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Effects of Bisphenol A to interspecific hybrids between marine medaka Oryzias dancena and javanese medaka O. javanicus

바다송사리, Oryzias dancena와 자바송사리, O. javanicus 간 잡종에 대한 비스페놀 A의 효과

  • Kim, Bong-Seok (Biotechnology Research Division, National Fisheries Research & Development Institute) ;
  • Song, Ha-Yeun (Department of Marine Bio-Materials & Aquaculture, Pukyong National University) ;
  • Nam, Yoon-Kwon (Department of Marine Bio-Materials & Aquaculture, Pukyong National University) ;
  • Kim, Dong-Soo (Department of Marine Bio-Materials & Aquaculture, Pukyong National University)
  • 김봉석 (국립수산과학원 생명공학과) ;
  • 송하연 (부경대학교 해양바이오신소재학과) ;
  • 남윤권 (부경대학교 해양바이오신소재학과) ;
  • 김동수 (부경대학교 해양바이오신소재학과)
  • Received : 2011.04.12
  • Accepted : 2011.07.06
  • Published : 2011.08.31

Abstract

Bisphenol A (BPA) is mainly used in the production of epoxy resins and polycarbonate plastics, which is a known endocrine disruptor and acutely toxic to aquatic organisms. In this study, estrogenic effect of BPA was investigated on hybrid between Oryzias dancena and O. javanicus (ODJ). ODJ were exposed to BPA of various concentrations (eg. 2.5 mg/L, 5.0 mg/L and 10.0 mg/L) for 56 days. The growth rate, abnormality and the ratio of female and male were observed in test group and control group. As a result, the growth was $14.7{\pm}2.0$ mm in total length (TL) in 2.5 mg/L, $13.7{\pm}2.5$ mm in 5.0 mg/L, $12.8{\pm}2.5$ mm in 10.0 mg/L in test group while it was $18.0{\pm}1.2$ mm in TL in control group which was not treated with bisphenol A. The result showed that the growth decreased as the concentration of BPA increased. The abnormality rate was 13.6% in control group, 65.4% in 2.5 mg/L, 81.3% in 5.0 mg/L and 98.1 % in 10.0 mg/L which showed increase in abnormality as an increase of BPA concentration. As a result of analyzing ratio of sex in the test group and control group, 6.0% was examined to be interspecific in controls, 76.9% in 2.5 mg/L and 100.0% in 5.0 mg/L and 10.0 mg/L. In conclusion, these results suggest that BPA has estrogenic effect on ODJ.

본 연구에서는 비스페놀 A를 사용하여 바다 송사리 Oryzias dancena와 자바 송사리 O. javanicus의 잡종군(ODJ)의 성전환을 유도하였다. 부화 직후의 ODJ에 비스페놀 A를 2.5 mg/L, 5.0 mg/L와 10.0 mg/L의 농도로 56일간 처리한 결과 대조군의 경우 평균 전장이 $18.0{\pm}1.2$ mm로 나타났고 비스페놀 A 처리군에서는 2.5 mg/L로 처리한 경우 $15.0{\pm}2.0$ mm, 5.0 mg/L 처리군은 $13.7{\pm}2.5$ mm, 10.0 mg/L 처리군에서는 $12.8{\pm}2.5$ mm로 나타나 대조군과 비스페놀 A 처리군에서 성장 차이가 관찰되었다. 또한, 처리군 간에서도 비스페놀 A의 농도가 높을수록 성장이 느린 것으로 나타났다. 기형률을 조사한 결과 대조군은 13.6%였고, 비스페놀 A 처리군의 경우 2.5 mg/L는 65.4%로 대조군에 비해 매우 높게 나타났으며, 이보다 농도가 높은 5.0 mg/L와 10.0 mg/L에서는 각각 81.3%와 98.1%로 처리 농도가 높아질수록 기형률이 높게 나타났다. 성전환율을 분석하기 위하여 조직학적 분석을 한 결과 대조군에서 사용된 ODJ 50마리 중 정상 수컷이 47마리였으나, 3마리가 간성(intersex)을 나타내었으며, 비스페놀 A 농도가 2.5 mg/L인 그룹에서 76.9%인 40마리가 간성으로 나타났으며, 23.1%인 12마리가 수컷으로 나타났다. 비스페놀 A 농도 5.0 mg/L와 10.0 mg/L인 그룹에서는 52마리 중 수컷은 한 마리도 나타나지 않았으며, 모든 개체에서 간성이 나타났다.

