Assessment of eutrophication level of municipal surface water, abuja nigeria | Blazingprojects Postgraduate Thesis
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Assessment of eutrophication level of municipal surface water, abuja nigeria

 

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 Eutrophication
  • 2.2Causes of Eutrophication
  • 2.3Effects of Eutrophication on Water Bodies
  • 2.4Monitoring and Assessment of Eutrophication
  • 2.5Eutrophication Management Strategies
  • 2.6Case Studies on Eutrophication
  • 2.7Global Perspectives on Eutrophication
  • 2.8Sustainable Practices to Reduce Eutrophication
  • 2.9Technological Innovations in Eutrophication Control
  • 2.10Policy and Regulatory Frameworks on Eutrophication

Chapter THREE

RESEARCH METHODOLOGY

  • 3.1Research Design and Methodology
  • 3.2Sampling Techniques
  • 3.3Data Collection Methods
  • 3.4Data Analysis Procedures
  • 3.5Research Instrumentation
  • 3.6Ethical Considerations
  • 3.7Validity and Reliability
  • 3.8Limitations of Research Methodology

Chapter FOUR

DATA PRESENTATION AND ANALYSIS

  • 4.1Data Analysis and Interpretation
  • 4.2Eutrophication Levels in Municipal Surface Water
  • 4.3Comparison of Eutrophication Indicators
  • 4.4Correlation Analysis of Water Quality Parameters
  • 4.5Spatial Distribution of Eutrophication
  • 4.6Temporal Variation in Eutrophication Levels
  • 4.7Impact Assessment of Eutrophication
  • 4.8Discussion on Findings

Chapter FIVE

SUMMARY, CONCLUSION AND RECOMMENDATIONS

  • 5.1Summary of Findings
  • 5.2Conclusion
  • 5.3Implications for Policy and Practice
  • 5.4Recommendations for Future Research
  • 5.5Contribution to Knowledge

Thesis Abstract

Abstract
Eutrophication is a major environmental issue affecting surface water bodies worldwide. In the context of municipal water sources in Abuja, Nigeria, understanding and assessing the eutrophication levels is crucial for effective water resource management and conservation. This research project aimed to assess the eutrophication level of municipal surface water in Abuja, Nigeria, using a combination of field surveys, water quality analysis, and remote sensing techniques. The study focused on selected surface water bodies within the Abuja metropolis, including rivers, streams, and reservoirs that serve as sources of municipal water supply. Field surveys were conducted to collect water samples and measure various physical and chemical parameters such as dissolved oxygen, nutrient concentrations, chlorophyll-a levels, and turbidity. These parameters were analyzed to determine the trophic status of the water bodies and assess the degree of eutrophication. In addition to field data collection, remote sensing techniques were employed to monitor the spatial and temporal variations in water quality parameters across the study area. Satellite imagery was used to map the distribution of chlorophyll-a concentrations and identify potential eutrophication hotspots in the surface water bodies. The integration of field data with remote sensing results provided a comprehensive assessment of the eutrophication levels in the municipal water sources of Abuja. The findings of this study revealed varying degrees of eutrophication in the surface water bodies of Abuja, with some areas showing elevated nutrient levels and chlorophyll-a concentrations indicative of nutrient enrichment. These results highlight the importance of implementing sustainable water management practices to mitigate the impacts of eutrophication and ensure the availability of clean and safe water for municipal use. Overall, this research contributes to the understanding of eutrophication dynamics in municipal surface water sources in Abuja, Nigeria, and provides valuable information for policymakers, water resource managers, and other stakeholders involved in water quality monitoring and conservation efforts. The findings underscore the need for continued monitoring and management strategies to address eutrophication and maintain the ecological integrity of surface water bodies in the region.

