Condition Factor and Hepatosomatic Index of Ptychadena mascariensis Exposed to Crude Oil

Authors

  • Nafagha-Lawal, Magdalene Okeh Center for Marine Pollution Monitoring and Seafood Safety, University of Port Harcourt, Nigeria Author
  • Sikoki, Francis David Department of Animal and Environmental Biology, University of Port Harcourt, Nigeria Author
  • Georgewill, Onwunari Abraham Department of Pharmacology, University of Port Harcourt, Nigeria Author

Abstract

Amphibian population declines have been reported and many causes have been implicated which include habitat alteration, environmental change and pollution. Unfortunately, not much is known of the effects of crude oil pollution on the species. This study therefore investigated the haematological changes associated with exposure of the frog, Ptychadena mascariensis to sub-lethal concentrations of the water-soluble fractions of crude oil using static renewal bioassay system for 12 weeks. Water parameters were also monitored throughout the duration of the experiment. Water quality parameters remained within the ranges for water bodies in the Niger Delta with no significant differences between the control and treatment groups. The results revealed that crude oil had a negative impact on the frogs and showed dose-dependent reductions in K and HSI values. However, the values of K were not significantly reduced in the test groups compared to the control groups (p>0.05). HSI values were significantly reduced in the test groups compared to the control groups (p<0.05). Given the frequent cases of oil spills in the Niger Delta which expose frogs to persistent levels of crude oil in the environment, there are possible long-term effects on the physiological well-being of the frogs as demonstrated by the results of this study.

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References

APHA, (1988). Standard methods for the examination of water and waste water (16th Ed.), American Public Health Association, Washington DC.1268pp.

Ariweriokuma S.V., Akinrotimi, O.A and Gabriel, U.U. (2011). Effects of Cypermethrin On Condition Factor and Organosomatic Indices of

Clarias gariepinus. Journal of Agriculture and Social Research.11: (2):67-72.

Bagenal, T.B. (1978). Aspects of fish fecundity. In: Gerking, S.D. (Eds). Ecology of Freshwater Fish Production. Blackwell Scientific Publications, Oxford. 75-101.

Bagenal, T.B. and Tesch, F.W. (1978). Age and Growth. In: Begenal, T. ed.Methods for assessment of fish production in fresh waters. 3rd ed. IBP Handbook No. 3, Oxford, Blackwell Science Publications. 101-136.

Barton, B.A., Morgan, J. D., and Vijayan, M.M. (2002). Physiological condition-related indicators of environmental stress in fish. In S. M.

Adams (Ed.), Biological indicators of aquatic ecosystem stress Bethesda: American Fisheries Society. 111–148.

Blaustein, A.R. Romantic J.M. and Kiese, B.J. (2003). Ultraviolet radiation, toxic chemicals and amphibian population declines, Diversity and distributions 9: 123-140.

Carey C. and Bryant, C.J. (1998). Possible interrelations among environmental contaminant and toxicants, amphibians development and decline of amphibian populations, Environ, health prospect103: 13-17.

Charles-Barnham P.S.M. and Baxter, A.(2003). Condition Factor, K, for Salmonid Fish. Fisheries note. State of Victoria, Department of Primary Industries.1-3.

Çiftçi, N., Özcan A, Karayakar, F., Cicik, B and Erdem.C. (2015). Effects of Zinc and Cadmium on Condition Factor, Hepatosomatic and Gonadosomatic Index of Oreochromis niloticus. Fresenius Environmental Bulletin 24: 1-4.

Corn, P.S. Stolzenburg, W. and Bury, R.B. (1989). Acid precipitation studies in Colorado and Wyoming: interim report of surveys of montane amphibians and water chemistry”. U.S fish and wildlife service biological report. 80: 26- 40.

Egunjobi, O.J. (2010). Growth performance and Hepatosomatic Index and Yield of Clarias gariepinus Fed Industrial Noodles Waste Cased Diet. BSc. Project of Aquaculture and Fisheries Management, University of Agriculture, Abeokuta, Nigeria. 41pp.

Ekweozor, I. K. E. (1989). A review of the effects of oil pollution in West African environment, Discovery and Innovation 3: 27-37.

