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Concentrations and Human Health Risk Assessment of Cd, Co, Cr, Ni, and Pb via Eating White Granulated Garri Produced in Nigeria

Received: 6 October 2019     Accepted: 6 November 2019     Published: 6 July 2020
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Abstract

White granulated garri, an extensively consumed foodstuff in Nigeria made from fermented cassava tubers has recorded little studies on its heavy metals content. The concentrations of Cd, Co, Cr, Ni and Pb in commercial white granulated garri commonly sold in three major markets in Port Harcourt, Nigeria were established using Inductively Coupled Plasma - Mass Spectrometry (ICP-MS) after microwave-assisted acid digestion. The mean concentrations (x ̅±SD,in mg/kg on dry-weight basis) of heavy metals in garri samples were Cd: 0.021 ± 0.005, Co: 0.027 ± 0.004, Cr: 2.50 ± 0.047, Ni: 0.849 ± 0.021, and Pb: 0.522 ± 0.039 respectively. A food frequency questionnaire-based (FFQ) survey on dietary consumption rates of garri as a source of carbohydrate among consumers and marketers showed that garri accounted for ˃ 97.5% of total carbohydrate consumed in Nigeria. Statistical evaluation of the data by one-way analysis of variance discloses noteworthy differences of metal contents for Cd, Co, Ni and Pb in garri from the study area with the exception of Cr. The mean daily intake of metals (mg/person/day) from garri consumption using dietary modelling was found to be Cd: 1.49 x 10-4, Co: 1.34 x 10-5, Cr: 1.24 x 10-2, Ni: 4.23 x 10-3 and Pb: 2.60 x 10-3 respectively. These values are lower than the upper tolerable daily intake limits for heavy metals in food. The target hazard quotients (THQ), health risk index (HRI) and lifetime cancer risk (CR) for Cd, Co, Cr, Ni, and Pb indicate that, the probable human health risk associated with consumption of garri for the target population is moderately low at the moment. However, modest consumption rate of the product is recommended due to potential bioaccumulation of heavy metals found in garri.

Published in American Journal of Environmental Protection (Volume 9, Issue 4)
DOI 10.11648/j.ajep.20200904.11
Page(s) 77-85
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), 2020. Published by Science Publishing Group

