Effects of columbite/tantalite (COLTAN) mining activities on water quality in Edege-Mbeki mining district of Nasarawa state, North Central Nigeria
Bulletin of the National Research Centre volume 43, Article number: 179 (2019)
The release of environmental pollutants such as heavy metals due to mining activities has received worldwide condemnation. Therefore, understanding the contamination of both surface and groundwater in Edege-Mbeki mining district is very important for the health and wellbeing of its people. Hence, the purpose of this study was to determine the physicochemical parameters of water samples and the level of heavy metals in Edege-Mbeki Columbite/Tantalite (COLTAN) mining site, North Central Nigeria.
A total of 15 water samples were collected and analyzed in triplicate. The concentrations of five heavy metals (Ni, Mn, Pb, Cd, and Fe) in surface and groundwater samples were measured using atomic absorption spectrophotometer (AA-6800 Shimadzu). The physicochemical properties of the water samples were also examined. The results of the water quality assessments show that the water samples were contaminated with alarming levels of Pb, Cd and Ni. Mean concentrations were Ni (0.008 mg/L), Mn (0.087 mg/L), Pb (0.324 mg/L), Cd (0.029 mg/L), and Fe (0.839 mg/L) in Edege-Mbeki groundwater, while the surface water (mining ponds) had Ni (0.102 mg/L), Mn (0.099 mg/L), Pb (0.358 mg/L), Cd (0.025 mg/L), and Fe (6.99 mg/L). The groundwater samples in Mararaban-Edege which served as the control site had mean concentration levels of Ni (0.032 mg/L), Mn (0.096 mg/L), Pb (0.122 mg/L), Cd (0.039 mg/L), and Fe (0.608 mg/L). The range of pH was found to be from 5.6 ± 0.02 to 6.5 ± 0.12, turbidity was between 39.27 ± 0.29 and 2271 ± 0.00 NTU, and conductivity ranged from 39.27 ± 0.29 to 757.33 ± 5.69 μS/cm, TDS from 25.0 ± 2.3 to 450.67 ± 6.03 mg/L while dissolved oxygen (DO) values from 3.1 ± 0.3 to 3.5 ± 0.3 mg/L.
This study confirmed that surface and ground water samples in Edege-Mbeki and Mararaban-Edege are not fit for human consumption and other domestic use. Hence, government and community leaders must provide alternative means of water for the people of these communities.
The pollution of water sources by heavy metals has received attention and widespread condemnation from environmentalists owing to the toxicity, abundance, persistence, and biomagnifications of heavy metals in the environment and their long-term accumulation in marine organisms (Wei et al. 2018). Heavy metals in the environment could originate from either natural or anthropogenic sources (Masindi and Muedi 2018). However, anthropogenic activities such as mining are known to release a significant amount of toxic metals into the environment (EPA 2007). Research has shown that mining is the most critical contributor to heavy metal pollution in river basins. Apart from the pollution of water bodies by heavy metals, mining activities bring about the destruction of the natural ecosystem through the alteration of soil vegetative cover and the fauna beneath (Ologundudu 2019). Therefore, mining poses a great toxicological danger for the surrounding ecosystem and the human population (Franco-Hernández et al. 2010). From the foregoing, therefore, it is very imperative to understand the concentration, distribution, and sources of heavy metals in the environment. This will serve as a scientific point of reference for the protection of water resources, the control of water pollution and the remediation of polluted sources (Wei et al. 2018).
The mining of columbite/tantalite (COLTAN) has a negative effect on the different spheres of the environment notably; hydrosphere, lithosphere, and the atmosphere (Eisler 2004). Just like gold mining, COLTAN extraction involves the breaking of crystallographic bond in the mineral ore to get the products in the pure form. By so doing, a large quantity of waste is generated and subsequently released into the environment (Ologundudu 2019).
