Transfer Factor of Heavy Metals due to Mining Activities in Plateau State, Nigeria (Health Implications on the Inhabitants)

Authors

  • J. Waida Department of Physics, Borno State University, Maiduguri, Borno State, Nigeria
  • U. Ibrahim Department of Physics, Nasarawa State University, Keffi, Nasarawa State, Nigeria
  • N. G. Goki Department of Geology and Mining, Nasarawa State University, Keffi, Nasarawa State, Nigeria
  • S. D. Yusuf Department of Physics, Nasarawa State University, Keffi, Nasarawa State, Nigeria
  • Rilwan Loko Usman Department of Physics, Nigerian Army University, Biu, Borno State, Nigeria.

DOI:

https://doi.org/10.30564/jor.v4i2.4490

Abstract

Accumulation of heavy metals in agricultural soils is instigated by industrial and other human activities such as mining, smelting, cement-pollution, energy and fuel production, power transmission, traffic activities, intensive agriculture, sludge dumping and melting operations. Plants received heavy metals from soils through ionic exchange, redox reactions, precipitation-dissolution, and so on. Which implies that the solubility of trace elements based on factors like minerals in the soil (carbonates, oxide, hydroxide etc.), soil organic matter (humic acids, fulvic acids, polysaccharides and organic acids), soil pH, redox potential, content, nutrient balance, other trace elements concentration in soil, physical and mechanical characteristics of soil, soil temperature and humidity, and so on. In this study, the soil-edible plant and soil-water Transfer Factor (TF) for various metals showed that the TF values differed slightly between the locations. On soil-edible plant transfer, the mean TF for different heavy metals in soil-edible plants decreased in the following order: As (0.6) mg/kg > Cd (0.1) mg/kg > Cr (0.06) mg/kg > Pb (0.003) mg/kg > Ni (0.001) mg/kg. The total TF for different location decreases in the following order: Barkin Ladi (1.0) mg/kg > Jos South and Jos East (0.7) mg/kg > Bassa and Mangu (0.6) mg/kg. On soil-water transfer, the mean TF for different heavy metals in soil-edible plants decreased in the following order: Cd (0.001) mg/l > As (0.0007) mg/l > Cr (0.0005) mg/l > Pb (0.0001) mg/l and Ni (0.0001) mg/l. The total TF for different location decreases in the following order: Jos South (0.003) mg/kg > Barkin Ladi, Bassa, Jos East and Mangu (0.002) mg/kg. Based on the findings of this study, it can be concluded that the water and edible plants in the study area are good for public consumption, even though, regular checking of heavy metals in the study area is recommended.

Keywords:

Heavy Metals, Soil-Plant, Soil-Water, Transfer Factor, Water, Soil, Edible Plant

References

[1] Balabanova, B., Stafilov, T., Šajn, R. and Bačeva, K. (2014). Comparison of response of moss, lichens and attic dust to geology and atmospheric pollution from copper mine. International Journal of Environmental Science and Technology. 11: 517-528.

[2] Moore, F., Kargar, S. and Rastmanesh, F. (2013). Heavy metal concentration of soils affected by Zn-smelter activities in the Qeshm Island, Iran. Journal of Sciences, Islamic Republic of Iran. 24: 339-346.

[3] Ogunkunle, C.O., Fatoba, P.O., Awotoye, O. O. and Olorunmaiye, K. S. (2013). Root-shoot partitioning of copper, chromium and zinc in Lycopersicon esculentum and Amaranthus hybridus grown in cement-polluted soil. Environmental and Experimental Biology. 11: 131-136.

[4] Yan, X., Zhang, F., Zeng, C., Zhang, M., Devkota, L. P. and Yao, T. (2012). Relationship between heavy metal concentrations in soils and grasses of roadside farmland in Nepal. International Journal of Environmental Research and Public Health. 9: 3209-3226.

[5] Kouamé, I.K., Kouassi, L.K., Dibi, B., Adou, K. M., Rascanu, I. D., Romanescu, G., Savané, I. and Sandu, I. (2013). Potential groundwater pollution risks by heavy metals from agricultural soil in Songon area (Abidjan, Côte d’Ivoire). The Journal of Environmental Protection. 4: 1441-1448.

[6] Shamuyarira, K. K. and Gumbo, J. R. (2014). Assessment of heavy metals in municipal sewage sludge: A case study of Limpopo Province, South Africa. International Journal of Environmental Research and Public Health. 11: 2569-2579.

