Abstract
These findings documented the physical, chemical and heavy metal contents in leachate, borehole water, surface stream, treated water and soil samples around the municipal solid waste dumpsite at Uyo metropolis, Akwa-lbom State, Nigeria. Samples were collected during the wet and dry seasons 2010/2011. The sam pies were analysed for the following parameters: heavy metals (Fe, Cu, Mn, Zn, Cr, Cd, Pb), anions (PO,SO~CI, NO,, NH’,-N), essential metals (Na, K, Ca, Mg), total dissolved solids (TDS), dissolve oxygen (DO), Chemical oxygen demand (COD), pH, salinity, turbidity and conductivity. The results revealed that most of the parameters recorded for the leachate samples significantly exceeded the WHO international standards for drinking water in both seasons. Fe (47.33 and 113.13mg(L), Cd (2.29 and 14.47mg/l), Cu (5.78 and 35.87mg/l), Cr (1.63 and 7.63mg/l), Pb (12.33 and 31.13mg/l), Zn (17.33, and 34.5mg/l), BOD (52.2 and 159.6mg/l), CI (284.37 and
536mg/l), NO, (74.03 and 87.83mg/l), TDS (1709.5 and 2043mg/l) and
DO (1.73  and  2.73mg/l).   In  leachate,  all  the heavy  metals,  CI,  COD, salinity,   and   conductivity   contents   showed   significant   increase (P<0.05)  while  SO,  recorded significant decrease (P<0.05)  during  the dry season.  The physico-chemical  contents  recorded for the  borehole water  and  treated  water  samples  in  both  seasons  agree  with  the international  standards for drinking water, except for high PO,° content (1.13  to  2.17mg/l)  recorded  for  the  borehole  water  samples  in  both seasons  which  exceeded  the  WHO  permissible  limit  of  0.1 mg/I  for drinking  water.  The  borehole  water  sample   recorded  significant increase  (P<0.05)  in Fe, Mn, Na, K. and a significant decrease in SO, contents during the dry season.  The  stream  water sample  recorded high  Fe (0.61  and  2.5mg/l)  content  in both  seasons  and  high  Mn (2.37 mg/I),  Cr (0.42mg/l),  Cd (0.46mg/l)  and  Cu (3.95mg/l)  contents  during the  dry season  which  exceeded  the  WHO  international  standard  for drinking  water.     The  stream  water  samples   recorded  significant increase  in BOD,,  Cu, Mn, Cd and  Cr contents  during  the  dry season (P<0.05). The heavy metal  contents  recorded for soil samples  from the dumpsite, from 10 and 20m east, west,  south and north of the dumpsite and  from  the  control  site  were  all  within  the  WHO  international standards  in both  seasons.  The  heavy  metal  contents  in the  dumpsite soil  sample  in  both  seasons  were significantly  higher;  pb  (9.90  and 11.82mg/kg),  Zn  (1370  and  146mg/kg),  Ni (12.56  and  11.82mg/kg),  Cr (3.60  and  4.05mg/kg)  Cd  (9.05  and  12.2mg/kg)  and  Mn  (94.0  and 91.2mg/kg)  In  both  seasons  than  the  control;  Pb  (3. 78mg/kg)  Zn (50.90mg/kg), Ni (2.19mg/kg), Cr (1.06mg/kg), Mn (44.27mg/kg), and Cd (1.09mg/kg).  Heavy metal  contents for soil samples  10 and 20m east of the dumpsite were also  significantly  higher (P<0.05) than  that of the control. This study infer that the solid  waste dumpsite is affecting the natural  quality of the ambient environment.  Therefore  indiscriminate dumping  of solid waste at the dumpsite
CHAPTER ONE
INTRODUCTION
1.1 Background of the study
The municipal solid waste dumpsite (MSWD) examined is located within the barrack’s road street at Uyo Metropolis; Akwa • lbom State. The dumpsite examined contains both biodegradable
and non biodegradable materials of all sorts. The different waste materials may contain different physical, chemical and biochemical properties. In the presence of atmospheric water, high temperature and high microbial populations, these waste materials may decompose and get dissolved in the presence of water to generate a waste liquid substance called leachate. This waste water produced may infiltrate into the ground water aquifer, it may be washed into a near by surface stream and it may affect the soil properties. When humans come into direct contact with such contaminated samples, it may lead to many health problems.
