ASSESSMENT OF EUTROPHICATION LEVEL OF MUNICIPAL SURFACE WATER, ABUJA NIGERIA
Table Of Contents
<p> <b>TABLE OF CONTENTS </b></p><p>Title page-------------------------------------------------------------------------------------i </p><p>Declaration-----------------------------------------------------------------------------------ii</p><p>Certification--------------------------------------------------------------------------------- iii</p><p> Acknowledgement------------------------------------------------------------------------iv </p><p>Dedication-----------------------------------------------------------------------------------v</p><p> Abstract--------------------------------------------------------------------------------------vi</p><p> Table of Contents-------------------------------------------------------------------------vii</p><p> List of Figures------------------------------------------------------------------------------xi</p><p> Abbreviations, Definitions and Symbols-------------------------------------------xiii </p><p>
Chapter ONE
----------------------------------------------------------------------------1 </p><p>1.0 INTRODUCTION---------------------------------------------------------------------1 </p><p>1.1 Causes of Eutrophication-----------------------------------------------------------3 </p><p>1.1.1 Natural sources---------------------------------------------------------------------3 </p><p>1.1.2 Anthropogenic sources-----------------------------------------------------------5 </p><p>1.2 Statement of Problem---------------------------------------------------------------6 </p><p>1.3 Aims And Objectives-----------------------------------------------------------------6 </p><p>
Chapter TWO
---------------------------------------------------------------------------7 </p><p>2.0 LITERATURE REVIEW-------------------------------------------------------------7 </p><p>2.1 Factors Controlling Eutrophication-----------------------------------------------7 </p><p>2.1.1 Algal bloom-------------------------------------------------------------------------8 </p><p>2.1.2 Organic manure application----------------------------------------------------10 </p><p>2.1.3 Water hyacinth invasion--------------------------------------------------------12 </p><p>2.1.4 Impact of erosion----------------------------------------------------------------12 </p><p>2.2 Approaches to Controlling Eutrophication and Water Loss--------------13</p><p> 2.2.1 Nutrient control-------------------------------------------------------------------14 </p><p>2.3 Urbanization and Eutrophication Profile--------------------------------------18 </p><p>
Chapter THREE
---------------------------------------------------------------------23 </p><p>3.0 MATERIALS AND METHODS---------------------------------------------------23 </p><p>3.1 Sampling Sites-----------------------------------------------------------------------23 </p><p>3.2 Sample Collection and Preservation-------------------------------------------23 </p><p>3.3 Measurement of Physical Parameters-----------------------------------------26 </p><p>3.3.1 Temperature----------------------------------------------------------------------26 </p><p>3.3.2 Measurement of total dissolved solid----------------------------------------26 </p><p>3.3.3 Measurement of conductivity--------------------------------------------------26 </p><p>3.3.4 Measurement of chemical oxygen demand (Titrimetric method)----27 </p><p>3.3.5 Measurement of pH-------------------------------------------------------------28 </p><p>3.3.6 Measurement of biological oxygen demand (Titrimetric method)-----28</p><p> 3.3.7 Measurement of potassium---------------------------------------------------29 </p><p>3.3.8 Determination of nitrate (Colorimetric method)---------------------------30 </p><p>3.3.9 Determination of phosphate--------------------------------------------------30 </p><p>3.4 Principles of Operation of Colorimeter DR/890---------------------------31 </p><p>
Chapter FOUR
----------------------------------------------------------------------33 </p><p>4.0 RESULTS----------------------------------------------------------------------------33 </p><p>
Chapter FIVE
--------------------------------------------------------------------------53 </p><p>5.0 DISCUSSION-----------------------------------------------------------------------53 </p><p>5.1 BOD Concentrations-------------------------------------------------------------53 </p><p>5.2 Nitrates-------------------------------------------------------------------------------54 </p><p>5.3 Total Dissolved Solid-------------------------------------------------------------55 </p><p>5.4 Chemical Oxygen Demand----------------------------------------------------56</p><p>5.5 Conductivity-------------------------------------------------------------------------57 </p><p>5.6 Temperature------------------------------------------------------------------------58 </p><p>5.7 Algae Count------------------------------------------------------------------------59 </p><p>5.8 pH Level-----------------------------------------------------------------------------61 </p><p>5.9 Phosphate----------------------------------------------------------------------------62 </p><p>5.10 Potassium--------------------------------------------------------------------------62 </p><p>CHAPTER SIX--------------------------------------------------------------------------64 </p><p>6.0 SUMMARY AND CONCLUSION---------------------------------------------64 </p><p>6.1 Recommendations---------------------------------------------------------------65 </p><p>REFERENCES--------------------------------------------------------------------------67 </p><p>APPENDICES---------------------------------------------------------------------------72 </p>
