The impact of o, p`- DDT pesticide toxicity on the growth of Medaka fish embryo <i>Oryzias latipes</i>

Authors

  • Nguyen Xuan Tong Graduate University of Science and Technology, VAST, Vietnam Institute for Environmental Science, Engineering and Management, Industrial University of Ho Chi Minh city, Ho Chi Minh city, Vietnam
  • Tran Thi Thu Huong Faculty of Environment, Hanoi University of Mining and Geology, Hanoi, Vietnam
  • Mai Huong University of Science and Technology Hanoi, VAST, Vietnam
  • Duong Thi Thuy Institute of Environmental Technology, VAST, Vietnam
  • Nguyen Hoang Thuy Vy Department of Aquatic Biotechnology, Biotechnology Center of Ho Chi Minh city, Ho Chi Minh city, Vietnam

DOI:

https://doi.org/10.15625/1859-3097/14023

Keywords:

Medaka O. curvinotus, toxicity, o, p`- DDT, LC50, POPs, mortality.

Abstract

The one-day-old O. latipes embryos is harvested and exposed to different concentrations of o, p`-DDT 0.04; 0.08; 0.12; 0.16; 0.2; 0.24; 0.28 and 0 µg/l (the control sample is not supplemented with o, p`-DDT) for 24, 48, 72 and 96 hours. After 24, 48, 72 and 96 hours, the results showed that LC50 value is gradually decreased, respectively 0.1013; 0.0772; 0.0486 and 0.0359 µg/l. The difference between LC50 values depends on the exposure concentration and exposure time. The results showed that the mortality rates of Medaka O. latipes increased with increasing pesticide concentrations as well as increasing exposure time. The experiment for observation of morphology and structure also found malformations in the spine and eyes of fish embryos. This chemical has strongly affected embryonic heart rate and embryonic morphology during growth and development.

Downloads

Download data is not yet available.

References

Stockholm Convention on Persistent Organic Pollutants - POP, 2011.

PCB management project in Vietnam, 2012. Training documnets for PCB communication skills.

Ministry of Agriculture and Rural Development, 2014. Report of real status and management solutions for plant protection drugs.

Vietnam Environment Administration - Ministry of Natural Resources and Environment, 2014. 10-year book on implementation of the Stockholm Convention on persistent organic pollutants in Vietnam.

ATSDR (Agency for Toxic Substances and Disease Registry), 2002. Toxicological profile for DDT, DDE, and DDD. US Department of Health and Human Services, Public Health Service, Agency for Toxic Substances and Disease Registry.

Jezierska, B., Ługowska, K., and Witeska, M., 2002. The effect of temperature and heavy metals on heart rate changes in common carp Cyprinus carpio L. and grass carp Ctenopharyngodon idella (Val.) during embryonic development. Fisheries & Aquatic Life, 10(2), 153–165.

Brodeur, J. C., Dixon, D. G., and McKinly, R. S., 2001. Assessment of cardiac output as a predictor of metabolic rate in rainbow trout. Journal of Fish Biology, 58(2), 439–452.

Lucas, M. C., 1994. Heart rate as an indicator of metabolic rate and activity in adult Atlantic salmon, Salmo salar. Journal of Fish Biology, 44(5), 889–903.

Uchida, M., Nakamura, H., Kagami, Y., Kusano, T., and Arizono, K., 2010. Estrogenic effects of o, p’-DDT exposure in Japanese medaka (Oryzias latipes). The Journal of toxicological sciences, 35(4), 605–608.

Paul-Prasanth, B., Shibata, Y., Horiguchi, R., and Nagahama, Y., 2011. Exposure to diethylstilbestrol during embryonic and larval stages of medaka fish (Oryzias latipes) leads to sex reversal in genetic males and reduced gonad weight in genetic females. Endocrinology, 152(2), 707–717.

Woody, C. A., Hughes, R. M., Wagner, E. J., Quinn, T. P., Roulson, L. H., Martin, L. M., and Griswold, K., 2010. The mining law of 1872: change is overdue. Fisheries, 35(7), 321–331.

