Heavy metal concentrations and degradation efficiency of total petroleum hydrocarbons on environment in ibeno local government area, akwa ibom state, nigeria | Blazingprojects Postgraduate Thesis
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Heavy metal concentrations and degradation efficiency of total petroleum hydrocarbons on environment in ibeno local government area, akwa ibom state, nigeria

 

Table Of Contents


Chapter ONE

INTRODUCTION

  • – – – – – – 1 Statement of problem – – – – – – 8 Objectives of the study – – – – 9 Scope of the study – – – – – – – 10

Chapter TWO

LITERATURE REVIEW

  • – – – – – – 11 Heavy metals – – – – – – – 11 Heavy metals in sediment – – – – – – – 11 Heavy metals in water – – – – – – – 13 Heavy metals in Soil – – – – – – – 14 Sources of heavy metal pollutants in soil – – – – – 16 Individual element – – – – – – 18 Vanadium – – – – – – 18 Sources of vanadium – – – – – – – 18 Vanadium in human being – – – – – – – 19 Vanadium in plant and soil – – – – – – – 20 Health importance of vanadium – – – – – – 20 Effects of vanadium on experimental animals and human beings – 21 Cadmium – – – – – – 21 Sources of cadmium in the environment – – – – – – 22 Uses of cadmium – – – – – – 22 Cadmium in soil – – – – – – 22 Cadmium in plant – – – – – – 23 Effects of cadmium in human beings – – – – – – 25 Lead – – – – – – 25 Uses of lead – – – – – – – 25 Sources of lead in the environment – – – – – – 26 Lead in soil – – – – – – 26 viii Lead in plant – – – – – – – 27 Toxicity of lead – – – – – – 28 Zinc – – – – – – 29 Zinc in the environment – – – – – – – 29 Zinc in fossil fuels – – – – – – – – 29 Zinc in plant – – – – – – – – – 29 Toxicity of zinc – – – – – – 31 Cobalt – – – – – – – 32 Cobalt in soil – – – – – – – 32 Cobalt chemistry affecting availability to plant – – – – 32 Uses and toxicity of cadmium- – – – – – – 33 Nickel – – – – – – – 34 Physical properties of nickel – – – – – – – 34 Nickel in aquatic environment – – – – – – 34 Effect of nickel in plant – – – – – – – 35 Nickel in soil – – – – – – – – – 36 Human exposure to nickel – – – – – – – 38 Telfairia occidentalis (fluted pumpkin) – – – – – 39 Telfairia occidentalis as an environmental bio-indicator for Monitoring of heavy metals soil ecosystem – – – – 41 Types of bio-indicators – – – – – – – 42 Soil electrical conductivity – – – – – – – 44 Soil pH – – – – – – – – – 46 Biodegradation of total petroleum hydrocarbons in soil – – – – 46 Chemical composition of palm bunch ash (PBA) – – – – 51 Tween 80 – – – – – – 52 Chemical structure of Tween 80 – – – – – – 53

Chapter THREE

RESEARCH METHODOLOGY

  • Study design and methodology – – – – – – 54 ix Niger Delta – – – – – – 54 Map of the study area – – – – – – 55 The study area (Qua Iboe Coastal Area) – – – – – 56 Geographical description – – – – – – 56 Climate – – – – – – 56 Geology and hydrogeology – – – – – – – 57 Soil – – – – – – – – – – 57 Socio-economic characteristics – – – – – – 57 Sampling program design – – – – – – – 58 Sampling procedure for soil – – – – – – – 59 Precaution to avoid being exposed to contaminants – – – – 59 Analytical procedure for the soil/sediment samples preparation – – 60 Preparation of aqua regia – – – – – – – 60 Sample collection (fluted pumpkin) – – – – – – – 60 Sample preparation: leaves of fluted pumpkin – – – – – 61 Analytical procedure for fluted pumpkin sample – – – – 61 Experimental – – – – – – – 61 Samples collection procedures: sediment and water – – – – 62 Sample preparation for water – – – – – – – 62 Analytical procedure for sediment – – – – 62 Experimental procedure for determination of electrical Conductivity and pH of the soil – – – – – 63 Determination of total petroleum hydrocarbons – – – 64 Materials and apparatus – – – – – – – 64 Samples collection and preparation — – — – – – 64 Preparation of soil and surfactant mixture – – – – – 66 Analysis of the soil for total petroleum hydrocarbons – – – 66 Statistical analysis – – – – – – 70

