Concentrations of Organochlorine Pesticide (OCP) Residues in Environmental and Biota Samples from Azuabie and Okujagu Creeks, Upper Bonny Estuary, Nigeria

Authors

  • C.M. Okolocha
  • I.K.E. Ekweozor
  • E.R. Daka
  • M. Moslen

Keywords:

Upper Bonny Estuary, Carcinogenic, DDT, Aldrin, Food Safety

Abstract

This study evaluated the concentrations of organochlorine pesticides (OCPs) in surface water, sediment and biota (Oysters and Periwinkle) between August 2023 and June 2024. Samples were collected bimonthly from four stations located in Azuabie creek (AZ1 and AZ 2) and Okujagu Creek (OK 1 and OK2). Analysis for OCPs was accomplished using liquid-liquid extraction gas chromatographic method 1 (LL-EGC). Descriptive statistics, analysis of variance and correlation analysis were used for statistical analysis of the results. OCP values in surface water (Azuabie: 1.67±0.36 – 3,252.98±1,536.73ppb; Okujagu: 0.99±0.51 – 1,300.54±295.23ppb) did not differ significantly by location but were significant by time. OCP in sediment (Azuabie: 9.56±3.03 – 3,252.98±1,536.73ppb; Okujagu: 8.24±0.57 – 1,300.54±295.23ppb) varied significantly both by location and time. OCP values in both oysters (Azuabie: 10.36±4.34 – 882.79±232.34ppb; Okujagu: 8.69±0.54 – 971.91±94.03ppb) and periwinkles (Azuabie: 21.30±3.07 – 1.091.52±282.69ppb; Okujagu: 20.96±1.52 – 1,287.65±204.25ppb) were not significant by location but varied significantly by time. At Azuabie, there were significant correlations between the OCP concentrations in sediment and surface water; there were also significant correlations between sediment and Oyster and Periwinkle.  At Okujagu, significant correlations were observed between the OCP concentrations in sediment and surface water, oyster and surface water, periwinkle and surface water, sediment and oyster, and periwinkle and oyster. The constituents recorded included Alpha-BHC, Beta-BHC, Gamma-BHC, Heptachlor, Delta-BHC, Aldrin, Heptachlor Epoxide, Alpha-Chlordane, Gamma-Chlordane, Endosulfan I, Endosulfan II, P,p’-DDE, P,p’-DDD, P,p’-DDT, Dieldrin, Endrin, Endrin Aldehyde, Endosulfan Sulfate, Methoxychlor and Endrin Ketone. The dermal hazard quotient for DDT, aldrin, alpha-chlordane and penta-chlorobenzene showed that the average values obtained were not carcinogenic (0.1ppm). Most of the individual OCP such as Alpha-BHC, Beta-BHC, Endrin, Endrin-aldehyde etc had values that exceeded the USEPA and WHO acceptable limits. This is of public health concern due to the bioaccumulation potential of the biota which are regularly consumed by the public. Preventive measures should therefore be taken to prevent continued pollution while aiding the recovery of both creeks. Measures should also be taken to ensure food safety among the population. In conclusion, the result for the toxicity limit for OCP ranged between 0.1 to 0.2 ppm which is within Occupational regulation government permissible limit of 0.1ppm and for PAH, it ranged between 1.7 to 5.1ppm which is also within OSHA limit of 0.02-6.68ppm. However, there is need for constant check and control so as to reduce it and ensure it does not exceed this limit .

Author Biographies

  • C.M. Okolocha

    Port Harcourt, 500102, Nigeria

  • I.K.E. Ekweozor

    Rivers State University, 500101, Nigeria

  • E.R. Daka

    Rivers State University, 500101, Nigeria

  • M. Moslen

    Rivers State University, 500101, Nigeria

References

[1]. C. Olisah, O. O. Okoh and A.I. Okoh. “Occurrence of organochlorine pesticide residues in biological and environmental matrices in Africa: A two-decade review”. Heliyon, vol. 6, e03518, Mar. 2020.

[2]. B. Gevao, P.B. Kurt-Karakus, A. Birgul, K. Martinez-Guijarro, C. Sukhn, D. Krishnan, S, Rajagopalan, M. Hajeyah, M. Bahloul, H. Alshemmari and M.I. Orif. “Ambient air concentrations and risk assessment of selected organochlorine pesticides (OCPs) across five Middle Eastern countries”. Journal of Environmental Exposure Assessment, vol. 1, http://dx.doi.org/10.20517/jeea.2022.05, May 2022.

