Ecotoxicity of Selected Marine Paints on Tilapia guineensis, Palaemonetes africanus, Tympanotonus fuscatus, Aspergillus flavus and Pseudomonas aeruginosa

Authors

  • Elizabeth Briggs Department of Microbiology, University of Port Harcourt, Choba, Port Harcourt, Rivers State, Nigeria Author
  • Lucky O. Odokuma Department of Microbiology, University of Port Harcourt, Choba, Port Harcourt, Rivers State, Nigeria Author

Keywords:

Toxicity, Mortality, Heavy metals, Marine paint, Total Petroleum, Hydrocarbon (TPH), Poly Aromatic Hydrocarbon (PAH).

Abstract

Physiochemical analyses of two marine paints; Jotun and International paints, revealed 437.87mg/l and 382.13mg/l for TPH, 11.47 and 14.96mg/l for PAH. Heavy metals present included Nickel (6.904 and 9.208mg/L), iron (601.36 and 1,620.48mg/l), lead (16.47 and 174.40mg/l), Copper (5.848 and 22.732mg/l), Zinc (25.152 and 52.56m/l), Cadmium (0.41 and 1.43mg/l) and Chromium (2.632 and 3.348 mg/l). Mortality was used as an index for the 96hr acute toxicity test for fish, mollusc and crustacean while 24hr and 48hr were used for Bacteria and Fungi. Median lethal concentration (LC50) was calculated using the Probit method. The 96hr LC50 for Tilapia guineensis, Palaemonetes africanus, and Tympanotonus fuscatus for International paint were 5.01, 9.14, and 7.15ppm while that of Jotun paint were 7.62, 5.76 and 7.97ppm. The 24hr LC50 for Tilapia guineensis, Palaemonetes africanus, and Tympanotonus fuscatus for both toxicants were 0.21 and 0.26ppm respectively. The 24hr LC50 for Pseudomonas aeruginosa for both toxicants were 0.26 and 0.35ppm respectively. The 48hr LC50 for Aspergillus flavus for both toxicants are 0.21 and 0.26ppm. There was no significant difference between the LC50 of both paints to the various test organisms. Iron was found to be more predominant in the Tilapia guineensis than other metals. These findings further portray that the use of marine paint should be continued but manufacturers should develop environment-friendly nonstick coatings to prevent the adhesion of fouling organism by providing an extremely smooth surfaces on which these organisms have great difficulty in settling.

Downloads

Download data is not yet available.

References

[1] Bao, V. W. W., Leung, K. M. Y., Qiu, J. W., Lam, M. H. W. (2011). Acute toxicities of five commonly used antifouling booster biocides to selected subtropical and cosmopolitan marine spkecies. Marine Pollution Bulletin, 62(5), 1147–1151.

[2] Abbott A, Abel P. D., Arnold, Milne A. (2000). Cost-benefit analysis of the use of TBT: the case for a treatment approach. Science Total Environment, 258, 5–19.

[3] Atli, G., Canli, M. (2011). Essential metal (Cu, Zn) exposures alter the activity of ATPases in gill, kidney and muscle of tilapia Oreochromis niloticus. Ecotoxicology, 20, 1861–1869.

[4] Ito, M., Mochida, K., Ito, K., Onduka, T., Fujii, K. (2013). Induction of apoptosis in testis of the marine teleost mummichog Fundulus heteroclitus after in vivo exposure to the antifouling biocide 4, 5-dichloro-2-n-octyl-3(2H)-isothiazolone (Sea-Nine 211). Chemosphere, 90, 1053–1060.

[5] Schultz, M. P., Bendick, J. A., Holm, E. R., Hertel, W. M. (2011). Economic impact of biofouling on a naval surface ship. Biofouling, 27, 87-98.

[6] Almeida, E., Diamantino, T. C., de Sousa, O. (2007). Marine paints: the particular case of antifouling paints. Progress in Organic Coatings, 59, 2–20.

[7] Guardiola, F. A., Cuesta, A., Meseguer, J., Esteban, M. A. (2012). Risk of using antifouling biocides in aquaculture. International Journal of Molecular Science, 13, 1541-1560.

[8] Ho, K. K. Y., Leung, K. M. Y. (2014). Organotin contamination in seafood and its implication for human health risk in Hong Kong. Marine Pollution Bulletin, 85, 634–640.