Chapter FOUR

DATA PRESENTATION AND ANALYSIS

  • Results and discussion – – – – – – 71 Results of extractable heavy metals concentration in soil, fluted pumpkin, sediment, and water – – – – – 71 Results physicochemical properties of soil – – – – – 86 x Seasonal dynamics of individual element – – – – – 95 Nickel (Ni) – – – – – – – – 95 Vanadium (V) – – – – – – – — 100 Cadmium (Cd) – – – – – – – – 104 Lead (Pb) – – – – – – — – – 110 Manganese (Mn) – – – – – – – – 115 Iron (Fe) – – – – – – – – – 119 Zinc (Zn) – – – – – – – – – 123 Cobalt (Co) – – – – – – – – – 127 Degradation efficiency kinetics of (TPHs) by palm bush ash and Tween 80 – – – – – 130 Effects natural surfactant palm bush ash (PBA) and synthetic surfactant Tween 80 on physicochemical properties of the soil – – – – – – 150 Correlation coefficient (r) between extractable Heavy metals in soil Telfairia occidentalis – – – – 151 Leaves of Telfairia occidentalis (Fluted pumpkin) as bio-indicator – – 154 Dry and wet season’s variation between concentrations of heavy metals in soil, fluted pumpkin, water and sediment – – 156 Relationship between concentrations of heavy metals in the fifteen sampling locations – – 165 Electrical conductivity and pH – – – – – – 176

Chapter FIVE

SUMMARY, CONCLUSION AND RECOMMENDATIONS

  • – – – – – – – – – 183 Contributions to knowledge – – – – – – – 184 Recommendations – – – – – – – – 185 References – – – – – – – – – 186 Appendix – – – – – – – – – 202 

