International Journal of Environmental Protection and Policy

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Characterized Organic Pollutants and Their Health Effects in Sampled Groundwater Around Ilorin Metropolis

Received: 06 March 2020    Accepted: 23 March 2020    Published: 30 April 2020
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Abstract

The study was aimed at determining the possible volatile organic compounds present in groundwater from hand-dug wells within and around filling stations across Ilorin metropolis as well as to ascertain the possible sources of the contaminants and their health effects. Water samples were obtained from twenty-six (26) wells that were found within the scope of stations above the age of 15 years and functioning with underground storage tank capacities of over 33,000 L each for different petroleum products stored above the water level. Laboratory analysis to determine volatile organic compounds and their concentrations were carried out using the gas chromatography- mass spectrophotometer (GC-MS) after prior extraction of hydrocarbon from the water samples by the Liquid-Liquid Extraction (LLE) method. The result revealed a total of fifty-three (53) VOCs across samples where nonanal, dodecane, methyl palmitate, heptanophenone, 13, hexyloxacyclotridec – 10 – en – 2 – one, cyclohexane, octyl, decahydro- 4, 4, 8, 9, 10 – pentamethyl naphthalene, (z) – 3 – heptene, were the most frequently occurring compounds, which could be traced to anthropogenic activities involving the use of paints, detergents, stain removers, leaking underground storage tanks, piped networks containing petroleum products as the possible sources of release into the environmental media. Related health impacts from exposure to these contaminants includes brain damage, cancer, tumours, anaemia, central and peripheral nervous system breakdown, liver, bones, autism, Skin, eye, and nose irritation, headache, dizziness, narcosis, and death at high levels of exposure. The study concluded that groundwater sources at close proximity to filling stations are susceptible to contamination through activities in the stations and such water resource should be treated before consumption and use to avoid negative health effects.

DOI 10.11648/j.ijepp.20200802.11
Published in International Journal of Environmental Protection and Policy (Volume 8, Issue 2, March 2020)
Page(s) 36-43
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2024. Published by Science Publishing Group

Keywords

Volatile Organic Compounds, Groundwater, Filling Stations, Ilorin Metropolis, Health Impact