Acid mine drainage is one of the major sources of toxic metals that is associated with high concentrations of iron, mercury, arsenic, and antimony, thus contaminating both ground and surface water (Corkhill and Vaughan 2009). The use of fossil fuels for energy generation used in large scale mining operations also releases huge amounts of toxic metals into the atmosphere. A series of reactions in the atmosphere ensures that the toxic metals end up in the water body, hence, contaminating it (Adejumoke et al. 2018). Furthermore, seasonal variability in precipitation and temperature has a significant impact on the concentration of toxic metals and the effects on wildlife (Said et al. 2012).
Edege-Mbeki plays an essential role in Nasarawa Local Government Area in terms of revenue generation and agricultural activities. The Nigerian government’s drive to diversify the economy to reduce its dependence on oil revenue has seen an influx of both registered companies as well as artisanal miners into the old mining town. Over 60 years of unsustainable mineral exploration and mining activity have severely damaged the fragile local ecological environment and compromised water quality. Additionally, most of the mines are located near Paddock (the biggest mining pond in the mining district) and Odemu, two of the vital sources of water. Hence, the quality of water has deteriorated. These areas have increasingly brought about conflict between locals and the miners and drawn the attention of local and state governments. Suffice it to say that little attention has been paid to the deterioration of the water quality in response to human activities such as mining.
In order to evaluate the damages that COLTAN mining activities exert on the environment, especially in areas where old methods of mining are still practiced, this present study aimed to investigate the contents of Ni, Mn, Pb, Cd, and Fe in ground and surface water in the mining district of Edege-Mbeki and to determine how the physicochemical parameters affect heavy metals’ concentration. The choice of these heavy metals is premised on their potentially toxic nature and their adverse health effects above a threshold level (Khan and Bhat 2011). The results obtained can be applied to improve water management efficiency.
Edege-Mbeki is located in Nasarawa local government area of Nasarawa state, North Central Nigeria, at latitude 08°19′30′′ N and longitude 70°50′80′′ E (Fig. 1) with an area of about 400 km2. The area falls within the tropical guinea savannah with a mean annual rainfall of 1000–1500 mm and a mean temperature of 25.60 °C (Akintola 1986).
Edege-Mbeki mining district (Fig. 2) is geologically underlain by the cretaceous sedimentary rocks and the Jurassic younger granite of the middle Benue trough. The Benue trough is a rift basin that extends for about 800 km in length and 150 km in width, with approximately 6000 m of cretaceous tertiary sediments (Okegye and Gajere 2015). In the study area, the main anthropogenic activities consist of agriculture, mining, and grazing. However, agricultural activity in this area has greatly dwindled due to mining and insecurity problems.
Materials and methods
Water sample collection and pre-treatment
To assess the water quality and the concentration of heavy metals in the study area, a total of 15 water samples were collected from mining ponds and hand-dug wells in April 2017. The collection and preservation of all water samples were carried out according to the methods of APHA (2005). Well-labeled and preserved polyethylene sampling bottles (2 dm3) previously cleaned by washing in detergent, rinsed with tap water, and later soaked in 10% HNO3 for 24 h and finally rinsed with distilled water before they were used for sampling. At each sampling point, the bottles were rinsed three times with the water before the collection of a 15-ml water sample. Figure 2 shows all the sampling sites and the distribution of mines. Five water samples were collected in the mining ponds around the mines; one of which was collected from tailings pond, and five hand-dug well water samples were collected from Edege-Mbeki town. Furthermore, five hand-dug well water samples were also collected at Mararaban-Edege (control site). At the time of sampling, there was no control for surface water because all the streams in the area had dried up.
All the water samples collected were filtered into polyethylene sampling bottles that were prewashed with de-ionized water. During the sampling times, parameters such as pH, electrical conductivity, temperature, and total dissolved solids were measured on-site using a portable Jenway pH/conductivity meter (Jenway 430), and turbidity was measured using a portable Hanna digital turbidity meter while the dissolved oxygen level was measured using a Biocotek portable DO analyzer. The pH meter was calibrated with pH 4 and 7 standards. The collected water samples were preserved by acidifying with concentrated HNO3 to keep the metal ions in the dissolved state and slow down microbial activities (Boamponsem et al. 2010) and then stored in the ice chest at 4 °C and shipped to the laboratory for heavy metal analysis.