Thesis Abstract

Heavy metal concentrations and degradation efficiency of total petroleum hydrocarbons
(TPHs) on environment in Ibeno Local Government Area, Akwa Ibom State, Nigeria was
investigated. Experimental design method was adopted for this study. Fifteen composite
samples each of soil, leaves of Telfairia occidentalis, sediment and water were collected in
December 2012 and June 2013. The sediment and water samples were collected using corer
and clean plastic bottles respectively. Soil and sediment samples were air dried, mechanically
ground using mortar and pestle, and 2 mm mesh size obtained for further analysis. The soil
and sediment samples (1.0 g) each were weighed into Kjeldahl flasks. Aqua regia (15 cm3)
was added, swirled to mix and kept overnight. The flasks were heated on a hot plate to 50 oC
for 30 min; temperature was later adjusted to 120 oC and heated continuously for 2 h. The
mixture was cooled, and 0.2 M HNO3 (10 cm3) added. The resulting mixture was filtered with
a Whatman no. 541 filter paper. The filtrate was transferred into a 50 cm3 standard flask and
made up to the mark with 0.2 M HNO3. The leaves samples were washed with de-ionized
water, dried to constant weight in an oven at 105 oC, pulverized and 2 mm mesh size obtained
for further analysis. The ground leaves were digested with 1.0 cm3 concentrated HClO4, 5
cm3 concentrated HNO3 and 0.5 cm3 concentrated H2SO4 in 50 cm3 Kjeldahl flask. Each
water sample (10 cm3) was digested with 2 cm3 concentrated HNO3. Concentrations of the
heavy metals were determined using AAS Unicam 939 model. The soil samples (150 g) each
were transferred into four (4) plastic buckets labeled A, B, C and D. Varying concentrations
palm bunch ash (PBA) (0.0 g, 50.0 g), Tween 80 (50.0 g) and PBA + Tween 80 (25.0 g) each
were added to A, B, C, and D, where A served as control. Portions (5 g each) of A, B, C and
D were weighed into standard flasks, 25 cm3 of xylene added and shaken, NaCl (5 g) was
added and left for 72 h. The liquid portion was decanted into a separatory funnel, corked and
shaken. The xylene layer was transferred into 100 cm3 centrifuge tube containing 5 g of
Na2SO4 and agitated for 15 min, the absorbance of the solution was measured at 425 nm and
used for calculating concentrations of TPHs. Concentrations of TPHs were determined at 20
days intervals for 60 days. The data were analyzed on the basis of first order kinetic model
InC = InCo- kt. Heavy metal concentrations (mg kg-1) during dry season were, soil Fe (15.15
± 5.91), Mn (10.36 ±3.18), Cd (0.23±0.31 ), V (0.17 ± 0.29), Ni (0.19 ± 0.05), leaves of
Telfairia occidentalis Mn (7.73 ± 3.06), Fe (5.93±1.28), V (0.16±0.26), Cd (0.21 ± 0.16), Ni
(0.02 ± 0.01), sediment Fe (22.18 ± 14.82), Mn (9.67±2.75), V (3.39±3.30), Ni (2.18±0.78),
Cd (0.48 ± 0.75), and water Mn (2.80±0.93), V (1.53±1.42), Ni (1.50 ± 1.53), Fe (0.86 ±
0.25), Cd (0.27±0.21), During wet season, soil Fe (12.09±4.98), Mn (9.66 ± 2.18), Ni
(0.05±0.03), V (0.04±0.01), Cd (0.04±0.02); leaves of Telfairia occidentalis Mn (7.75±3.76),
Fe (5.96±4.07), V (0.21±0.09), Cd (0.19±0.06), Ni (0.03±0.06), sediment Fe (23.28±0.24),
Mn (9.45±2.63), V (3.31±3.34), Ni (1.94±1.48), Cd (0.48±0.74), and water Mn (3.13 ±
0.79),V (1.88 ±1.45), Ni (1.45 ±1.04), Fe(1.05 ± 0.25), Cd (0.10 ± 0.13), were obtained. The
correlation coefficients were V (0.556), Ni (0.376), Cd (-0.043), Pb (0.856), Mn (0.813), Co
xx
(0.255), Zn (- 0.193), Fe (- 0.383), and V (-0.419), Ni (- 0.355), Cd (0.248), Pb (0.745), Mn
(0.974), Co (- 0.022), Zn (0.886) and Fe (-0.384) for dry and wet seasons respectively. The
mean concentration of TPHs in the soil was 14.55±0.01 mg kg1. Degradation efficiencies
obtained were PBA (86.69 %), PBA + Tween 80 (85.63 %), Tween 80 (76.70 %), and control
(5.40 %). The rates of degradation (mg kg-1 day-1) ranged from 2.70×10-2 to 1.30×10-2;
5.00×10-1 to 2.18×101; 2.49×10-1 to 1.84×10-1 and 4.67×10-1 to 2.09×10-1 for A, B, C and D
respectively. k ranged from 2.09 × 10-2 to 2.78 × 10-2, 3.79×10-2 to 5.81×10-2, 2.78×10-2 to
2.09×10-2, 5.13×10-2 to 3.23×10-2 for A, B, C and D respectively. Concentrations of heavy
metals in wet and dry seasons were variables. The concentrations of all the investigated
heavy metals in soil were within permissible range as recommended by DPR, but higher than
the reference soil samples. Mean concentrations of some of the investigated heavy metals
(Ni, V, Pb, Zn and Co) in leaves of Telfairia occedentalis were within the normal range of
WHO and FME standards for vegetables and food stuff except Cd, Fe and Mn. The
concentrations of Ni, V, Cd, Pb, and Mn in water were higher than WHO and DPR standards.
Also, the concentrations of Mn, Ni, Pb, and Zn in sediment were higher in dry season
compared to wet season except Fe, V and Co. Concentrations of Fe were the highest in all
the seasons; sediment retained the highest concentrations of heavy metals. Telfairia
occidentalis can be used as a resident indigenous plant bio indicator for monitoring
anthropogenic influenced V, Pb, Mn and Zn in the soil of the study area. Degradation
efficiency of TPHs were as follows PBA (86.69 %) > PBA + tween 80 (85.63 %) > tween 80
(76.70 %) > control (5.40 %). The rate of degradation of TPHs decreased as the
concentrations of the surfactants decreased with time.