[3]. J.N. Nuntah, O.J. Abolagba, J.O. Igene, S.F. Usifoh, C.E. Omoti and C.O. Usifoh. “Organochlorine pesticide concentrations in selected rivers in South-West Nigeria”. South Asian Research Journal of Agriculture and Fisheries, vol. 2, pp. 74-78, Jun. 2020.

[4]. A. Abba, Y. Ibrahim, J. Yakubu, A.J. Maina and J.C. Akan. “Assessment of organochlorine pesticide residues in water and sediment in selected areas of River Kaduna, Kaduna State, Nigeria”. Journal of Chemical Technology, vol. 1, pp. 126-133, Sep. 2025.

[5]. American Public Health Association (APHA). Standard Methods for the Examination of Water and Wastewater (19th ed.). Washington, D.C.: American Public Health Association Inc., 1995, pp. 117-118.

[6]. A.A Okunola, A. Adekunle, K. Xijun, L. Bin, Z. Yuling and H. Xia. “Comparative evaluation of environmental contamination by electronic wastes in Nigeria and China”. Science of the Total Environment, vol. 423, pp. 62-72, Mar. 2012.

[7]. United States Environmental Protection Agency (USEPA). Risk Assessment Guidance for Superfund Volume I: Human Health Evaluation Manual (Part E, Supplemental Guidance for Dermal Risk Assessment). Washington, DC: U.S. Environmental Protection Agency, 2004, pp. A1-E2.

[8]. K. Oginawati, S.H. Susetyo, S.I. Rahmawati, S.B. Kurniawan and S.R.S. Abdullah. “Distribution of organochlorine pesticide pollution in water, sediment, mollusk, and fish at Saguling Dam, West Java, Indonesia”. Toxicological Research, vol. 38, pp. 149-157, Mar. 2021.

[9]. United States Environmental Protection Agency (USEPA). National Primary Drinking Water Regulations. 2015, pp. 550–560. Available online: https://www.epa.gov/sites/production/files/2015-11/documents.

[10]. European Commission. Commission Regulation (EU) 2020/585 of 29 April 2020 amending Regulation (EC) No 396/2005 of the European Parliament and of the Council as regards maximum residue levels for chlorpyrifos and chlorpyrifos-methyl in or on certain products. Official Journal of the European Union 2020 L 135/3.

[11]. World Health Organization (WHO). Protecting groundwater for health: managing the quality of drinking-water sources. Geneva: World Health Organization, 2006.

[12]. A.H. Santuraki, Z. Abdu, A.U. Babayo and A.G. Abdulkadira. “Concentration and Human Health Risk Assessment of Dichlorodiphenyltrichloroethane in Two Species of Fish Muscle from River Gongola Basin and its Dam, Dadinkowa, Gombe State, Nigeria”. Journal of Applied Science and Environmental Management, vol. 26, pp. 1909-1914, Dec. 2022.

[13]. C.M. Okolocha. “Evaluation of persistent organic pollutants in sediment and biota obtained from Azuabie and Okujagu Creeks in the Upper Bonny Estuary, Nigeria”. MSc, Rivers State University, Port Harcourt, 2018.

[14]. T. Krithiga, S. Sathish, A.A. Renita, D. Prabu, S. Lokesh, R. Geetha, S.K.R. Namasivayam and M. Sillanpaa. “Persistent organic pollutants in water resources: Fate, occurrence, characterization and risk analysis”. Science of The Total Environment, vol. 831, 154808, Mar. 2022.

[15]. R. Alani, A. Lawal, S. Awonuga and B. Alo. “Distribution of Organochlorine Pesticide Residues in Surface Water and Sediments of Ogun River at Kara Abattoir, Ogun State, Nigeria”. Nigerian Journal of Environmental Sciences and Technology, vol. 6, pp. 270-282, Mar. 2022.

[16]. G.D. Gasperina. “Environmental decay and the illegal market in e-waste from a European perspective: current problems and future directions”. Revista Catalana De Dret Ambiental, vol. I, pp. 1 – 54, Nov. 2010.

[17]. J.B. Puckett., S. Westervelt, R. Guitierrez and Y. Takamiya. The Digital Dump Exporting Re-use and Abuse to Africa. The Basel Action Network, pp. 1- 43, 2005.

[18]. P. Baumard, H. Budzinski and P. Garriques. “Polycyclic Aromatic Hydrocarbons in Sediment and Mussels of the Western Mediterranean Sea”. Environmental Toxicology and Chemistry, vol. 17, pp.765-776, Nov. 1998.

[19]. P. Baumard, H. Budzinski, P. Garrigues, H. Dizer and P.D. Hansen. “Polycyclic aromatic hydrocarbons in recent sediments and mussels (Mytilus edulis) from the Western Baltic Sea: occurrence, bioavailability and seasonal variations”. Marine Environmental Research, vol. 47, pp. 17-47, Feb. 1999.