Digestion of water samples for heavy metal analysis
Exactly 5 ml of water samples were digested by the addition of exactly 10 ml of concentrated nitric acid and 10 ml of hydrogen peroxide. This was heated on a hot plate to about half the original volume. The flask was allowed to cool, its contents were filtered into a 25-ml standard volumetric flask and made up to the mark with distilled water according to Popoola et al. (2011). The digest was then filtered into 25-ml standard flask, and cooled and diluted to mark. To rule out experimental bias or some random error, triplicate digestion of each sample was carried out and a portion of the solution was used for heavy metal determination. The analysis was conducted using a flame atomic absorption spectrophotometer (model AA240FS).
Quality assurance and quality control
To ensure that the results were authentic and correct, strict quality assurance and control protocols were rigorously adhered to. All the chemicals and reagents used were of analytical grade. All polyethylene sampling bottles and glassware used in the laboratory were cleaned by washing with detergent, rinsed in tap water, later soaked in 10% HNO3 for 24 h, and then finally rinsed with distilled water before use for sampling (APHA 2005).
The contamination factor (CF) is obtained using the following equation:
which was used by Boamponsem et al. (2010). In this research work, the WHO (2004) guidelines for drinking water quality were selected as the background level for the calculation of the contamination factor of the water samples.
Modified degree of contamination (mCd)
The excessive value of monitored heavy metals in water samples was assessed using a modified and generalized form of Hakanson equation (Ata et al. 2009). This equation is given as follows:
where n = number of analyzed elements, i = ith element or pollutant, and CF = contamination factor. Table 1 gives a gradation of the classification and description of the mCd according to Abrahim and Parker (2008).
The pollution load index (PLI) of heavy metals
This index has been used for pollution assessment of heavy metals in the water samples within the area of study (Bhupander et al. 2011). The pollution load index for each site was calculated using the following relation:
where CF is the contamination factor of each metal that will be examined, and n equals the number of contamination factor.
A PLI value > 1 indicates pollution whereas PLI value< 1 indicates no pollution (Ong et al. 2012).
Enrichment factor (EF) of heavy metals
An enrichment factor is a parameter that is used to evaluate natural or anthropogenic sources of heavy metal content in the soil and water (Ata et al. 2009). This index was used to distinguish between natural and anthropogenic sources. To calculate the enrichment factors for the entire element, iron (Fe) will be used as a reference element. Reference elements are mostly conservative ones, such as the most commonly used elements which include Fe, Sc, and Ti (Hernadez et al. 2003; Ata et al. 2009).
where (Cn/Cfe) sample is the ratio of the concentration of the element of concern (Cn) to that of Fe in the sediment sample and (Cn/Cfe) shale has the same ratio with an unpolluted reference sample.
The results of the study carried out on both surface and groundwater samples are presented below (Table 2). Triplicate determinations were carried out simultaneously for each sample and the results were recorded as average.
Water physicochemical properties and quality assessment pH
According to Fakayode (2005), the pH of a water body determines the quality because it affects the solubility and toxicity of metals. The pH of both ground and surface water in the study area is slightly acidic. During the present investigation, the mean pH of the water samples (well) was observed to be less than the WHO (2004) permissible range of 6.5 and 9.2 units. However, the pH level of surface water (6.57 ± 0.21) was within the WHO permissible range. It is important to note that the groundwater sample in the control area is more acidic than the study area. This may be attributed to the composition of rocks and sediments. Furthermore, the high acidity may be linked to the high concentration of CO2 due to more human activities in the control area (Osinbajo 2012). Acidic water has been shown to lower the pH of water, hence, increasing the concentration of heavy metals such as lead, copper, and zinc (SON 2007).
Electrical conductivity (EC) measures the ability of water to conduct electricity, which is related to the amount of dissolved minerals in the water without an indication of which element is present or absent. A high value of EC is an indication of the presence of sodium, potassium, chloride, or sulfate contaminants (Orebiyi et al. 2010). EC conductivity is a good way to measure the total dissolved ions as it has a direct relationship with the total amount of solids in the water samples. This then means that a high number of dissolved ions in water translate to a greater number of ions in water (Adewoye et al. 2013). Analysis of the results of this research shows that the EC of all the water sampled were below the WHO (2004) permissible limit of 1000 μS/cm (Table 2).