 


Thesis Overview

<p> </p><p>INTRODUCTION<br>Metal pollutants have been a part of human history since the dawn of civilization. However,<br>toxic metals pollution of the biosphere has intensified rapidly since the onset of the industrial<br>revolution, posing major environmental and health problems1. Recently, environmental<br>scientists have raised concern on the increasing ecological and toxicological problems arising<br>from pollution of the environment. Heavy metals represent an important source of the<br>pollution 2. Heavy metals like As, Pb, Hg, Cd, Co, Cu, Ni, Zn, and Cr are phyto-toxic at all<br>concentrations or above certain threshold levels3. Toxic metals are biologically magnified<br>through the food chain. They infect the environment by affecting soil properties, its fertility,<br>biomass, crops yield and human health3.<br>Heavy metals occur naturally in small quantities in soil though rarely at toxic level,<br>but human activities have raised these to exceptionally high levels at many polluted land and<br>water sites. Soil is a crucial component of rural and urban environments, and in both places,<br>land management is the key to soil quality4. Human endeavours such as technology,<br>industrialization, agriculture, transportation, education, construction, trade, commerce, as<br>well as nutrition have rendered the whole environmental system a “throwing society”. This is<br>true because indiscriminate disposal of wastewater coupled with increasing world population<br>and urbanization have combined to worsen the situation. The use of synthetic products e.g.<br>(pesticides, paints, batteries, industrial waste, and land application of industrial and domestic<br>sludge) can result in heavy metal contamination of urban and agricultural soils.4<br>The extent of soil pollution by heavy metals and metal base ions, some of which are<br>soil micronutrients is very alarming. Ademoroti 5, reported positive linear correlation<br>between cadmium, lead, and nickel contents in the soil and vegetable.<br>Essein et al. 4, observed the trend of mean heavy metals concentrations in Mkpanak a<br>community in the study area as Fe &gt; Zn &gt; Pb &gt; Ni &gt; V &gt; Cd. The mean concentration of iron<br>in the soil was quite high and exceeded the critical toxicity level. The result obtained also<br>showed that the mean concentration of Cd was high and exceeded the lower limit of 0.01 mg<br>kg-1. Also, Osuji et al.6, had earlier reported possible bio-magnification of Ni, V, Pb, Cu and<br>Cd in the area. Industrial wastes are the major sources of soil pollution and originate from<br>mining industries, chemical industries, metal processing and petroleum industries; the wastes<br>include a variety of chemicals like heavy metals.6<br>2<br>While many heavy metals are essential elements at low levels, they can exert toxic<br>effects at concentration higher. Soil receives heavy metals coming from different sources and<br>at the same time acts as a buffer, which controls the movement of these heavy metals to other<br>natural components2.<br>Increase in anthropogenic activities, heavy metals pollution of soil, water and<br>atmosphere represent a growing environmental problem affecting food quality and human<br>health 7 in the Niger Delta region of Nigeria. Nigeria as a major producer and exporter of<br>crude petroleum oil continue to experience oil spill and this exposes the environment to<br>hazards and its effects on agricultural lands as well as on plant growth8. Oil pollution of soil<br>leads to the buildup of essential (Organic carbon, P, Ca, Cu) and non-essential (Mn, Pb, Zn,<br>Fe, Co, Cu) elements in soil and the eventual translocation in plant tissues9. Industrialization<br>coupled with an ever-increasing demand for petrochemicals have resulted in prospecting for<br>more oil wells with consequent pollution of the environment. Causes of oil pollution in<br>Nigeria include discharge from sludge, production test, drilling mud, and spills from<br>pipelines, well blowouts, gas flaring and sabotage10. Oil spills have long effects on soil; an<br>immediate effect of petroleum products in the soil is a depression in population of soil<br>microorganisms. Besides the economic and aesthetic damages caused by oil spills, plants and<br>animals life in both aquatic and terrestrial environment are affected as most life form die<br>rapidly following spillage. Many unique plants and animals’ species have gone into<br>extinction in the Niger Delta regions11.