Keywords

References

  1. Alo, R., Facciolo, R.M., Madeo, M., Giusi, G., Carelli, A. and Canonaco, M.: Effects of the xenoestrogen bispheno A in diencephalic regions of the teleost fish Coris julis occur preferentially via distinct somatostatin receptor subtypes. Brain Res. Bull., 65: 267-273, 2005. https://doi.org/10.1016/j.brainresbull.2005.01.006
  2. Arukwe, A., Celius, T., Walther, B.T. and Goksoyr, A.: Effects of xenoestrogen treatment on zona radiata protein and vitellogenin expression in Atlantic salmon (Salmo salar). Aquat. Toxicol., 49: 159-170, 2000. https://doi.org/10.1016/S0166-445X(99)00083-1
  3. Brotons, J.A., Olea-Serrano, M.F., Villalobos, M., Pedraza, V. and Olea, N.: Xenoestrogens released from lacquer coatings in food cans, Environ. Health Perspectives, 103: 608-612, 1995. https://doi.org/10.1289/ehp.95103608
  4. Estlander, T., Jolanki, R., Henriks-Eckerman, M.L. and Kanerva, L.: Occupational contact allergy to bisphenol A. Contact Dermatitis, 40: 52-53, 1999. https://doi.org/10.1111/j.1600-0536.1999.tb05982.x
  5. Gray, M.A., Niimi, A.J. and Metcalfe, C.D.: Factors affecting the development of testis-ova in medaka, Oryzias latipes, exposed to octylphenol. Environmental Toxicology and Chemistry, 18: 1835-1842, 1999. https://doi.org/10.1897/1551-5028(1999)018<1835:FATDOT>2.3.CO;2
  6. Haubruge, E., Petit, F. and Gage, M.J.G.: Reduced sperm counts in guppies (Poecilia reticulata) following exposure to low levels of tributyltin and bisphenol A. Proc. R. Soc. Lond. B., 267: 2333-2337, 2000. https://doi.org/10.1098/rspb.2000.1288
  7. Inoue, K. and Takei, Y.: Asian medaka fishes offer new models for studying mechanisms of seawater adaptation. Comp. Biochem. Physiol. B., 136: 635-645, 2003. https://doi.org/10.1016/S1096-4959(03)00204-5
  8. Ishibashi, H., Watanabe, N., Matsumura, N., Hirano, M., Nagao, Y., Shiratsuchi, H., Hohra, S., Yoshigara, S. and Arizono, K.: Toxicity to early life stages and an estrogenic effect of a bisphenol A metabolite, 4-methyl-2,4-bis (4-hydroxyphenyl) pent-1-ene on the medaka (Oryzias latipes). Life Sciences, 77: 2643-2655, 2005. https://doi.org/10.1016/j.lfs.2005.03.025
  9. Kang, I.J., Yokota, H., Oshima, Y., Tsuruda, Y., Oe, T., Imada, N., Tadokoro, H. and Honjo, T.: Effects of bisphenol A on the reproduction of Japanese medaka (Oryzias latipes). Environ. Toxicol. Chem., 21: 2394-2400, 2002. https://doi.org/10.1002/etc.5620211119
  10. Kim, D.S., Bang, I.C. and Kim, I.B.: Gonadal sex differentiation in Misgurnus mizolepis. Korean J. Ichthyol., 2: 95-105, 1990.
  11. Kishida, M., McLellan, M., Miranda, J.A. and Callard, G.V.: Estrogen and xenoestrogens upregulate the brain aromatase isoform (P450aromB) and perturb markers of early development in zebrafish (Danio rerio). Comp. Biochem. Physiol., 129: 261-268, 2001. https://doi.org/10.1016/S1095-6433(01)00322-1
  12. Kwak, H.J., Bae, M.O., Lee, M.H., Lee, Y.S., Lee, B.J., Kang, K.S., Chae, C.L., Sung, H.J., Shin, J.S., Kim, J.H., Mar, W.C., Sheen, Y.Y. and Cho, M.H.: Effects of nonylphenol, bisphenol A, and their mixture on the vivipaours swordtail fish (Xiphophorus helleri). Environ. Toxicol. Chem., 20: 787-795, 2001. https://doi.org/10.1897/1551-5028(2001)020<0787:EONBAA>2.0.CO;2