Total dissolved solid (TDS)
Total dissolved solids refer to the inorganic and small amounts of organic matter present in solution in water (WHO 2006). There are no known possible health effects associated with the ingestion of drinking waters with high total dissolved solids. Rather, the result of an early epidemiological study shows that low concentrations of TDS in drinking water have beneficial effect. However, the presence of high TDS may be unacceptable to consumers due to the taste and scaling of pipes, boilers, heaters, and household appliances (WHO 2006). All the water samples analyzed in the study area were found to be below the WHO (2004) permissible limits of 500 mg/L. However, the control area has a higher amount of TDS. In the control area, agricultural activity is intensive as well as industrial activities. This may be responsible for the higher values.
Water turbidity is very important because high turbidity is often associated with a higher level of disease-causing organisms such as bacteria and other parasites (Shittu et al. 2008). The turbidity values of all the water samples analyzed were above the WHO (2006) permissible limit of 5 NTU. This may be due to the presence of a large amount of inorganic particulate matter, suspended minerals, bacteria, and plankton, as well as dissolved organic and inorganic substances. The high turbidity values obtained, therefore, indicate that the water located in the study area is unhealthy for human use and consumption. Besides, the high turbidity of the water decreases the concentration of oxygen in the water and the photosynthetic activity of plants and algae (Teng et al. 2007).
Dissolved oxygen (DO)
Dissolved oxygen is one of the most important parameters used to measure water quality and to determine the degree of freshness of a river (Fakayode 2005). It is also used to indicate the level of organic pollution in a water body (Wetzel and Likens 2006). It is important to note that there is a direct relationship between the amount of dissolved oxygen and temperature as well as biological activities (Chapman and Kimstach 1992). The maximum DO level recorded at the mining ponds was (3.5 ± 0.3 mg/L) while 3.1 ± 0.3 mg/L was the minimum recorded in Mararaban-Edege. The high value recorded in surface water may be attributed to the open-source of the water and is highly enriched with oxygen from the atmosphere. For all the water samples analyzed, the values were below the 5-mg/L minimum standard limit (WHO 2006). These low values of DO might retard the biochemical reactions in all the water samples.
Water contamination by heavy metals (Ni, Mn, Pb, Cd, and Fe) was evaluated by comparing their concentrations with the guidelines for drinking water and surface water established by the Standard Organisation of Nigeria (SON). The surface and groundwater resource in the study area plays an important role in the supply of water resources for human consumption, agricultural, and mining activity. Standard Organisation of Nigeria (SON) served as the primary guideline against which to evaluate the heavy metal contamination (Table 3).
The result of heavy metals in the study area shows that the level of nickel in all the water samples was above the recommended level by the Nigerian standard (Table 4) except for well water in Edege-Mbeki. This could pose a serious health challenge to the inhabitants of the study area. Research shows that contact with nickel or nickel compounds has adverse effects such as contact dermatitis, lung fibrosis, cardiovascular, and kidney disease as well as cancer of the respiratory tract. Other health effects include nausea, vomiting, cough, giddiness, headache, abdominal problems, diarrhea, and visual disturbance (El Safty et al. 2018).
The level of manganese in all the water samples analyzed was below the maximum desirable limit as specified in the national and international standards. This means the people may not suffer from the problem of manganese, because excess manganese can increase bacterial growth, interfere with the ingestion of dietary iron, and cause hypertension in patients older than 40 years (Adewoye et al. 2013).
The most significant of all heavy metals are lead (Pb) owing to its toxicity and abundance in the earth’s crust (Gregoriadou et al. 2001). Lead is harmful even in the minutest quantity (Adewoye et al. 2013). Children are more susceptible to Pb exposure than adults; it has been shown to impair children’s physical growth and lowering their intelligence (Agency for Toxic Substance and Disease Registry 2007). Exposure to lead has been associated with attention deficit, hyperactivity disorder, antisocial behavior, an endocrine disorder, and hormonal dysfunction. Furthermore, lead is a known carcinogen and a neurotoxin substance (Bellinger 2008). All the water samples analyzed showed lead (Pb) concentration above the maximum permissible limit as specified by the SON standard, indicating Pb contamination. The high concentration of Pb may result in metallic poisoning that manifests in possible human carcinogens (Bakare-Odunola 2005).