<br>Pollution of the ecosystem by toxic metals during man’s activities poses serious<br>concerns because heavy metals are not biodegradable and are persistent in the ecosystem.<br>Once metals are introduced and contaminate the environment, they will remain for a very<br>long time.11<br>The presence of heavy metals in toxic concentrations can result in the formation of<br>super oxide radicals, hydrogen peroxide (H2O2), hydroxide radicals (OH-), bio-molecules like<br>lipids, protein and nucleic acid. Chromium, Copper and Zinc can induce the activity of<br>various antioxidant enzymes and non-enzymes like ascorbate and glutathione3. Petroleum<br>renders the soil infertile, burns vegetation and kills useful soil organism12.<br>In Nigeria, a study of heavy metals concentration near Warri refinery found three to<br>seven times elevated levels of various heavy metals in the soil13. Although the petroleum<br>industry is by far the largest industrial sub-sector in the Niger Delta, at least eight of the most<br>polluting sub-sectors in Nigeria (steel work, metal fabrication, food processing, textile,<br>refineries and paints manufacturing) operate in the Niger Delta13, 14.<br>3<br>Oil exploration and exploitation have uplifted Nigerian economy leading to rapid<br>development but the impact on the environment is receiving less attention15. One of the major<br>anthropogenic sources of heavy metals enrichment in terrestrial habitats of oil producing area<br>of Nigeria is the frequent spills of crude oil on land and gas flaring 12. Nigerian crude oil is<br>known to contain heavy metals such as Zn, As, Ba, Fe, Pb, Co, Cu, Cr, Ga, Mn, Ni and V.<br>Toxicity of ingested heavy metals has been an important health issue for decades 16.<br>Some species of Brassica (cabbage) are high accumulators of heavy metals in the edible parts<br>of the plants 17 and this can be an important exposure pathway for people who consume<br>vegetable grown in heavy metal contaminated soil 15. The level of heavy metals for examples<br>lead, cadmium and copper where determined in cassava from different location of oil<br>exploration areas of Delta State, Nigeria. The results of different heavy metals have higher<br>values when compared with WHO standard. These metals have damaging effects on the<br>plants themselves and may become hazardous to man and animals. Above certain<br>concentrations and over a narrow range, the heavy metals turn toxic. Moreover, these metals<br>adversely affect natural microbial population leading to disruption of vital ecological<br>processes. Plants can accumulate heavy metals in their tissues and uptake increases generally<br>in plants that are grown in areas with increased soil contamination with heavy metals and<br>therefore, many people could be at risk of adverse health effects from consuming common<br>garden vegetables cultivated in contaminated soil 12.<br>Streit and Strum, and Ruszewski et al 18, 19, classified the exchange of chemicals<br>between soil and plants; they divided the most common method of assessing metal toxicity to<br>plants from soil into three categories:<br>i. monitoring of the presence or absence of specific plant ecotypes and or plant<br>species (indicator plant).<br>ii. measurements of metal concentration in tissues of selected species<br>(accumulative bio-indicators).<br>iii. recording of physiological and biochemical responses (bio-makers) in<br>sensitive bio-indicators.