F.E.P.A (1999). Guidelines and standards for environmental pollution control in Nigeria. The Federal

Environmental Protection Agency. 238pp.

Geode, R.W. and Barton, B.A. (1990). Organism indices and an autopsybased assessment as indicators of health and condition of fish. In:

Adams, S. A.(Eds). Biological indicators of stress. Bethsaida, Maryland. America fisheries society. 93-108.

Htun-han, M. (1978). The reproductive biology of the dab Limanda limanda (L) in the North Sea; gonadosomatic Index; Hepatosomatic Index and condition factor. J. Fish Biol. 13: 369-378.

Jennings, M.R. and Hayes, M.P. (1985). Pre-1900 overharvest of California [USA] red-legged frogs (Rana aurora draytonii): The inducement for bullfrog (Rana catesbeiana) introduction, Herpetologica. 41:94-103.

Kicheniuk, J.W. and Khan R.A. (1987). Effect of petroleum hydrocarbons on Atlantic cod Gardus following chronic exposure. Can. J. Zool. 65:490-494.

Kori-Siakpere, O. (2000). Petroleum induced alterations in the African catfish, Clarias gariepinus(Teugels 1984): II-Growth factors, Nig. J. Sc. Env. 2:87-92.

Lefcort, H.and Blaustein, A.R. (1995). Disease, predation avoidance and vulnerability to predation in tadpoles, Oikos. 74: 469-474.

Loumbourdis, N.S. and Vogiatzis, A.K. (2002). Impact of cadmium on liver pigmentary system of the frog Rana ridibunda. Ecotoxicol. Environ. Saf.53: 52-58

Nebeker, A.V., Schuytema, G.S., and Ott, S.L., (1995). Effect of cadmium on growth andbioaccumulation in theNorthwestern salamander Ambystoma gracile. Arch. Environ. Contam. Toxicol. 29: 492-499.

Nafagha, M.O., Sikoki, F. D and Georgewill, O. A. (2014). Histopathological Alterations of Ptychadena mascariensis Exposed to Sub Lethal Concentrations of Crude Oil. Biological and Chemical Research.3:151-159.

Nafagha, O.M. (2007). Effects of water soluble fractions of crude oil on tadpoles of Bufo macalatus and Ptychadena mascariensis. Msc. thesis of the Rivers state university of science and technology.82 pp.

Nafagha, O. M., (1999.) A survey of amphibian community (anura) of Port Harcourt, Rivers State, Nigeria, BSc project of University of Benin.48 pp.

Sessions, S.K. and Ruth, S.B. (1990). Explanation for naturally occurring supernumerary limbs in amphibians, The journal of experimental zoology Photochem. Photobiol. 61: 650-655.

Sindhe V. R. and Kulkarni, R.S. (2004). Gonadosomatic and hepatosomatic indices of the freshwater fish Notopterus notopterus (Pallas) in response to some heavy metal exposure. J Environ Biol.25(3):365-368.

Sun, P. L., Hawkins, W. E., Overstreet, R. M. and Brown-Peterson, N. J. (2009). Morphological deformities as biomarkers in fish fromcontaminated rivers in Taiwan,International Journal of Environmental Research and Public Health.6(8):2307–2331.

Papadimitriou, E.A. and Loumbourdis, N.S. (2003) Copper kinetics and hepatic metallothionein levels in the frog Rana ridibunda, after exposure to CuCl2. Bio. Metals, 16: 271-277.

Pauly, D. (1984). Fish Population Dynamics in Tropical Waters: Manual for use with Programmable Calculators. ICLARM Studies and Revision. 8:325pp.

Stolyar, O.B., Loumbourdis, N.N., Falfushinska, H.I., and Romanchuk, L.D. (2008). Comparison of Metal Bioavailability in Frogs from Urban and Rural Sites of Western Ukraine. Arch. Environ. Contam. Toxicol, 54:107-113.

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Published

2024-03-01

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How to Cite

Okeh, N.-L. M., David, S. F., & Abraham, G. O. (2024). Condition Factor and Hepatosomatic Index of Ptychadena mascariensis Exposed to Crude Oil. Toxicology Digest, 4(1), 65-73. https://toxicologydigest.org.ng/index.php/home/article/view/6

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