Cadmium is a known carcinogen, especially for lung cancer. It also causes kidney, intestinal, and lung damage. Cadmium is associated with behavioral and learning defects, low fetal weight, and skeletal deformation in pregnant animals. Research also suggests that low sperm count and low birth weight are caused by cadmium (EPA 2007). In the study under review, cadmium was above the national and international permissible limit, meaning there was cadmium contamination.
Fe is a necessary element found in nearly all living organisms and is considered at the border between macro and microelements. Iron-containing enzymes and proteins often contain heme-prosthetic groups that participate in many biological oxidations and transport (Chandra et al. 2009). The concentration of iron ranged from a minimum of 0.608 ± 0.540 mg/L to a maximum of 6.99 ± 6.06 mg/L. The iron (Fe) content of all the water samples was found to be below the WHO (2004) maximum permissible limit of 1 mg/L except for surface water in Edege-Mbeki (6.99 ± 6.06). Though an important component of human dietary requirement required by hemoglobin, a high concentration of iron is stored in the pancreas, heart, spleen, and the liver. This may end up damaging these vital organs. Furthermore, the presence of excess iron in water affects the taste as well as promotes the growth of iron bacteria that increases the rate of rusting (Chukwu et al. 2008).
From the foregoing, the result of the water quality in Edege-Mbeki mining district was within the permissible limit values concerning the physicochemical parameters. However, the water samples were contaminated with alarming levels of Ni, Cd, and Pb. Therefore, the water quality is not good, and it is contaminated; hence, appropriate measures need to be put in place to avoid an outbreak of diseases.
All the water samples analyzed showed very high contamination (CF > 6) for Pb and Cd, while the remaining samples showed low to medium contamination. Mining pond water in Edege-Mbeki recorded the highest contamination degree of 11.29 for all the heavy metals analyzed. The well waters of both Edege-Mbeki and Mararaban-Edege recorded moderately low to high values of contamination degree (5.53−8.71).
The enrichment factors (EF) calculated for nickel (Ni) and manganese (Mn) for all the water samples was lower than 2 except for nickel in Mararaban-Edege, thus highlighting their natural origin in the water samples. However, except Edege-Mbeki surface water (mining pond), the enrichment factor for lead (Pb) and cadmium (Cd) in the water samples was found to be greater than 2. On the whole, the presence of lead (Pb) and cadmium (Cd) in the water samples of the study area may be due to anthropogenic origin and artisanal tantalite/columbite mining probably.
The physicochemical properties of water samples were generally within the national and international acceptable limits. On the other hand, groundwaters of all the studied villages, as well as surface water of Edege-Mbeki, were contaminated with Ni, Cd, Fe, and Pb. This implies that all the water sources within the mining district of Edege-Mbeki (Nasarawa Local Government Area of Nasarawa state) may not be fit for drinking purposes.
The authors recommend the regular monitoring and evaluation of water and sediment samples in Edege-Mbeki all year round. Furthermore, for the biodiversity and endangered species to be protected, spatial assessment of water and sediment samples in Edege-Mbeki mining district is recommended.
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The authors wish to thank the Multi-User Science Research Laboratory (MUSRL) of the Department of Chemistry Ahmadu Bello University Zaria and the National Research Institute for Chemical Technology (NARICT) Zaria for the Laboratory and AAS Analysis.
The cost associated with the collection, analysis, and interpretation of data in this manuscript was the responsibility of the corresponding author.
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Isah, M.E., Abdulmumin, N.A., Elaoyi, P.D. et al. Effects of columbite/tantalite (COLTAN) mining activities on water quality in Edege-Mbeki mining district of Nasarawa state, North Central Nigeria. Bull Natl Res Cent 43, 179 (2019). https://doi.org/10.1186/s42269-019-0237-0
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