<br>The pollution of rivers, lakes, underground water, bays of oceans, and streams with<br>chemical contaminants (heavy metals, organic and inorganic compounds) has become one of<br>the most critical environmental problems of the century.4 Non-degradable, bio-persistent<br>stock pollutant such as heavy metals and mineral hydrocarbons could get into aquatic<br>environment from a wide range of natural and anthropogenic point sources. In aquatic<br>ecosystems, heavy metals are contained in four reservoirs, namely; the suspended sediment,<br>4<br>the bottom sediment, the surface water and the pore water. Studies have revealed that<br>contaminants in aquatic system are usually in pore water-surface water-sediment dynamic<br>with bottom sediment acting as the major depository of heavy metals5. The questions of<br>heavy metals in water first became an issue only in Sweden and later in Canada.<br>Writing on the impact of economic activities on the environment of the Niger Delta,<br>Agbozu 13, stated that water bodies have been heavily polluted due to the recurring incident<br>of oil spillage. Most micro-populations and invertebrates are eliminated following large-scale<br>spillage, while sub lethal levels of oil following several scale spillages have generally<br>affected aquatic resources.<br>Ibeno Local Government Area is a coastal sub-region characterized by abundant<br>water resources. The absence of potable water supply for domestic use in some parts of Ibeno<br>has compelled the population to rely heavily on natural sources of water supply for domestic<br>uses. The quality of most of these sources of water is doubtful. The study area is one of the<br>coastal area as well as an oil producing area in Akwa Ibom State bordered by the Atlantic<br>ocean and has various environmental problems including pollution of available water<br>resources. There are many types of water sources available for domestic, recreational, fishing<br>and industrial uses. These include ponds, streams, boreholes, lakes, rivers, oceans and rain<br>water, but they are all polluted by human and industrial activities in the area. The<br>anthropogenic and natural phenomena seem to affect water quality in the study area. These<br>include gas flaring, oil spillage, washing wastewater and sludge from industrial processes,<br>poor sanitation, storm surges, salt-water extrusion and intrusion, release of untreated human<br>waste and sewage into waterways.<br>Water pollution occurs when chemical, physical or biological substances exceed the<br>capacity of water body to assimilate or break down the substance that can cause harm to the<br>aquatic ecosystem. Precipitation that reaches the earth’s surface follows two basic pathways;<br>it either flows overhead or soaks into the soil20. Water that flows over the ground is often<br>called run off. The term surface water refers to water flowing in streams and rivers as well as<br>water stored in natural or artificial lakes. Surface water is water that flows or rests on land<br>and is open to atmosphere; lakes, pond, lagoons, rivers, streams, oceans, ditches, man-made<br>impoundments are bodies of surface water 20. Analysis of soil samples from Uyo town by<br>Akaeze 106 disclosed that heavy metals such as lead, copper and iron are present in the soil,<br>these may contaminate soil water, which constitutes the major sources of drinking water 21.<br>Oil spillage and dumping of petroleum effluents on land are common phenomena. Gas flaring<br>also contributes to heavy metals contamination of soil15.<br>5<br>The contamination of the environment by heavy metals is viewed as an international<br>problem because of the effects on the ecosystem in most countries. In Nigeria, the situation is<br>no better by the unethical activities of most industries and because of countries inability to<br>manage industrial wastes with the increasing level of pollution of water bodies.<br>Environmental degradation of the oil rich Niger Delta region has caused a wanton destruction<br>and continuous harm to their health, social and economic consequences for its people, for<br>over a decade. Petroleum refineries produce a wide variety of air and water pollutants and the<br>distillation products of refining and industrialization, intensive agriculture and other<br>anthropogenic activities have led to land degradation, environmental pollution and decline in<br>crop productivity and sustainability. These have been of great concern to human and animal<br>health 22, 23.