 For Policy Makers. 45
5.4.2 For Further Research. 45
REFERENCES. 46
Table 4.1: Heavy Metal
Concentrations in Watermelon Samples……………………...………..40
LIST OF FIGURES
Figure 3.1: Map of the Study area………………………………………………….……………32
Figure 4.1: Comparison of
Heavy Metal Concentrations between Watermelon Samples…..…..41
Figure 4.2:
Comparison of
Concentrations with WHO/FAO Standards……….………………..42
Heavy metals are a category of metallic elements that
possess relatively high densities, atomic weights, or atomic numbers and are
known for their potential toxicity even at trace levels. Prominent heavy metals
of environmental and agricultural concern include lead (Pb), cadmium (Cd),
chromium (Cr), copper (Cu), nickel (Ni), iron (Fe), manganese (Mn), and zinc
(Zn) (Habibullah et al., 2023; Boularbah et al., 2006). These elements are
naturally present in the earth’s crust but can become concentrated in soils,
water, and biota due to anthropogenic activities such as industrial discharge,
mining, waste disposal, and the extensive use of agrochemicals in agriculture
(Alloway, 2013; Shahid et al., 2018).
The uptake of heavy metals by food crops has raised
global food safety concerns because these metals can bioaccumulate in edible
plant parts, subsequently entering the human food chain and potentially causing
significant health risks (Tchounwou et al., 2012; Habibullah et al., 2023).
Heavy metals do not degrade and tend to persist in the environment, posing
chronic exposure hazards. Among these metals, Pb and Cd are particularly
notorious due to their high toxicity, ability to cause neurological, renal, and
carcinogenic effects, even at low concentrations (Jarup, 2003; Khan et al., 2017).
Chromium exists in multiple oxidation states, with hexavalent chromium (Cr VI)
being highly toxic and carcinogenic, unlike the trivalent form (Cr III), which
is an essential nutrient at trace levels (Jiang et al., 2019).
Watermelon (Citrullus
lanatus), a member of the Cucurbitaceae family, is one of the widely
cultivated fruits in Nigeria and other tropical regions, valued both
nutritionally and economically (Isaac, 2024). Its cultivation is often
concentrated in irrigation areas which utilize water sources that may be
subjected to contamination by heavy metals. Irrigation water quality
significantly influences the levels of heavy metals in soils and crops. For
instance, irrigation with wastewater or water contaminated by industrial
effluents and agricultural runoff can lead to accumulation of toxic metals in
both soil and edible crops, raising serious health implications for consumers
(Boularbah et al., 2006; Huh et al., 2008; Habibullah et al., 2023).
Studies elsewhere have demonstrated that heavy metal
contamination in watermelon varies substantially depending on the environmental
conditions and degree of contamination of irrigation resources. Huh et al.
(2008) reported measurable accumulation of Pb, Cd, and Cr in watermelons grown
in contaminated soils in South Korea. Similarly, Habibullah et al. (2023) found
varied heavy metal concentrations across watermelon samples irrigated with
different water qualities in districts of Balochistan, Pakistan.
The bioaccumulation of heavy metals in edible crops like
watermelon constitutes a critical public health issue especially in developing
countries such as Nigeria, where environmental regulation and monitoring
infrastructure may be limited (Adeyemi et al., 2018; Tchounwou et al., 2012).
Chronic ingestion of heavy metals through contaminated fruits can lead to
severe health complications including neurotoxicity, immunotoxicity, renal
dysfunction, and increased risks of cancers (Jarup, 2003; Mohan et al., 2020).
This is particularly concerning in regions where watermelons and other fruits
comprise an essential part of the local diet across various age groups.
International bodies such as the World Health
Organization (WHO) and the Food and Agriculture Organization (FAO) have
established maximum permissible limits for heavy metals in food crops to
safeguard consumer health (WHO, 2019; FAO/WHO, 2011). These guidelines provide
a benchmark for evaluating contamination levels and are an essential reference
for regulatory and monitoring programs. Assessing watermelon samples against
these standards enables identification of potential health risks and
formulation of appropriate risk management strategies.
Recent methodological advances such as the use of
UV-Visible spectrophotometry have facilitated the accurate and cost-effective
quantification of heavy metals in agricultural produce (Kumar & Singh,
2021; Isaac, 2024). This analytical approach, coupled with appropriate sample
preparation techniques including acid digestion, allows for reliable detection
of trace metal concentrations in complex matrices like fruits. Implementation
of these methods in research within the Kiyawa L.G.A context can yield accurate
site-specific data crucial for evidence-based interventions.