Balistrieri, L. S., Box, S. E., Bookstrom, A. A., Hooper, R. L., and Mahoney, J. B., 2002. Impacts of historical mining in the Coeur d’Alene River Basin. Pathways of metal transfer from mineralized sources to bioreceptors. US Geological Survey Bulletin, 2191, 1–34.

National Research Council, 2005. Superfund and mining megasites: Lessons from the Coeur d’Alene River Basin. National Academies Press.

Cairns Jr, J., 1977. Aquatic ecosystem assimilative capacity. Fisheries, 2(2), 5–7.

Maret, T. R., and MacCoy, D. E., 2002. Fish assemblages and environmental variables associated with hard-rock mining in the Coeur d’Alene River basin, Idaho. Transactions of the American Fisheries Society, 131(5), 865–884.

Kivi, R., 2010. How Does Water Pollution Affect Fish. Available at (eHow. com).

Kirchmaier, S., Naruse, K., Wittbrodt, J., and Loosli, F., 2015. The genomic and genetic toolbox of the teleost medaka (Oryzias latipes). Genetics, 199(4), 905–918.

Naruse, K., Tanaka, M., and Takeda, H. (Eds.), 2011. Medaka: a model for organogenesis, human disease, and evolution. Springer Science & Business Media.

Kasahara, M., Naruse, K., Sasaki, S., Nakatani, Y., Qu, W., Ahsan, B., ... and Jindo, T., 2007. The medaka draft genome and insights into vertebrate genome evolution. Nature, 447(7145), 714–719.

Long, T. D., Thu, V. T., and Thuy, T. T., 2015. Zebra and Medaka fishs are model for human disease research. The Second Conference of Youth Science and Technology, Faculty of Medicine and Pharmacy.

Howe, K., Clark, M. D., Torroja, C. F., Torrance, J., Berthelot, C., Muffato, M., ... and McLaren, S., 2013. The zebrafish reference genome sequence and its relationship to the human genome. Nature, 496(7446), 498–503.

Nair, S. G., Radha, R., and Nair, C. R., 2017. Studies on acute toxicity to pesticide stress in a freshwater fish Cirrhinus mrigala. International Journal of Fisheries and Aquatic Studies, 5, 335–358.

Thanh, D. T. H., Thanh, N. L., and Thang, N. D., 2016. Toxicological and melanin synthesis effects of Polygonum multiflorum root extracts on zebrafish embryos and human melanocytes. Biomedical Research and Therapy, 9(3), 1–11.

Holcombe, G. W., Phipps, G. L., and Tanner, D. K., 1982. The acute toxicity of kelthane, dursban, disulfoton, pydrin, and permethrin to fathead minnows Pimephales promelas and rainbow trout Salmo gairdneri. Environmental Pollution Series A, Ecological and Biological, 29(3), 167–178.

Veeraiah, K., Rao, S., and Dhilleswarao, H., 2013. Changes in biochemical parameters of freshwater fish Labeo rohita exposed to lethal and sub-lethal concentrations of indoxacarb. International Journal of Bioassays, 2, 1282–1387.

Anastasi, A., and Bannister, T. V., 1990. Effect of pesticide on Mediterranean fish muscle enzyme. Acta Adriatica, 21, 119–136.

Kumar, H. E. M. A. N. T., and Gupta, A. B., 1997. Toxicity of organophosphorus, carbnonate and synthetic pyrethroid pesticides to the Indian catfish, Heteropneustes fossilis. J Nature Conserve, 9(1), 111–114.

Marrs, T. C. (Ed.), 2012. Mammalian toxicology of insecticides (No. 12). Royal Society of Chemistry.

Narahashi, T., 2010. Neurophysiological effects of insecticides. In Hayes’ Handbook of Pesticide Toxicology (pp. 799–817). Academic Press.

Downloads

Published

2020-03-30

How to Cite

Tong, N. X., Huong, T. T. T., Huong, M., Thuy, D. T., & Vy, N. H. T. (2020). The impact of o, p`- DDT pesticide toxicity on the growth of Medaka fish embryo <i>Oryzias latipes</i>. Vietnam Journal of Marine Science and Technology, 20(1), 73–81. https://doi.org/10.15625/1859-3097/14023

Issue

Section

Articles