References
[1] Odipe, O., Lawal, A., Adio, Z., Karani, G., & Sawyerr, H. (2018). GIS-Based Location Analyse of Retail Petrol Stations in Ilorin, Kwara State, Nigeria. International Journal of Scientific & Engineering Research, 9 (12), 790–794.
[2] FGN. (2007). Legal Notice on Publication of the 2006 Census Report. Federal Government of Nigeria official Gazette, 4 (94), 1-8.
[3] Club, S. (2011). Leaking underground storage tanks: A threat to public health & environment. San Francisco.
[4] Rockett, L., Gee, R., Aldous, E., Benson, V., Brandon, Y., Briere, B.,... & Watts, C. (2014). Volatile organic compounds—Understanding the risks to drinking water. Toxicology Letters, (229), S127.
[5] Adelana, S. M. A; Olasehinde, P. I; Bale, R. B; Vrbka, P; Goni, I. B and Edet, A. E. (2008). An overview of the geology and hydrogeology of Nigeria. In: (Adelana SMA and MacDonald AM eds.). Applied Groundwater Studies in Africa. IAH Selected Papers on Hydrogeology, Volume 13: 171-197, CRC Press/Balkema, London.
[6] Obaje, N. G. (2009). Geology and mineral resources of Nigeria (Vol. 120). Springer.
[7] Olorunfemi, M. O., Fatoba, J. O., & Ademilua, L. O. (2005). Integrated VLF-electromagnetic and electrical resistivity survey for groundwater in a crystalline basement complex terrain of Southwest Nigeria. Global Journal of Geological Sciences, 3 (1), 71-80.
[8] Oyegun, R. O. (1983). Water Resources in Kwara State. Matanmi and Sons printing and publishing Co. Ltd. Ilorin.
[9] Ajadi, B. S., Adaramola, M. A., Adeniyi, A., & Abubakar, M. I. (2016). Effect of effluents discharge on public health in Ilorin Metropolis, Nigeria. Ethiopian Journal of Environmental Studies and Management, 9 (4), 389-404.
[10] Iroye, K. A. (2017). Correlating pattern of river discharge with degree of urbanization in sub-catchments of River Asa in Ilorin, Nigeria. Ethiopian Journal of Environmental Studies and Management, 10 (2), 251-261.
[11] U.S. Environmental Protection Agency (US EPA) (2005) Reregistration eligibility decision (RED) for 1,2-benzisothiazoline-3-one. http://www.epa.gov/oppsrrd1/REDs/benzisothiazolin_red.pdf.
[12] PubChem, (2019a). National Center for Biotechnology Information. PubChem Database. Nonanal, CID=31289, https://pubchem.ncbi.nlm.nih.gov/compound/Nonanal (accessed on Nov. 11, 2019).
[13] Bingham, E., Cohrssen, B., & Powell, C. H. (2001). Patty's toxicology. Volume 2: toxicological issues related to metals, neurotoxicology and radiation metals and metal compounds (No. Ed. 5). John Wiley and Sons.
[14] Verschueren, K. (2001). Handbook of environmental data on organic chemicals: Vol. 1 (No. Ed. 4). John Wiley and Sons, Inc.
[15] Alvarez-Rivera, G., Lores, M., Llompart, M., & Garcia-Jares, C. (2013). Cosmetics and toiletries: chromatography.
[16] Lewis, R. J., Jr (1993) Hawley’s Condensed Chemical Dictionary, 12th Ed., New York, Van Nos-trand Reinhold, p. 1217.
[17] PubChem, (2016). National Center for Biotechnology Information. PubChem Database. Linalool, CID=6549, https://pubchem.ncbi.nlm.nih.gov/compound/Linalool (accessed on Nov. 12, 2019).
[18] HMPC, (2005). Committee on Herbal Medicinal Products. Final Public Statement on the Use of Herbal Medicinal Products Containing Estragole. http://www.ema.europa.eu/docs/en_GB/document_library/Scientific_guideline/2010/04/WC500089960.pdf.
[19] World Health Organization (WHO). (2015). Exposure to Benzene: A Major Public Health Concern. WHO Document Production Services.
[20] Yehye, Wageeh A.; Rahman, Noorsaadah Abdul; Ariffin, Azhar; Abd Hamid, Sharifah Bee; Alhadi, Abeer A.; Kadir, Farkaad A.; Yaeghoobi, Marzieh (2015). "Understanding the chemistry behind the antioxidant activities of butylated hydroxytoluene (BHT): A review". European Journal of Medicinal Chemistry. 101: 295–312. doi: 10.1016/j.ejmech.2015.06.026. PMID 26150290.
[21] Isaacs, K. K., Glen, W. G., Egeghy, P., Goldsmith, M. R., Smith, L., Vallero, D.,... & Özkaynak, H. (2014). SHEDS-HT: an integrated probabilistic exposure model for prioritizing exposures to chemicals with near-field and dietary sources. Environmental science & technology, 48 (21), 12750-12759.
[22] Kraft, P., & Fráter, G. (2001). Enantioselectivity of the musk odor sensation. Chirality, 13 (8), 388-394.
[23] EPA, (2019b). Chemical Data Reporting under the Toxic Substances Control Act. Website: https://www.epa.gov/chemicals-under-tsca.
[24] EPA/ N. P. F. S. P. (2007). United States Environmental Protection Agency: Prevention, Pesticides And Toxic Substances., Washinton, pp.
[25] ACGIH (2008). Documentation of the Threshold Limit Values and Biological Exposure Indices. 7th ed. Cincinnati, OH: American Conference of Governmental Industrial Hygienists, 2008.
[26] HSDB. (2015). “National Library of Medicine Hazardous Substances Data Bank (HSDB).” 2015. http://toxnet.nlm.nih.gov/newtoxnet/hsdb.htm.
[27] HSDB, (2016). National Library of Medicine Hazardous Substances Data Bank. Available from, as of Nov 23, 2016: http://toxnet.nlm.nih.gov/newtoxnet/hsdb.htm.
[28] Kaur-Knudsen, D., Menné, T., & Christina Carlsen, B. (2012). Systemic allergic dermatitis following airborne exposure to 1, 2-benzisothiazolin-3-one. Contact dermatitis, 67 (5), 310-312.