<br>One of the prominent sources contributing to increased load of soil contamination is<br>the disposal of municipal and industrial wastes. The wastes are either dumped on roadsides or<br>used in landfills. These wastes although useful as sources of nutrients are also sources of<br>carcinogens and toxic metals 23<br>.<br>In the study of the socio-economic impact of oil pollution, Worgu 23 stated that crude<br>oil exploration has had adverse environmental effect on soil, forest and water bodies in host<br>communities in the Niger Delta. All stages of oil exploration impacted negatively on the<br>environment and the greatest single intractable environment problem caused by crude oil<br>exploration in the Niger Delta region is oil spillage. According to Annual reports of the<br>Department of Petroleum Resources (DPR) 1997, over 6,000 spills have been recorded in the<br>40 years of oil exploration in Nigeria with an average of 150 spills per annum. In the period<br>1976 – 1996, 647 incidents occurred resulting in the spillage of 2,369,407.00 barrels of crude<br>oil with only 549,040.38 barrel recovered, while 1,820,410.50 barrels of oil were lost to the<br>ecosystem23. These chemicals if not properly controlled according to guidelines and standards<br>set by regulating agencies like Department of Petroleum Resources, it can pollute the soil and<br>groundwater system in the area where such operation is carried out. Thousands of spills occur<br>across the fragile Niger Delta and have destroyed livelihoods of fishermen and farmers,<br>fouled water sources and polluted the ground and air. The Nigerian government estimates that<br>there were over 7,000 spills, large and small, between 1970 and 2000. That is approximately<br>300 spills a year and some spills have been leaking for years. Vast swathes of the Delta are<br>covered with tar and stagnant lakes of crude. By some estimate, over 13 million barrels of oil<br>have spilled into the Delta. An additional 2,405 spills by all major oil companies in the region<br>6<br>have occurred since 2006. Corroded pipes caused a spill in 2010 that leaked about 232 barrels<br>of crude oil 23.<br>7<br>Table 1: Number of spills, quantity of spills (barrels), and quantity of oil recovered<br>(barrels) and net loss to the environment in barrels between 1976 -1989.<br>Year Number<br>of spills<br>Quantity<br>(barrels)<br>Quantity<br>recovered<br>(barrels)<br>Net loss to the<br>environment<br>(barrels)<br>1976 128 26157.00 7135.00 19021.50<br>1977 104 32879.25 1703 3117675.00<br>1978 154 489294.75 391445.00 97849.75<br>1979 157 64117.13 63482.20 630635.95<br>1980 241 600511.02 42416.23 558094.19<br>1981 238 42722.50 5470.20 37052.30<br>1982 257 42814.00 2171 40669.60<br>1983 173 48351.30 6355.90 41995.40<br>1984 151 40209.00 1644.80 38564.20<br>1985 187 11876.60 1719.30 10157.30<br>1986 155 12905.00 252.00 12358.00<br>1987 129 31866.00 6109.00 25358.00<br>1988 108 9172.00 2153.00 7202.00<br>1989 118 5956.00 2092.55 3830.00<br>Source: Annual report of Department of Petroleum Resources (DPR), 1997191<br>8<br>1.0.1 Statement of the problem<br>The study area (Ibeno Local Government Area) in recent times has received attention<br>owing to considerable stress it has been subjected to through deliberate and or accidental oil<br>spills, blast water discharge, untreated sewage, gas flaring and industrial effluents.<br>Qua Iboe River estuary is the point where petroleum exploration and production (E<br>and P) wastes from the Exxon Mobil Qua Iboe Terminal (QIT) tank farm are transferred to<br>the lower Qua Iboe River estuary and adjourning creeks through two 24 mm diameter pipes.<br>The Exxon Mobil oily sludge dumpsite and flare stack, where gas is flared continuously are<br>in the study area. The study area has a number of oil wells, NNPC pipelines run across and<br>some flow stations situated.