[9] Cima, F., Bragadin, M., Ballarin, L. (2008). Toxic effects of new antifouling substances on tunicate haemocytes. I. Sea-Nine 211 and Chlorothalonil. Aquatic Toxicology, 86, 299–312.

[10] Telegdi, J., Trif, L., Románszki, L. (2016). Smart anti-biofouling composite coatings for naval applications. Smart Composite Coatings and Membranes: Transport, Structural, Environmental Energy Applied, 123–155.

[11] Haak, P. W. (1996). Antifouling systems, current status and developments. In: The Present Status of TBT-Copolymer Antifouling Paints. Proceedings of the International Symposium on Antifouling Paints for Ocean-going Vessels, The Hague, February 21, 1996.

[12] Railkin, A. I. (2004). Marine Biofouling Colonization Processes and Defenses. CRC Press, Boca Raton, FL.

[13] Alzieu, C., Sanjuan, J., Deltreil, J. P., Borel, M. (1986). Tin contamination in Arcachon Bay— effects on oyster shell anomalies. Marine Pollution Bulletin, 17, 494–498.

[14] Schultz, M. P. (2017). Effects of coating roughness and biofouling on ship resistance and powering. Biofouling, 23(5), 331–341.

[15] DPR, Environmental guidelines and standard for the petroleum industry in Nigeria. 1991.

[16] Bray, S. (2006). Tributyltin pollution on a global scale. An Overview of Relevant and Recent Research: Impacts and Issues, WWF UK.

[17] Pereira, M., & Ankjaergaard, C. (2009). Legislation affecting antifouling products. In Advances in Marine Antifouling Coatings and Technologies.

[18] Blanca, A. L. (2008). Environmental levels, toxicity and human exposure to tributyltin (TBT)-contaminated marine environment. A review. Environment International, 34(2), 292–308.

[19] Cheesbrough, M. (2004). District Laboratory practice in Trophical Countries, Part 2. Cambridge University Press, U.K. 76-85.

[20] APHA (1998). Standards methods for examination of water and wastewater. American Journal of Water Resources, 8(4), 155-163.

[21] Nrior, R. R. & Odokuma, L. O. (2016). Comparativer Toxicity of Drilling Fluids to Marine Water Shrimp (Mysidoposis bahia) and Brackish Water Shrimp (Palaemonetes africanus). IOSR Journal of Environmental Science, Toxicity and Food Technology, 9, 73-79.

[22] Williamson, K. J. and Johnson, O. G. (1981). A bacterial bioassay for assessment of wastewater toxicity. Water Research, 15, 383-390.

[23] Reish, O. L. and Oshida, O. S. (1987). Manual of method in aquatic Environment research. Part 10 – short-term static bioassays. FAO Fisheries Technical Paper No. 247, Rome, Pp 62.

[24] DPR, (1991). Environmental guidelines and standard for the petroleum industry in Nigeria.

[25] Hassinger, E. & Watson, J. (1998). Health effects of drinking water contaminants. Cooperative Extension. The University of Arizona. Arizona Water Series: p. 5.

[26] Odokuma, L. O. & Kindzeka, I. B. (2003). Response of Nitrobacter, Desmocaris tripinosa and Metylus edulish to Toxicity of Fire Oil Spill Dispersants. African Journal of Applied Zoology and Environmental Biology, 5, 14-20.

[27] Okpokwasili, G. C. & Odokuma, L. O. (1994). Tolerance of Nitrobacter to toxicity of some Nigerian crude oil. Bulletin of Environmental Contamination and Toxicology, 52(3), 388-395.

[28] Luke, M. E. & Odokuma, L. O. (2017). Acute toxicity of Houseboat Effluents on Palaemonetes africanus and Tilapia guineensis. IOSR Journal of Environmental Science, Toxicity and Food Technology. 11: 69-78.

Downloads

Published

2024-10-01

Issue

Section

Articles

How to Cite

Briggs, E., & Odokuma, L. O. (2024). Ecotoxicity of Selected Marine Paints on Tilapia guineensis, Palaemonetes africanus, Tympanotonus fuscatus, Aspergillus flavus and Pseudomonas aeruginosa. International Journal Of Research And Technopreneurial Innovations, 1(2), 24-33. https://ijrti.com.ng/index.php/home/article/view/45

Similar Articles

1-10 of 26

You may also start an advanced similarity search for this article.