Thesis Overview

<p> </p><p>1.0 INTRODUCTION</p><p>Eutrophication is the natural process whereby a confined water body (e.g. lake or dam) ages with time due to accumulation of silt or organic matter in the lake (Ademoroti, 1996).</p><p>A young lake is characterized by low nutrient level and consequently low plant productivity and at this stage is described as oligotrophic (few food) lake. The water body gradually acquires inorganic and organic nutrient from catchment areas and these promote aquatic growth and increased biological productivity causing the lake to become murky with decaying organic matter and phytoplankton. The water body is said to be eutrophic (well fed) and consequently, the decaying organic matter depletes its available oxygen. Increase in the accumulation of silt and organic matter, makes the water body shallower and sunlight penetrate slowly to the bottom, making the water warmer. Plants take roots along the shallow edges and the lake slowly transforms into a marsh or swamp which may eventually lead to dry land (Ademoroti, 1996).</p><p>Anthropogenic impact and seasonal climatic changes have aggravated eutrophication in water bodies worldwide. Advancement in science and technological innovation in agricultural practices has resulted in increased usage of natural and synthetic manures rich in phosphorus, potassium, and calcium in farming. These have accelerated the natural process of eutrophication worldwide. Nations of the world are conscious of the famous Malthusian economic theory and hence fight against this detrimental prediction by increasing food production through the construction of dams for irrigation and energy. Nations in arid regions are also making efforts to conserve their existing water resources to<br>meet the increasing food demand through water storage reservoirs to conserve and harness this precious resource more efficiently. Such reservoirs and lakes are subject to several kinds of degradation and losses through evaporation, inefficient storage and consumption waste in addition to the growth of all kinds of aquatic organisms such as plankton, insects, fish and angiosperms. These changes lead to the phenomenon of eutrophication (Rashid and Anjum, 1985).</p><p>Eutrophication therefore causes progressive deterioration of water quality especially lakes due to luxuriant growth of plants with the effect that the overall metabolism of the water is affected (Richard, 1970).</p><p>A research carried out by Rashid and Anjum (1985) showed that the presence of</p><p>Euglena, oscillatoria and Anabaena Spp indicate high organic pollution responsible for eutrophication and this affects the species of microinvertebrates and macrovertebrates including the species of fish in the water. It was found that the predatory specie Notopterus hotopterus was gradually increasing causing threat to the survival of some useful fish in the water body. Eutrophication is therefore detrimental to crop production, fish farming and provision of portable drinking water.</p><p>Eutrophic water bodies receive large amount of aquatic plant nutrients relative to their surface area and volume and have high production of aquatic plants (Fred and Ann, 1978). Oligotrophic water bodies tend to be poorly fertilized and have low aquatic plant production, mesotrophic water bodies receive moderate amount of aquatic plants nutrients.</p><p>Thermocline is a term used in describing the depth in a water body in which there is rapid change in temperature with depth as a result of the division of the water body into</p><p>2</p><p>layers with different densities (Fred and Ann 1978). These are the epilimnion the warmer and less dense surface waters and also the hypolimnion which describes the cooler, more dense bottom waters. The thermocline provides a barrier of mixing water between these two layers and is normally present between early June to October in temperate water bodies (Fred and Ann 1978). During this thermal stratification, waters of the hypolimnion are isolated from the atmosphere by the thermocline and cannot replenish their oxygen. Algae which have grown in this area died and decomposed leading to reduction of oxygen at the bottom. In many eutrophic waters, this depletion is sufficient to cause anoxic conditions (Zero dissolved oxygen) in the hypolimnion (Fred and Ann 1978; Muir, 2001).</p><p>It was discovered that the river Jordan which is currently the largest and longest river that flows into Israel was under threat of extinction following eutrophication. Adequate measures were taken to keep it alive for utility and consumption since major rivers in Israel were contaminated by agriculture and industrial wastes which made the Jordan River the only natural and clean river in the country (Shoshana, 2012). Biodiversity of algal communities in the upper Jordan River formed as a result of natural climatic and anthropogenic impact was used to predict the disastrous outcome.