[29] TOXNET, (2015). Toxicology Data Network, Fact Sheet, 1,2-Benzisothiazoline-3-one National Library of Medicine. Website: https://toxnet.nlm.nih.gov/cgi-bin/sis/search/a?dbs+hsdb:@term+@DOCNO+8271.
[30] Forschungsgemeinschaft, D. (2015). List of Substances. List of MAK and BAT Values 2015: Permanent Senate Commission for the Investigation of Health Hazards of Chemical Compounds in the Work Area, 19-162.
[31] James, S. J., Cutler, P., Melnyk, S., Jernigan, S., Janak, L., Gaylor, D. W., & Neubrander, J. A. (2004). Metabolic biomarkers of increased oxidative stress and impaired methylation capacity in children with autism. The American journal of clinical nutrition, 80 (6), 1611-1617.
[32] Francavilla, R., Ercolini, D., Piccolo, M., Vannini, L., Siragusa, S., De Filippis, F.,... & Serrazanetti, D. I. (2014). Salivary microbiota and metabolome associated with celiac disease. Appl. Environ. Microbiol., 80 (11), 3416-3425.
[33] Azario, I., Pievani, A., Del Priore, F., Antolini, L., Santi, L., Corsi, A.,... & Bernardo, M. E. (2017). Neonatal umbilical cord blood transplantation halts skeletal disease progression in the murine model of MPS-I. Scientific reports, 7 (1), 9473.
[34] Yang, J. H., Lee, C. H., Monteiro-Riviere, N. A., Riviere, J. E., Tsang, C. L., & Chou, C. C. (2006). Toxicity of jet fuel aliphatic and aromatic hydrocarbon mixtures on human epidermal keratinocytes: evaluation based on in vitro cytotoxicity and interleukin-8 release. Archives of toxicology, 80 (8), 508-523.
[35] Koniecki, D., Wang, R., Moody, R. P., & Zhu, J. (2011). Phthalates in cosmetic and personal care products: concentrations and possible dermal exposure. Environmental research, 111 (3), 329-336.
[36] European Chemicals Agency (ECHA) (2015a). European Chemicals Agency (ECHA) and data classification and on 2-Nitro-4-(trifluoromethyl) phenol. Website: https://echa.europa.eu/information-on-chemicals/cl-inventory-database/-/discli/details/97711.
[37] UNECE (2017). About the GHS, Globally Harmonized System of Classification and Labelling of Chemicals (GHS). Available online: https://www.unece.org/trans/danger/publi/ghs/ghs_welcome_e.html.
[38] European Chemicals Agency (ECHA) (2015b). European Chemicals Agency (ECHA) and data classification and on azidobenzene. Website: https://echa.europa.eu/information-on-chemicals/cl-inventory-database/-/discli/details/134767.
[39] Wang, W., & Kannan, K. (2019). Quantitative identification of and exposure to synthetic phenolic antioxidants, including butylated hydroxytoluene, in urine. Environment international, 128, 24-29.
[40] European Chemicals Agency (ECHA) (2015c). European Chemicals Agency (ECHA) and data classification and on 1,2 - Bis (trimethylsilyl) benzene. Website: https://echa.europa.eu/information-on-chemicals/cl-inventory-database/-/discli/details/191884.
[41] Imamura, Y., Narumi, R., & Shimada, H. (2007). Inhibition of carbonyl reductase activity in pig heart by alkyl phenyl ketones. Journal of enzyme inhibition and medicinal chemistry, 22 (1), 105-109.
[42] Pieprzyca, E., Skowronek, R., Korczyńska, M., Kulikowska, J., & Chowaniec, M. (2018). A two fatal cases of poisoning involving new cathinone derivative PV8. Legal Medicine, 33, 42-47.
[43] European Chemicals Agency (ECHA) (2015d). European Chemicals Agency (ECHA) and data classification and on trans-2-Decenoic acid. Website: https://echa.europa.eu/information-on-chemicals/cl-inventory-database/-/discli/details/37727.
[44] European Chemicals Agency (ECHA) (2015e). European Chemicals Agency (ECHA) and data classification and on 1-[4-tert,-butyl] phenyl]-2(4-bluidino)-1-ethanone. Website: https://echa.europa.eu/information-on-chemicals/cl-inventory-database/-/discli/details/46162.
[45] EPA, (2019). Chemical Data Reporting under the Toxic Substances Control Act. Website: https://www.epa.gov/chemicals-under-tsca.
[46] National Toxicology Program. Institute of Environmental Health Sciences, National Institutes of Health (NTP). 1992. National Toxicology Program Chemical Repository Database. Research Triangle Park, North Carolina: NTP via httn.canieochemicals.noaa.gov/chemical/20568.
[47] Guidebook (2004). A guidebook for first responders during the initial phase of a dangerous goods/hazardous materials transportation incident. US Department of Transportation, Transport Canada, and the Secretariat of Communications and Transportation Mexico. Washington, DC, USA.
[48] National Toxicology Program (2014). Testing Status of Agents at NTP. Available from, as of Jul 31, 2014: http://ntp.niehs.nih.gov/.
[49] USEPA/IRIS (2015) Integrated Risk Information System. Available from, as of Jul 31, 2014: http://www.epa.gov/iris/.
[50] European Chemicals Agency (ECHA) (2015f). European Chemicals Agency (ECHA) and data classification and on Tetrasiloxane decamethyl. Website: https://echa.europa.eu/information-on-chemicals/cl-inventory-database/-/discli/details/46796.
[51] ATSDR (2016). Tox Profiles. Total Petroleum Hydrocarbons. Available from, as of Nov 23, 2016: http://www.atsdr.cdc.gov/toxprofiles/index.asp.
Author Information
  • Department of Environmental Health Sciences, School of Allied Health and Environmental Science, College of Pure and Applied Science, Kwara State University, Malete, Nigeria