Pollution occurs when a product added to our natural environment adversely affects nature’s ability to dispose it off. A pollutant is something which adversely interferes with health, comfort, property or environment of the people. Generally, most pollutants are introduced in the environment as seawage, waste, accidental discharge and as compounds used to protect plants and animals. There are many types of pollution such as air pollution, water pollution, soil pollution, nuclear pollution and oil pollution (Misra and Mani, 1991 ).
Solid wastes other than hazardous and radioactive materials are often referred to as Municipal Solid Waste (MSW). Municipal solid waste is useless unwanted material discharged as a result of human activity. Most commonly, they are solids, semi• solids or liquids in containers thrown out of houses, commercial
or industrial premises (Nyangababo and Hamya, 1980). Municipal solid waste varies in composition, which may be influenced by many factors, such as culture affluence, location etc. Municipal solid waste management depends on the characteristics of the solid wastes including the gross composition, moisture contents, average particle size, chemical composition and density, in which knowledge of these usually helps in disposal plans (Sally, 2000).
In Nigeria, agencies like the Federal Environmental Protection Agencies (FEPA), Ministry of environment, Environmental Sanitation Authorities, for example Akwa lbom State Environmental Protection Agency (AKSEPA) and even local authorities are responsible for planning a defined line of action for the disposal of waste generated on daily basis in our society.
The report that refuse dumps have caused traffic delays in some strategic parts of our urban centers and cities is an example of poor management of refuse dumps in Nigerian towns and cities (Umaakuta and Mba, 1999). According to Eddy, Odoemelem and Mbaba (2006), the series of problems are as a result of lack of designed strategies that can be based on scientific principles and approach.
However, human endeavours, such as technology, industrialization, construction, trade, commerce, as well as nutrition have rendered the whole environment system a “throw away society”. This is true because indiscriminate disposal of waste coupled with increasing world population and urbanization
have  combined to worsen  the  situation  day  in,  day  out  (Eddy  et al., 2006).
According to Holmes (1992), site selection for waste disposal is generally based on geographic rather than geological and hydro geological considerations, that is the closer the site to the source of the waste the better in terms of transport cost
reduction. It is not uncommon therefore to find waste disposal sites within municipal boundaries and surrounded by residential areas. Clearly such sites pose-serious health risk just in terms of problems associated with litter, stray dogs, scavenging birds, rats and air borne contaminants from mobilization of fine particulate matter.
Despite the best attempts at waste avoidance reduction,
reuse and recovery (recycling, compositing and energy recovery), landfills and waste disposal sites are still the principal focus for ultimate disposal of residual wastes and incineration residues world-wide (Waite, 1995). The placement and compaction of municipal wastes in land fills facilitates the development of facultative and an aerobic conditions that promotes biological decomposition of land filled wastes. Hence, leachates of diverse composition are produced, depending on site construction and operational practices, age of the landfill, landfill method, climatic and hydro geological conditions and surface water ingress in to the landfill (Campbell, 1993).
A landfill is an engineered waste disposal site facility with specific  pollution  control  technology  designed   to  minimize potential  impacts.    Landfills  are  usually  either  placed  above ground or contained within quarries pits.  Landfills are sources of groundwater and soil pollution due to the production of leachates and  its  migration through  refuse  (Christensen  and  Stengmann, 1992).
According to Amina, et al., (2004), leachate corresponds to atmospheric water that has percolated through waste, interacting with bacteriological activity and especially organic substances. Its composition is a function of the nature and age of the land fill, type of waste, the method of burying, the geological nature of the site and climate.
Leachate pollution is a result of mass transfer process. Waste entering the landfill reactor undergoes biological, chemical and physical transformations, which are controlled among other influencing factors, by water input fluxes. In the reactor, three physical phases are present; the solid phase (waste), the liquid phase (leachate) and the gaseous phase. In the gaseous phase, mainly carbon (prevalently in the form of CO, and CH,) is present. The main environmental aspects of landfills leachate are the impacts on surface water quality, ground water quality as well as soil quality, if leachate is discharging into these bodies (Christensen et al., 1992).