Keywords

Garri, Heavy Metals, Cassava, Health Risk Assessment

References
[1] FAO (Food and Agriculture Organization) (2002). FAOSTAT Statistics Database. Available at: http://aps.fao.org [Accessed 2012].
[2] Ecocrop, (2011). Ecocrop database. FAO.
[3] Lebot, V., (2009). Tropical root and tuber crops: cassava, sweet potato, yams and aroids. Crop production science in horticulture (17), CAB books, CABI, Wallingford, UK.
[4] Wilberforce, J. and Oti, O (2015). Heavy Metal Accumulation in Tubers Grown in a Lead-zinc Derelict Mine and their Significance to Health and Phytoremediation. American Chemical Science Journal 8 (3): 1-9, 2015.
[5] Rakhshaee, R: M. Giahi, and A. Pourahmad, “Studying effect of cell wall's carboxyl-carboxylate ratio change of Lemna minor to remove heavy metals from aqueous solution,” Journal of Hazardous Materials, 163, (1). 165–173, 2009.
[6] Cho-Ruk, K; J. Kurukote, P. Supprung, and S. Vetayasuporn, “Perennial plants in the phytoremediation of lead-contaminated soils,” Biotechnology, 5, (1). 1–4, 2006.
[7] Orisakwe, Orish Ebere, Nduka, John Kanayochukwu and Amadi Cecilia Nwadiuto (2012). Heavy metals risk assessment for population via consumption of food crops and fruits in Owerri, South Eastern Nigeria. Chemistry Central Journal 6: 77, 1-7.
[8] Horsfall, M. (2011). Chemistry and Heavy Metals are Janus-faced. 81st Inaugural Lecture, University of Port Harcourt, Nigeria.
[9] Sharma, R. K; M. Agrawal, F. M. Marshall, Heavy metals in vegetables collected from production and market sites of a tropical urban area of India, Food Chem. Toxicol. 47 (2009) 583–591.
[10] Zeng-Yei, H (2004). Evaluating heavy metal contents in nine composts using four digestion methods. Bioresource Technology, 95 (2004) 53-59.
[11] Fernanda C. Bressy, Geysa B. Brito, Isa S. Barbosa, Leonardo S. G. Teixeira, Maria Graças A. Korn (2013). Determination of trace element concentrations in tomato samples at different stages of maturation by ICP OES and ICP-MS following microwave-assisted digestion. Microchemical Journal 109 (2013) 145–149.
[12] USEPA, 2011. Risked – based concentration table. United States Environmental Protection Agency, Washington, DC.
[13] Joseph O. Osakwe, Pereware Adowei and Michael Horsfall Jnr (2014). Evaluation of Heavy Metal Species in Bottom Sediments from Imo River System, Southeastern Nigeria. Res. J. Chem. Sci. 4 (6), 1-6,
[14] Adeel Mahmood and Riffat Naseem Malik (2014). Human health risk assessment of heavy metals via consumption of contaminated vegetables collected from different irrigation sources in Lahore, Pakistan. Arabian Journal of Chemistry 7, 91–99.
[15] Shin, Mee-Young; Cho, Young-Eun; Park, Chana; Sohn, Ho-Yong; Lim, Jae-Hwan and Kwun, In-Sook (2013). The contents of heavy metals (Cd, Cr, As, Pb, Ni and Sn) in the selected commercial yam powder products in South Korea. Prev. Nutr. Food. Sci. 8 (4) 249-255.
[16] Divya, L, Jessen George and Midhun G (2015). Heavy Metal Contamination of Some Common Tubers Sold in Local Markets of Ernakulam District, Kerala, India. International Research Journal of Biological Sciences. Vol. 4 (3), 49-52, March (2015) Int. Res. J. Biological Sci.
[17] Chauhan, G and Chauhan, U. K (2014). Human health risk assessment of heavy metals via dietary intake of vegetables grown in wastewater irrigated area of Rewa, India. International Journal of Scientific and Research Publications 4 (9) 1-9.
[18] USEPA (US Environmental Protection Agency) (2010). Exposure Factors Handbook – General Factors. EPA/600/P-95/002Fa, vol. I. Office of Research and Development. National Center for Environmental Assessment. US Environmental Protection Agency. Wahington, DC.
[19] Food and Agricultural Organization (FAO) (2000). The places of Agriculture in Sustainable Development: the way forward on SARD. Committee on Agriculture, Sixteenth Session, Item 7 of the provisional Agenda, Rome, 26-30 March, 2000.
[20] NIFDS, 2006. The EU standard for concentration of heavy metal contents in potatoes. National Institute of Food and Drugs Safety Evaluation, Chungbuk, Korea.
[21] NIFDS, 2012. The Korea standard for concentration of heavy metal contents in root and tuber crop. National Institute of Food and Drugs Safety Evaluation, Chungbuk, Korea.
[22] CODEX, 2011. Working document for information and use in discussions related to contaminants and toxins in the GSCTFF, Codex Alimentarius Commission, Rome, Italy. Pp 13, 15.
[23] US EPA (2013): Reference dose (RfD): Description and use in health risk assessments, Background Document 1A, Integrated risk information system (IRIS); United States Environmental Protection Agency: Washington, DC, 15 March 2013; http://wwwepa.gov/iris/rfd.htm.
[24] US EPA (2000a). Risk-based concentration table. Philadelphia PA: United States Environmental Protection Agency, Washington DC.
[25] Singh, A; Sharma, R. K; M. Agrawal, F. M. Marshall, (2010). Risk assessment of heavy metal toxicity through contaminated vegetables from waste water irrigated area of Varanasi, India. Tro. Ecology 51: 375-387.
[26] Abdu N. and A. A Yusuf (2013). Human health risk characterization of lead pollution in contaminated farmlands of Abare village, Zamfara State, Nigeria. African Journal of Environmental Science & Technology 7 (9): 911–916.
[27] Harmanjit Kaur, Dinesh Goyal, Assessing potential risk of heavy metal exposure in green leafy vegetables. Int. J. Res. Environ. Sci. Technol. 1 (2011) 43-46.
[28] US EPA (2000b). Handbook for non-cancer health effects evaluation. Washington (DC) 7 U.S. Environmental Protection Agency.
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    Pereware Adowei, Elvis Ebenezer, Douye Markmanuel. (2020). Concentrations and Human Health Risk Assessment of Cd, Co, Cr, Ni, and Pb via Eating White Granulated Garri Produced in Nigeria. American Journal of Environmental Protection, 9(4), 77-85. https://doi.org/10.11648/j.ajep.20200904.11

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    ACS Style

    Pereware Adowei; Elvis Ebenezer; Douye Markmanuel. Concentrations and Human Health Risk Assessment of Cd, Co, Cr, Ni, and Pb via Eating White Granulated Garri Produced in Nigeria. Am. J. Environ. Prot. 2020, 9(4), 77-85. doi: 10.11648/j.ajep.20200904.11

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    AMA Style

    Pereware Adowei, Elvis Ebenezer, Douye Markmanuel. Concentrations and Human Health Risk Assessment of Cd, Co, Cr, Ni, and Pb via Eating White Granulated Garri Produced in Nigeria. Am J Environ Prot. 2020;9(4):77-85. doi: 10.11648/j.ajep.20200904.11