  • Department of Environmental Health Sciences, School of Allied Health and Environmental Science, College of Pure and Applied Science, Kwara State University, Malete, Nigeria

  • Department of Pure and Applied Biology, Faculty of Pure and Applied Science, Ladoke Akintola University of Technology, Ogbomosho, Nigeria

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  • APA Style

    Oluwaseun Emmanuel Odipe, Henry Olawale Sawyerr, Solomon Olayinka Adewoye. (2020). Characterized Organic Pollutants and Their Health Effects in Sampled Groundwater Around Ilorin Metropolis. International Journal of Environmental Protection and Policy, 8(2), 36-43. https://doi.org/10.11648/j.ijepp.20200802.11

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    ACS Style

    Oluwaseun Emmanuel Odipe; Henry Olawale Sawyerr; Solomon Olayinka Adewoye. Characterized Organic Pollutants and Their Health Effects in Sampled Groundwater Around Ilorin Metropolis. Int. J. Environ. Prot. Policy 2020, 8(2), 36-43. doi: 10.11648/j.ijepp.20200802.11

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    AMA Style

    Oluwaseun Emmanuel Odipe, Henry Olawale Sawyerr, Solomon Olayinka Adewoye. Characterized Organic Pollutants and Their Health Effects in Sampled Groundwater Around Ilorin Metropolis. Int J Environ Prot Policy. 2020;8(2):36-43. doi: 10.11648/j.ijepp.20200802.11