According to Paster, et al., (1993); De-vare and Bahadir, (1994), uncontrolled leachates may exert deleterious effects on the environment, especially the input of high concentrations of organic leachate and inorganic solutions of metals at low oxidation states into water course which apparently depletes the dissolved oxygen content of the water and ultimately lead to extinction of all oxygen depending life. Also the non• biodegradable organic compounds in the leachate will persist for a long time. These compounds may adversely affect aquatic species when they are assimilated into food chains.
Ground water is that portion of subsurface water which occupies that part of the ground that is fully saturated and flows into a hole under pressure greater than atmospheric pressure. Groundwater occurs in geological formations called aquifer. An aquifer (gravel/sand) may be defined as a geological formation that contains sufficient permeable materials that yield significant quantities of water to wells and springs; this implies an ability to store and transmit water (Chae, 2000).
Groundwater is an important source of drinking water for human kind. It contains over 90% of the fresh water resources
and is an important reserve of good quality water. Groundwater, like any other water resource, is not just of public health and economic value it also has an important ecological function (Armon and Kitty, 1994). Groundwater contamination by landfill leachate is increasingly recognized as a serious problem (Hussan, et al., 1989; Loizidous and kapetanois, 1993; kwanchanawong and Kootlakers, 1993; AI-Muzains and Muslamani, 1994).
Soil is the collection of natural materials occupying part of the earth surface that may support plant growth, and which reflects the pedogenetic processes acting over time under the associated influences of climate, relief, living organisms, and parent materials. Soil pollution is caused by the removal or addition of substances and factors that decreases its productivity, quality of plants and ground water. Landscape pollution is simply the conversion of fertile land to barren one by dumping wastes over it.
Indiscriminate dumping of refuse can influence soil physico• chemical properties, but can still be used for farming provided the risks associated with its usage are continuously assessed and controlled. The introduction of metal contaminants into the environment could result from various sources; a few of which are application of sea wage materials, and leaching of garbage. The impact on man would be felt if the metals enter into the food chain and accumulate in living organisms (Moore and Ramamoorthy, 1984; Altundogan, et al., 1998).
Continuous  disposal  of  municipal  wastes  in  soil  may increased heavy  metal concentrations.  Heavy metals  may have harmful effects on soils, crops, and human health.  However, there is generally not strong relationship between the concentration of heavy  metals  in  soils  and  plants  because  it  depends  on  many factors  such  as soil  metal  bioavailability,  plant growth,  and metal distribution to plants parts.
Apart from the contamination of soil, water and agricultural land by other elements, lead alone has a poisoning effect. According to Akaeze (2001 ), the toxicity of lead could lead to encephalopathy, renal effect, and hematological effect. The WHO, had confirmed the effects of lead intake to include, abortion, infant mortality, malformation of foetus, genetic mutation, retarded growth, intoxication, depression of respiration and chromosomal aberrations. Smith, (1976), stated that heavy metals can be introduced into the environment through high tension electricity supply lines, municipal solid wastes and building materials. Sommers, et al., (1976), explains that copper is an essential constituent of all organisms, but if the copper concentration is increased above normal level, it becomes highly toxic. An increase in concentration of copper in the ocean by one part per billion has resulted in the death of several species of phytoplankton and the eggs of some fishes of open oceans. Based on these, researchers have opted to suggest ways of controlling the generation of wastes and effects on the environment.
Akpan (2001) observed that the major cause of land degradation in Uyo is solid waste, and on the characteristics of wastes, papers, food remains, metal scraps, tins, cans, rubber containers, plastics, cellophane bags, worn-out tyres, and tubes were identified as the major components of solid waste. Apart from the fact that solid waste degrade the environment, and pose problems to the aesthetic value of the environment, Etekpo (1999) has confirmed that health hazards associated with improper disposal of solid waste include;
harbouring and favouring rodents breeding and other harmful reptiles
empty can which favour mosquito breeding
putrescible wastes emit offensive odour thus polluting the air.