<br>Seemingly, most of the terrestrial ecosystem and shorelines in the oil producing<br>communities are under continuous cultivation. After heavy spills of crude oil, soils are<br>usually barren, and may run into low-lying areas with organic soils and natural re-vegetation<br>of the soil generally slow. Depending on the amount of oil in the soil, the soil may remain<br>completely barren for many years. Environmental pollution by the industrial and domestic<br>activities may therefore have far-reaching implication on the agricultural productivity on the<br>area and multiplier effect on the socio-economic wellbeing of the people. At present, there is<br>no report available on the seasonal levels of anthropogenically associated heavy metals in<br>Telfairia occidentalis (fluted pumpkin) a common vegetable cultivated in the study area. In<br>addition, more extensive work is needed on the comparison between the seasonal dynamics<br>of heavy metals levels in soil, plant, sediment and water with local and international<br>guidelines and standards.<br>Also, increase in demand for crude oil and petrochemicals has resulted in exploration<br>for more oil wells with consequent pollution of the environments. This has adversely affected<br>food quality and human health in Niger Delta region of Nigeria. The traditional methods of<br>detection and remediation of environments from contaminants include the use of Atomic<br>Absorption Spectrophotometer (AAS), capping and chemical precipitation for heavy metals<br>in soil and water respectively. In addition, accelerated solvent extraction and application of<br>Tween 80 to degrade total petroleum hydrocarbons (TPHs) in soil are cost prohibiting when a<br>large area is involved. They also affect the biota with resultant adverse effects on human<br>beings. These necessitated the quest for development of alternative, indigenous and ecofriendly<br>green remediation and bio-indicator technologies for controlling and assessing<br>environmental contaminants.<br>9<br>The present study was carried out to determine the existing concentrations of heavy<br>metals in soil, Telfairia occidentalis (fluted pumpkin), water and sediment during wet and dry<br>seasons in Ibeno coastal area. Also, to find bio-indicator properties of Telfairia occidentalis<br>as an indigenous and eco-friendly green tool in detecting heavy metals pollutants in soil of<br>the study area. Furthermore, the present study was conducted to determine the concentration<br>of total petroleum hydrocarbon in the soil of the study area and consequently developed an<br>alternative indigenous and eco-friendly remediation technology for total petroleum<br>hydrocarbon in soil by comparing degradation efficiencies kinetics of natural surfactant<br>(palm bunch ash) and synthetic surfactant (Tween 80).<br>1.0.2 Objectives of the study<br>This research work was designed, to achieve the following objectives:<br>(i) determine seasonal concentrations of heavy metals in soil, sediment, water,<br>and leaves of Telfairia occidentalis,<br>(ii) establish correlation between the amount of the heavy metals in soil and leaves<br>of Telfairia occidentalis,<br>(iii) determine bio-indicator properties of leaves of Telfairia occidentalis,<br>(iv) investigate the amount of total petroleum hydrocarbons (TPHs) in the soil, and<br>(v) compare the degradation efficiencies of the TPHs in the soil amended with<br>palm bunch ash (PBA) and Tween 80.<br>(vi) investigate the effects of palm bunch ash (PBA) and Tween 80 on the<br>physicochemical properties of the soil.<br>10<br>1.0.3 Scope of the study<br>The present study covered the following areas:<br>(i) samples collection and preparation.<br>(ii) determination of heavy metal concentrations, in soil, leaves of Telfairia occidentalis<br>(fluted pumpkin), water and sediment during wet and dry seasons in Ibeno coastal<br>area.<br>(iii) investigation of bioindicator properties of leaves of Telfairia occidentalis (fluted<br>pumpkin)<br>(iv) determination of total petroleum hydrocarbon concentration in soil and investigation<br>of the degradation efficiency kinetics of palm bunch ash and tween 80.<br>(v) verification of the effects of palm bunch ash and Tween 80 on the physicochemical<br>properties of oil polluted soil.</p><p>&nbsp;</p> <br><p></p>

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