[7] Bi, X., Feng, X., Yang, Y., Qiu, G., Li, G., Li, F., Liu, T., Fu, Z. and Jin, Z. (2006). Environmental contamination of heavy metals from zinc smelting areas in Hezhang County, western Guizhou, China. Environment International. 32: 883- 890.

[8] Tarradellas, J., Bitton, G. and Russel, D. (1996). Soil Ecotoxicology. (ed) CRC Lewis Publisher, New York.

[9] Panuccio, M. R., Sorgonà, A., Rizzo, M. and Cacco, G. (2009). Cadmium adsorption on vermiculite, zeolite and pumice: batch experimental studies. Journal of Environmental Manage. 90: 364-374.

[10] Guala, S. D., Vegaa, F. A. and Covelo, E. F. (2001). The dynamics of heavy metals in plant-soil interactions. Ecological Modelling. 221: 1148-1152.

[11] Mmolawa, K. B., Likuku, A. S. and Gaboutloeloe, G. K. (2011). Assessment of heavy metal pollution in soils major roadside areas in Botswana. African Journal of Environmental Science and Technology. 5: 186-196.

[12] Freitas, H., Prasad, M. N. V. and Pratas, J. (2004). Plant community tolerant to trace elements growing on the degraded soils of São Domingos mine in the south east of Portugal: environmental implications. Environment International. 30: 65- 72.

[13] Ibrahim, A. K., Yakubu, H. and Askira, M. S. (2014). Assessment of heavy metals accumulated in wastewater irrigated soils and lettuce (Lactuca sativa) in Kwadon, Gombe State Nigeria. American-Eurasian Journal of Agricultural & Environmental Sciences. 14: 502-508.

[14] Krstic, B., Stankovic, D., Igic, R. and Nikolic, N. (2007). The potential of different plant species for nickel accumulation. Biotechnology & Biotechnological Equipment. 21: 431-436.

[15] Naser, H. M, Sultana, S., Mahmud, N. U., Gomes, R. and Noor, S. (2011). Heavy metal levels in vegetables with growth stage and plant species variations. Bangladesh Journal of Agricultural Research. 36: 563-574.

[16] Jolly, Y. N., Islam, A. and Akbar, S. (2013). Transfer of metals from soil to vegetables and possible health risk assessment. Springer Plus. 2: 385.

[17] Filipović-Trajković, R., Ilić, S. Z. and Šunić, L. (2012). The potential of different plant species for heavy metals accumulation and distribution. The Journal of Food, Agriculture and Environment. 10: 959-964.

[18] Rangnekar, S. S., Sahu, S. K., Pandit, G. G. and Gaikwad, V. B. (2013a). Study of uptake of Pb and Cd by three nutritionally important Indian vegetables grown in artificially contaminated soils of Mumbai, India. International Research Journal of Environmental Sciences. 2: 1-5.

[19] Usman, R., A.M. Kamal, E.I. Ugwu, I.M. Mustapha, A. Mamman, and A. Hudu. 2020. “Assessment and Analysis of the Presence of Heavy Metals in Water in Ara and Laminga of Nasarawa State, Nigeria: Health Implication on the Populace”. The Pacific Journal of Science and Technology. 21: 240-246.

[20] Rilwan Usman, A. M. Kamal, A. Mamman, M.M. Idris, A. Ubaidullah, O.G. Okara and E.I Ugwu (2021). Health Implication of the Accumulation of Heavy Metals Concentration in Ara and Laminga Water Sources of Nasararawa Local Government Area in Nasarawa State, Nigeria. NAUB Journal of Science and Technology (NAUBJOST). 1: 101-106.

[21] Usman Rilwan, Auta Abdullahi Abbas and Hudu Abdulrahman (2020). Heavy Metal Contamination in Swampy Agricultural Soils of Kokona, Nasarawa, Nigeria. Asian Journal of Applied Chemistry Research. 5: 28-33.

[22] U. Rilwan, A. A. Abbas and S. Muhammad (2020). Heavy Metal Contamination and Its Risk for Swampy Agricultural Soils of Keffi, Nasarawa West, Nigeria. Asian Journal of Applied Chemistry Research. 5: 1-11.

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How to Cite

Waida, J., Ibrahim, U., Goki, N. G., Yusuf, S. D., & Usman, R. L. (2022). Transfer Factor of Heavy Metals due to Mining Activities in Plateau State, Nigeria (Health Implications on the Inhabitants). Journal of Oncology Research, 4(2), 13–26. https://doi.org/10.30564/jor.v4i2.4490

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