1.2 Statement of the problem
Humans and other living organisms depend  on a healthy environment  for  good  health.  The  Barrack’s  road  dumpsite examined  is situated very close  to residential areas. These areas use  borehole water, and  a nearby stream  located closed  to the dumpsite  for  drinking and  for  other  domestic  activities.  Soil around  the  dumpsite  is  used  for  farming  activities.  Rapid population  growth  and  industrialization,  coupled  with indiscriminate dumping  of solid wastes at the site, with little or no sound  solid  waste  management plants  at the  study  area  have contributed  to  increase  the  volume  of  solid  wastes  at  the dumpsite in an alarming rate. The different wastes types at the dumpsite,  possess  different physical,  chemical and  biochemical properties.  The  waste  water  produced  from  the  decomposed wastes materials each  times  it rains,  may drain  into the nearby surface stream,  may leach  into the sub-surface soil and then  into the groundwater aquifers. During this process, the boreholes, stream water and soil samples around the dumpsite may become contaminated.  This  may  be  very  possible   in  the  study  area because  the soil texture show  that soil  around the dumpsite and even  outside the  dumpsite  show  very  high  percentage  coarse sand  which  is  highly  conducive  to  leachate  transport.   When humans and other animals  come into direct contact with the contaminated samples they may face serious health challenges. With the desire to know the present quality of the borehole water, surface stream and soil around the dumpsite, the researcher deemed  it necessary  to  determine  the  physio-chemical characteristics  of leachate  from  the  dumpsite,  the  borehole water, surface stream  and  soil  sample  around the solid  wastes dumpsite  which  are  known  to  impact  on  human  health.  The results of this findings  may  reveal the  present qualities  of the boreholes, surface stream and soil around  the dumpsite.
1.3 Objective of study
1.3.1 General objective
To characterize leachate, groundwater, stream water and soil in the vicinity of a municipal dumpsite at Uyo metropolis to determined the level of impact of the dumpsite on the ambient environment.
1.3.2 Specific objective
1) To assess and compare the physic-chemical properties of leachate, borehole, surface stream and treated water samples around the barrack’s road dumpsite with the international standard for drinking water.
2) To assess and compare the heavy metal contents of soil samples from the dumpsite, samples from the control site (800m) and samples from 10 and 20m outside the dumpsite in the north, south, west and east transects with the internal standards.
3)     To compare the physic-chemical contents and heavy metals recorded  for  leachate,  borehole  water,  surface  stream treated  water  and  soil  samples  during  the  wet and  dry seasons.
1.4 Expected benefits of the study
This study is necessary because it is hoped that through its outcome, the magnitude of the environmental contamination in the study area will be highlighted.
To the author, this work is so important since it serves as a medium through which he can address the numerous problems associated with the waste dump site.
The outcome of this study may ginger the government to
adopt appropriate waste management strategies and control measures over indiscriminate dumping of waste.
Further more, it is hoped that the findings of this study will motivate other interested researchers in and outside the study area; thus helping to broaden our knowledge which is a prerequisite to formulation of effective control strategies in the future.
Finally, the result of this findings will be included into the
limited literature of pollution studies in the study area, and to the numerous existing literatures on studies around waste dumpsites.
1.5 Research questions
1) Why did you embark on pollution studies in the vicinity of the chosen dumpsite?
2) Was the levels of physico-chemical parameters and
heavy metal in all the samples analysed within the permissible limits?
3) Was there any variation in physico-chemical parameters
in all the samples analysed during the wet and dry seasons?
4) Was there any significant difference in heavy metal
concentrations in soil at dumpsite compared with soil outside the dumpsite?
1.6 Scope of the study
These findings, examined the physico-chemical and heavy metal characteristics of leachate, borehole water, treated water, stream water and soils at the vicinity of a municipal solid wastes dumpsite at Uyo metropolis, Akwa-lbom State, SE Nigeria, during the wet and dry seasons.
This material content is developed to serve as a GUIDE for students to conduct academic research
LEACHATE GROUNDWATER SURFACE STREAM TREATED WATER AND SOIL CHARACTERISTICS OF THE VICINITY OF A MUNICIPAL SOLID WASTE DUMPSITE AT UYO METROPOLIS AKWA-IBOM STATE NIGERIA
Project 4Topics Support Team Are Always (24/7) Online To Help You With Your Project
Chat Us on WhatsApp » 09132600555
DO YOU NEED CLARIFICATION? CALL OUR HELP DESK:
09132600555 (Country Code: +234)
YOU CAN REACH OUR SUPPORT TEAM VIA MAIL: [email protected]
09132600555 (Country Code: +234)