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  • @article{10.11648/j.ajep.20200904.11,
      author = {Pereware Adowei and Elvis Ebenezer and Douye Markmanuel},
      title = {Concentrations and Human Health Risk Assessment of Cd, Co, Cr, Ni, and Pb via Eating White Granulated Garri Produced in Nigeria},
      journal = {American Journal of Environmental Protection},
      volume = {9},
      number = {4},
      pages = {77-85},
      doi = {10.11648/j.ajep.20200904.11},
      url = {https://doi.org/10.11648/j.ajep.20200904.11},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ajep.20200904.11},
      abstract = {White granulated garri, an extensively consumed foodstuff in Nigeria made from fermented cassava tubers has recorded little studies on its heavy metals content. The concentrations of Cd, Co, Cr, Ni and Pb in commercial white granulated garri commonly sold in three major markets in Port Harcourt, Nigeria were established using Inductively Coupled Plasma - Mass Spectrometry (ICP-MS) after microwave-assisted acid digestion. The mean concentrations (x ̅±SD,in mg/kg on dry-weight basis) of heavy metals in garri samples were Cd: 0.021 ± 0.005, Co: 0.027 ± 0.004, Cr: 2.50 ± 0.047, Ni: 0.849 ± 0.021, and Pb: 0.522 ± 0.039 respectively. A food frequency questionnaire-based (FFQ) survey on dietary consumption rates of garri as a source of carbohydrate among consumers and marketers showed that garri accounted for ˃ 97.5% of total carbohydrate consumed in Nigeria. Statistical evaluation of the data by one-way analysis of variance discloses noteworthy differences of metal contents for Cd, Co, Ni and Pb in garri from the study area with the exception of Cr. The mean daily intake of metals (mg/person/day) from garri consumption using dietary modelling was found to be Cd: 1.49 x 10-4, Co: 1.34 x 10-5, Cr: 1.24 x 10-2, Ni: 4.23 x 10-3 and Pb: 2.60 x 10-3 respectively. These values are lower than the upper tolerable daily intake limits for heavy metals in food. The target hazard quotients (THQ), health risk index (HRI) and lifetime cancer risk (CR) for Cd, Co, Cr, Ni, and Pb indicate that, the probable human health risk associated with consumption of garri for the target population is moderately low at the moment. However, modest consumption rate of the product is recommended due to potential bioaccumulation of heavy metals found in garri.},
     year = {2020}
    }
    

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  • TY  - JOUR
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    AU  - Pereware Adowei
    AU  - Elvis Ebenezer
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    DO  - 10.11648/j.ajep.20200904.11
    T2  - American Journal of Environmental Protection
    JF  - American Journal of Environmental Protection
    JO  - American Journal of Environmental Protection
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    PB  - Science Publishing Group
    SN  - 2328-5699
    UR  - https://doi.org/10.11648/j.ajep.20200904.11
    AB  - White granulated garri, an extensively consumed foodstuff in Nigeria made from fermented cassava tubers has recorded little studies on its heavy metals content. The concentrations of Cd, Co, Cr, Ni and Pb in commercial white granulated garri commonly sold in three major markets in Port Harcourt, Nigeria were established using Inductively Coupled Plasma - Mass Spectrometry (ICP-MS) after microwave-assisted acid digestion. The mean concentrations (x ̅±SD,in mg/kg on dry-weight basis) of heavy metals in garri samples were Cd: 0.021 ± 0.005, Co: 0.027 ± 0.004, Cr: 2.50 ± 0.047, Ni: 0.849 ± 0.021, and Pb: 0.522 ± 0.039 respectively. A food frequency questionnaire-based (FFQ) survey on dietary consumption rates of garri as a source of carbohydrate among consumers and marketers showed that garri accounted for ˃ 97.5% of total carbohydrate consumed in Nigeria. Statistical evaluation of the data by one-way analysis of variance discloses noteworthy differences of metal contents for Cd, Co, Ni and Pb in garri from the study area with the exception of Cr. The mean daily intake of metals (mg/person/day) from garri consumption using dietary modelling was found to be Cd: 1.49 x 10-4, Co: 1.34 x 10-5, Cr: 1.24 x 10-2, Ni: 4.23 x 10-3 and Pb: 2.60 x 10-3 respectively. These values are lower than the upper tolerable daily intake limits for heavy metals in food. The target hazard quotients (THQ), health risk index (HRI) and lifetime cancer risk (CR) for Cd, Co, Cr, Ni, and Pb indicate that, the probable human health risk associated with consumption of garri for the target population is moderately low at the moment. However, modest consumption rate of the product is recommended due to potential bioaccumulation of heavy metals found in garri.
    VL  - 9
    IS  - 4
    ER  - 

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Author Information
  • Department of Pure & Industrial Chemistry, Faculty of Science, University of Port Harcourt, Port Harcourt, Nigeria

  • Department of Pure & Industrial Chemistry, Faculty of Science, University of Port Harcourt, Port Harcourt, Nigeria

  • Department of Chemical Sciences, Faculty of Science, Niger Delta University, Wilberforce Island, Bayelsa State, Nigeria

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