[20]. B.G. Onwumere and A.A. Oladimeji. “Accumulation of metals and histopathology in Oreochromis niloticus exposed to treated NNPC Kaduna (Nigeria) petroleum refinery effluent”. Ecotoxicology and Environmental Safety, vol. 19, pp. 123-134, Apr. 1990.

[21]. O.O. Ezomoh, F.M. Bigbo, E. Loveday and E. Wodu. “Vitamin and mineral contents in shrimps, oysters and periwinkles harvested from Brass Local Government Area in Bayelsa State, Nigeria”. EAS Journal of Nutrition and Food Sciences, vol. 4, pp. 123-127, Nov. 2022.

[22]. N.R. Ekere, N.M. Yakubu, T. Oparanozie and J.N. Ihedioha. “Levels and risk assessment of polycyclic aromatic hydrocarbons in water and fish of Rivers Niger and Benue confluence Lokoja, Nigeria”. Journal of Environmental Health Science and Engineering, vol. 17, pp. 383-392, Feb. 2019.

[23]. O.E. Akinrinade, F.O. Agunbiade, R. Alani and O.O. Ayejuyo. “Implementation of the Stockholm Convention on persistent organic pollutants (POPs) in Africa–progress, challenges, and recommendations after 20 years”. Environmental Science: Advances, vol. 3, pp. 623-634, Feb. 2024.

[24]. A.U. Dewa, J. Nelson and S.A. Olawale. “Distribution and Risk Assessment of Aldrin, Endrin, Heptachlor, and Heptachlor Epoxide in Some Villages in Hawul River Basin”. International Journal of Ground Sediment and Water, vol. 22, pp. 1795-1813, Apr. 2025.

[25]. G.E. Odesa and D.U. Olannye. Health risk assessment of PAHs and heavy metal levels in periwinkles (Pachymelania fusca mutans) and crabs (Scylla serrata) consumed in crude oil-contaminated coastal regions of Southern Nigeria. Toxicology Reports, vol. 14, 101852, Jan. 2025.

[26]. D.C. Firth, P.E. Strydom, L. Auerswald and L.C. Hoffman. “A Human Health Risk Assessment of Persistent Organic Pollutants in Wild Marine Mussels from the Western Cape Province of South Africa”. Foods, vol. 14, 2226, Jun. 2025.

[27]. S. Cui, Q. Fu, T. Li, W. Ma, D. Liu and M. Wang. “Sediment-Water Exchange, Spatial Variations, and Ecological Risk Assessment of Polycyclic Aromatic Hydrocarbons (PAHs) in the Songhua River, China”. Water, vol. 8, pp. 1-13, Aug. 2016.

[28]. E.Q. Umudi, E.K. Obruche, M.I. Sani, G.C. Onwugbuta, I.S. Aghemwenhio, S.C. Ikechukwu, P.D. Clark, A.G. Essiet, O.I. Eresanya, M.C. Ibe and A. Hashimu. “Evaluation of Polycyclic Aromatic Hydrocarbons (PAHs) Contents of Fishes, Waters and Sediments of River Niger: Human Health Risk Assessment”. Journal of Basic and Applied Science Research, vol. 3, pp. 187-199, Oct. 2025.

[29]. M. Moslen and A. Aigberua. |Heavy Metals and Hydrocarbon Contamination of Surface water in Azuabie Creek within Bonny Estuary, Nigeria”. Journal of Applied Science and Environmental Management, vol. 22, pp. 1083-1088, Aug. 2018.

[30]. K. Ajekwene, E. Aigbokhan, O. Akindele, M.E. Yibowei, F.P. Momoh and U.K Ugonna. “Electronic waste (e-waste): sources, proliferation, effects & management in developing nations”. IOSR Journal of Engineering, 12, 12-27, Jan. 2022.

[31]. P.J. Berríos-Rolón, M.C. Cotto and F. Márquez. “Polycyclic Aromatic Hydrocarbons (PAHs) in Freshwater Systems: A Comprehensive Review of Sources, Distribution, and Ecotoxicological Impacts”. Toxics, 13(4), 321, Apr. 2025.

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Published

2026-07-29

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How to Cite

C.M. Okolocha, I.K.E. Ekweozor, E.R. Daka, & M. Moslen. (2026). Concentrations of Organochlorine Pesticide (OCP) Residues in Environmental and Biota Samples from Azuabie and Okujagu Creeks, Upper Bonny Estuary, Nigeria. International Journal of Sciences: Basic and Applied Research (IJSBAR), 79(1), 274-289. https://gssrr.org/JournalOfBasicAndApplied/article/view/17802