Thesis Abstract
<p> <b>ABSTRACT </b></p><p>The level of some nutrient elements in Abuja surface water were investigated for six
months to determine the eutrophication profile and make logical inference on the fate of
surface water system in the nearest future. Samplings were done monthly for a period of six
months covering October to March and standard methods were used for the measurement
of some nutrients constituting the indices of eutrophication. The results showed high levels
of microbial activities. Biochemical oxygen demand (BOD) showed high levels of
pollution which varied with time and velocity of water current. Other parameters
investigated were chemical oxygen demand (COD), nitrate concentration, total dissolved
solid (TDS), conductivity, algae count, temperature, pH, phosphate and potassium
concentrations. Maximum and minimum values of some eutrophication parameters in the
sites were recorded as follows BOD ( Orozo 38mg/L- 7.37mg/L, Gidan Mangoro
31.2mg/L- 5.08mg/L, Nyanya 32.4mg/L- 10.05mg/L, Wuse 40.30mg/L- 7.007mg/L, Jabi
26.50mg/L- 3.10mg/L). Similarly total dissolved solid maximum and minimum values in
the sites were given as Orozo 1222mg/L- 105.1mg/L, Gidan Mangoro 861.0mg/L148.8mg/L, Nyanya 676.0mg/L- 127.6mg/L, Wuse 200.0mg/L- 86.2mg/L, Jabi 846.0mg/L151.8mg/L. These results point to eutrophication indicators in Abuja surface water system.
The results showed that the concentrations of nitrogen, phosphorus and potassium may be
significantly increased beyond their compensation level by the growing human population
in Abuja metropolis.
<br></p>
Thesis Overview
<p>
<b>1.0 INTRODUCTION </b></p><p><b>1.1 BACKGROUND STUDY </b></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).
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).
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
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).
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
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.
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.
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
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).
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.
<br></p><p>
<b>1.1 CAUSES OF EUTROPHICATION </b></p><p><b>1.1.1 Natural Sources </b></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
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).
<br></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).
Hydrolysis of urea </p><p>NH2CONH2 + H2O → 2NH3 + CO2
Oxidation of ammonia by Nitrosomonas.
55NH3 + 76O2 + 5CO2 → C5H7NO2 + 54NO2 + 52H2O + 54H+
(bacteria cells)
Oxidation of nitrite by Nitrobacter.
400NO2 + 195O2 + 5CO2 + NH3 + 2H2O → C5H7NO2 + 400NO3
(bacteria cells)
<br></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><b><i>1.1.2 Anthropogenic Sources </i></b></p><p>Domestic Activities
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).
Agricultural Practices
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
erosion and animal waste and soil water, making these nutrients mobile and enhancing
eutrophication (Eckert 1995; Gimba, 2011).</p><p><b><i> Industries
Developing </i></b></p><p>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><b>1.2 STATEMENT OF PROBLEM </b></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><br></p><p><br></p><p><br></p><p><br></p><p><br></p><p><br></p><p><br></p><p><br></p><p><br></p><p><br></p><p><br></p><p><br></p><p>The aim of this research work is assess eutrophication parameters in surface water bodies in
Abuja.
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. 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.
7
CHAPTER TWO
2.0 LITERATURE REVIEW
Eutrophication is a natural process that may take many years. These years can be
shortened by anthropogenic activities leading to a rapid eutrophication process with
detrimental effects on the man and animals.
2.1 FACTORS CONTROLLING EUTROPHICATION
Availability of sunlight and nutrient are factors controlling eutrophication. Sunlight
and nutrient stimulate photosynthetic reactions, algal bloom and vegetative productivity.
The amount of sunlight available in a water body is proportional to the transparency of the
water which in turn is a function of the level of eutrophication (Ademoroti, 1996). An
eutrophic lake may become so murky that photosynthesis can only take place at the surface
and the top layer (eutrophic zone) where plants grow and produce more oxygen by
photosynthesis than they can remove by respiration. The lower zone is called the profundal
zone. The transition between these two zones is termed the light compensation level
(Ademoroti 1996).
Algal can undergo photosynthesis, multiply and cause odourous clumps of rotten
debris when they decay. This clumps of rotten debris is biodegradable by bacteria to cause
oxygen depletion which is detrimental to the survival of fishes especially those who live in
colder regions at the bottom. Under this anaerobic condition hydrogen sulphide is formed
and metals such as iron and manganese tied up as sediments dissolve and are released into
the lake (Ademoroti, 1996). </p>