</p><p>1.1 CAUSES OF EUTROPHICATION</p><p>1.1.1 Natural Sources</p><p>Eutrophication can also be described as the process of fertilization of natural waters (Fred and Ann, 1978). There is no place in Abuja where Eutrophication has been described as an algal bloom. Nevertheless, there is the need to put drastic environmental measures to prevent its occurrence in the near future. Any process which favours the growth of aquatic</p><p>3</p><p>plants or plant life can lead to eutrophication. Nutrients required for plant growth include sulphur, calcium, magnesium ,sodium ,iron, zinc, copper etc. The major nutrients required by plants are nitrogen, phosphorus and potassium. Nitrate-nitrogen is most often obtained from urea. When urea is excreted by animals it hydrolyses rapidly to ammonia which is then acted upon by the bacteria Nitrosomonas and is oxidized to nitrite. Another bacterium called Nitrobacter oxidizes the nitrite to nitrate which is available as plant nutrient (Ademoroti, 1996). The triple bond of Nitrogen, N?N present as N2 in the atmosphere can be broken by thunderstorm to make it soluble in water during rain and all these form a natural process for nitrogen fixation into the soil which can be washed along with sand and silt to cause eutrophication in water body (Ababio 1990).</p><p>In stabilization ponds, nitrate acts as an algal nutrient thereby reinforcing the symbiotic relationship between algal and bacteria and this is the basis of wastewater purification in facultative ponds (Ademoroti, 1996).</p><p>Hydrolysis of urea</p><p>NH2CONH2 + H2O ? 2NH3 + CO2</p><p>Oxidation of ammonia by Nitrosomonas.</p><p>55NH3 + 76O2 + 5CO2 ? C5H7NO2 + 54NO-2 + 52H2O + 54H+ (bacteria cells)</p><p>Oxidation of nitrite by Nitrobacter.</p><p>400NO-2 + 195O2 + 5CO2 + NH3 + 2H2O ? C5H7NO2 + 400NO-3 (bacteria cells)</p><p>4</p><p>Other natural sources leading to eutrophication include rock weathering and erosion. Erosion can transport clay, silt and plant nutrients such as calcium and phosphorus in suspension into water bodies for eutrophication (Lathrop et al 1998). The nutrients available in an environment therefore also depend on the topography (Likens, 1972).</p><p>1.1.2 Anthropogenic Sources</p><p>Domestic Activities</p><p>Human activities in urban and rural areas have led to an increase in plant nutrients such as nitrogen, phosphorus, and potassium through improper disposal of sewage rich in urea from faeces and urine, food waste and other municipal waste products. The use of detergents with branch chain hydrocarbon cannot be degraded by bacteria and hence lead to the death of aquatic animals and subsequent enrichment of water body with nitrogen. The use of detergents with optical brighteners for aesthetic beauty of clothes has led to the enrichment of water bodies with nitrogen because these optical brighteners and perfumes often contain chromophore structure ?N=N- to enhance red shift and desirable colour characteristics (Ababio, 1990).</p><p>Agricultural Practices</p><p>Human agricultural practices such as the use of organic and inorganic fertilizers have led to increase in plant nutrients and consequently the phenomenon of eutrophication. Agricultural run-off from irrigated farms and leaching of fertilizer to water bodies have enormously increased these nutrients to favour the growth of algae (Lathrop, 1998). Nutrients from agricultural systems can pollute natural waters through drainage water, soil</p><p>5</p><p>erosion and animal waste and soil water, making these nutrients mobile and enhancing eutrophication (Eckert 1995; Gimba, 2011).</p><p>Industries</p><p>Developing nations of the world are embracing industrialization to improve their economies and standard of living and this trend has led to the production and discharge of various contaminants to the aquatic environment. Fertilizer industries, detergent industries, food industries among others discharge a lot of waste which can find their ways into lakes, streams or rivers or even directly to the municipal sewer system (Weibel, 1970).</p><p>1.2 STATEMENT OF PROBLEM</p><p>The increasing population density in the Federal Capital Territory (FCT) Abuja, have resulted in increasing discharge of domestic and industrial waste into water bodies. This could trigger eutrophication and hence the need for continuous monitoring for strategic planning in the FCT.</p><p>1.4 AIMS AND OBJECTIVES</p><p>The aim of this research work is assess eutrophication parameters in surface water bodies in Abuja.</p><p>The objectives include among others to;</p><p>I. Establish the physicochemical parameters of the surface water of the selected sites.</p><p>II. Determine the nutritional level of the surface water using standard methods.</p><p>III. Investigate the level of algal bloom in the selected sites.</p><p>IV. Correlate the algal bloom with nutritional level of the water bodies.</p><p>6</p> <br><p></p>

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