1.2 Statement of the research problem
Watermelon (Citrullus
lanatus), a major fruit crop widely consumed in Nigeria and other parts of
the world for its nutritional value, is particularly vulnerable to
contamination when grown in irrigation areas utilizing water and soils exposed
to pollutants (Isaac, 2024; Huh et al., 2008). Irrigation water of insufficient
quality, derived from sources contaminated with heavy metals, acts as a
critical vector for transferring these contaminants into soils and crops.
Consequently, the edible parts of watermelon may accumulate significant levels
of toxic metals, posing health risks upon human consumption (Habibullah et al.,
2023).
Despite the severity of heavy metal contamination and
its implications for food safety, existing monitoring efforts in many
agricultural communities-including Kiyawa Local Government Area (L.G.A) of
Jigawa State, Nigeria-are often fragmented and insufficient. Many studies tend
to focus primarily on evaluating contamination levels in soil or water
separately, without integrating the assessment of contaminant transfer from
these environmental matrices into the edible crop parts (Huh et al., 2008).
This piecemeal approach limits comprehensive understanding of the contamination
dynamics within the irrigation farming system and the resultant food safety risks.
Moreover, there exists a paucity of localized data
regarding heavy metal contamination specifically within the irrigation areas of
Kiyawa L.G.A, despite its importance as an agricultural hub. This study
recognizes the urgent need to address these challenges through assessment of
heavy metal concentrations in watermelon fruits. By doing so, it seeks to fill
the data gaps specific to Kiyawa L.G.A, providing essential evidence for
evaluating potential health risks and informing policy decisions.
1.3 Research Questions / Hypothesis
- What are the
concentrations of Pb, Cd, and Cr in watermelon fruits from Kiyawa
L.G.A?
- How do concentrations
vary between different watermelon samples in the area?
- Do these concentrations
comply with WHO/FAO safety standards?
To assess heavy metal concentrations in watermelon
fruits grown in Kiyawa L.G.A and evaluate potential health risks.
1.4.2 Objectives
- Determine heavy metal
(Pb, Cd, Cr) concentrations in watermelon fruit samples.
- Compare concentrations
among watermelon samples collected.
- Compare measured
concentrations with WHO/FAO permissible limits.
The study is restricted to watermelon (Citrullus lanatus) cultivated in
irrigation farms within Kiyawa LGA, Jigawa State. It focuses exclusively on
heavy metals (Pb, Cd, Cr) levels employing UV-Visible spectrophotometry for
quantification. Factors such as seasonal variations are not addressed within
this scope.
1.6 Significance of the Study
The study provides
essential, localized data crucial for food safety governance in Kiyawa LGA and
similar irrigation-based agricultural zones. By quantifying heavy metal
concentrations in a widely consumed fruit, the research informs regulators,
extension services, and farmers about potential health risks and compliance
with international standards. The findings can guide policy improvements, drive
the implementation of routine monitoring programs, support risk communication
with communities, and contribute to the broader literature on heavy metal
transfer in cucurbit crops in tropical settings.
1.7 Justification of the Study
Localized data are often
lacking for watermelon grown under irrigation in this region, yet such data are
vital for accurate risk assessment and decision-making. Pb, Cd, and Cr pose
known health risks, and their presence in edible fruit warrants attention from
public health and agricultural authorities. The study uses feasible,
cost-effective analytic approaches to generate site-specific evidence, enabling
targeted interventions, regulatory enforcement, and capacity-building for local
laboratories. The work also establishes a baseline for future longitudinal and
multidisciplinary research on heavy metal contamination and food safety in Kiyawa
LGA.
1.8 Limitations of the Study
The study focuses on a
subset of heavy metals (Pb, Cd, Cr) due to resource and methodological
constraints; results may not reflect the full metal burden. The use of
UV-Visible spectrophotometry, while accessible and cost-effective, may have
limitations in sensitivity and specificity compared with more advanced
instrumental techniques.
Single-season sampling
limits the ability to assess seasonal or annual trends. The geographic scope is
confined to selected irrigation farms in Kiyawa LGA; extrapolation to other
regions should be done with caution.
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