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  • @article{10.11648/j.ijepp.20200802.11,
      author = {Oluwaseun Emmanuel Odipe and Henry Olawale Sawyerr and Solomon Olayinka Adewoye},
      title = {Characterized Organic Pollutants and Their Health Effects in Sampled Groundwater Around Ilorin Metropolis},
      journal = {International Journal of Environmental Protection and Policy},
      volume = {8},
      number = {2},
      pages = {36-43},
      doi = {10.11648/j.ijepp.20200802.11},
      url = {https://doi.org/10.11648/j.ijepp.20200802.11},
      eprint = {https://download.sciencepg.com/pdf/10.11648.j.ijepp.20200802.11},
      abstract = {The study was aimed at determining the possible volatile organic compounds present in groundwater from hand-dug wells within and around filling stations across Ilorin metropolis as well as to ascertain the possible sources of the contaminants and their health effects. Water samples were obtained from twenty-six (26) wells that were found within the scope of stations above the age of 15 years and functioning with underground storage tank capacities of over 33,000 L each for different petroleum products stored above the water level. Laboratory analysis to determine volatile organic compounds and their concentrations were carried out using the gas chromatography- mass spectrophotometer (GC-MS) after prior extraction of hydrocarbon from the water samples by the Liquid-Liquid Extraction (LLE) method. The result revealed a total of fifty-three (53) VOCs across samples where nonanal, dodecane, methyl palmitate, heptanophenone, 13, hexyloxacyclotridec – 10 – en – 2 – one, cyclohexane, octyl, decahydro- 4, 4, 8, 9, 10 – pentamethyl naphthalene, (z) – 3 – heptene, were the most frequently occurring compounds, which could be traced to anthropogenic activities involving the use of paints, detergents, stain removers, leaking underground storage tanks, piped networks containing petroleum products as the possible sources of release into the environmental media. Related health impacts from exposure to these contaminants includes brain damage, cancer, tumours, anaemia, central and peripheral nervous system breakdown, liver, bones, autism, Skin, eye, and nose irritation, headache, dizziness, narcosis, and death at high levels of exposure. The study concluded that groundwater sources at close proximity to filling stations are susceptible to contamination through activities in the stations and such water resource should be treated before consumption and use to avoid negative health effects.},
     year = {2020}
    }
    

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  • TY  - JOUR
    T1  - Characterized Organic Pollutants and Their Health Effects in Sampled Groundwater Around Ilorin Metropolis
    AU  - Oluwaseun Emmanuel Odipe
    AU  - Henry Olawale Sawyerr
    AU  - Solomon Olayinka Adewoye
    Y1  - 2020/04/30
    PY  - 2020
    N1  - https://doi.org/10.11648/j.ijepp.20200802.11
    DO  - 10.11648/j.ijepp.20200802.11
    T2  - International Journal of Environmental Protection and Policy
    JF  - International Journal of Environmental Protection and Policy
    JO  - International Journal of Environmental Protection and Policy
    SP  - 36
    EP  - 43
    PB  - Science Publishing Group
    SN  - 2330-7536
    UR  - https://doi.org/10.11648/j.ijepp.20200802.11
    AB  - The study was aimed at determining the possible volatile organic compounds present in groundwater from hand-dug wells within and around filling stations across Ilorin metropolis as well as to ascertain the possible sources of the contaminants and their health effects. Water samples were obtained from twenty-six (26) wells that were found within the scope of stations above the age of 15 years and functioning with underground storage tank capacities of over 33,000 L each for different petroleum products stored above the water level. Laboratory analysis to determine volatile organic compounds and their concentrations were carried out using the gas chromatography- mass spectrophotometer (GC-MS) after prior extraction of hydrocarbon from the water samples by the Liquid-Liquid Extraction (LLE) method. The result revealed a total of fifty-three (53) VOCs across samples where nonanal, dodecane, methyl palmitate, heptanophenone, 13, hexyloxacyclotridec – 10 – en – 2 – one, cyclohexane, octyl, decahydro- 4, 4, 8, 9, 10 – pentamethyl naphthalene, (z) – 3 – heptene, were the most frequently occurring compounds, which could be traced to anthropogenic activities involving the use of paints, detergents, stain removers, leaking underground storage tanks, piped networks containing petroleum products as the possible sources of release into the environmental media. Related health impacts from exposure to these contaminants includes brain damage, cancer, tumours, anaemia, central and peripheral nervous system breakdown, liver, bones, autism, Skin, eye, and nose irritation, headache, dizziness, narcosis, and death at high levels of exposure. The study concluded that groundwater sources at close proximity to filling stations are susceptible to contamination through activities in the stations and such water resource should be treated before consumption and use to avoid negative health effects.
    VL  - 8
    IS  - 2
    ER  - 

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