  13. Labadie, P. and Budzinski, H.: Alteration of steroid hormone balance in juvenile turbot (Psetta maxaxa) exposed to nonylphenol, bisphenol A, tetrabromodiphenyl ether 47, diallylphthalate, oil, and oil spiked with alkylphenols. Arch. Environ. Contam. Toxicol., 50: 552-561, 2006. https://doi.org/10.1007/s00244-005-1043-2
  14. Lahnsteiner, F., Berger, B., Kletzl, M. and Weismann, T.: Effect of bisphenol A on maturation and quality of semen and eggs in the brown trout, Salmo trutta f. fario. Aquat. Toxicol., 75: 213-224, 2005. https://doi.org/10.1016/j.aquatox.2005.08.004
  15. Lindholst, C., Pedersen, K.L. and Pedersen, S.N.: Estrogenics response of bisphenol A in rainbow trout (Oncorhynchus mykiss), Aquatic Toxicol., 48: 87-94, 2000. https://doi.org/10.1016/S0166-445X(99)00051-X
  16. Milligan, S.R., Khan, O. and Nash, M.: Competitive binding of xenobiotic oestrogens to rat alpha-fetoprotein and to sex steroid binding proteins in human and rainbow trout (Oncorhynchus mykiss) plasma. General and Comparative Endocrinology, 112: 89-95, 1998. https://doi.org/10.1006/gcen.1998.7146
  17. Nimrod, A.C. and Benson, W.H.: Reproduction and development of Japanese medaka following an early life stage exposure to xenoestrogens. Aquatic. Toxicol., 44: 141-156, 1998. https://doi.org/10.1016/S0166-445X(98)00062-9
  18. Robert, T.R.: Systematic observations on tropical Asian medakas or ricefishes of the genus Oryzias, with descriptions of four new species. Ichthyol. Res., 45: 213-224, 1998. https://doi.org/10.1007/BF02673919
  19. Seki, M., Yokota, H., Matsubara, H., Tsuruda, Y., Maeda, M., Tadokoro, H. and Kobayashi, K.: Effect of ethinylestradiol on the reproduction and induction of vitellogenin and testis-ova in medaka (Oryzias latipes). Environmental Toxicology and Chemistry, 21: 1692-1698, 2002. https://doi.org/10.1002/etc.5620210822
  20. Sohoni, P., Tyler, C.R., Hurd, K., Caunter, J., Hetheridge, M., Williams, T., Woods, C., Evans, M. and Sumpter, J.P.: Reproductive effects of long-term exposure to bisphenol A in the fathead minnow (Pimephales promelas). Environ. Sci. Technol., 35: 2917-2925, 2001. https://doi.org/10.1021/es000198n
  21. Song, H.Y., Nam, Y.K., Bang, I-.C. and Kim, D.S.: Hybridization between marine medaka Oryzias dancena and Javanese medaka Oryzais javanicus. Kor. J. Fish Aquat. Sci., 43(5): 462-473, 2010.
  22. Tabata, A., Watanabe, N., Yamamoto, I., Ohnishi, Y., Itoh, M., Kamei, T., Magara, Y. and Terao, Y.: The effect of bisphenol A and chlorinated derivatives of bisphenol A on the level of serum vitellogenin in Japanese medaka (Oryzias latipes). Water Sci. Technol., 50: 125-132, 2004.
  23. Tabata, A., Miyamoto, N., Ohnishi, Y., Itoh, M., Yamada, T., Kamei, T. and Magara, Y.: The effect of chlorination of estrogenic chemicals on the level of serum vitellogenin of Japanese medaka (Oryzias latipes). Water Science and Technology, 47: 51-57, 2003.
  24. TemaNord: Chemicals with Estrogen-Like Effects, Nordic Council of Ministers, Copenhagen, pp. 35-51, 1996.
  25. Van den Belt, Verheyen, K.R. and Witters, H.: Comparison of vitellogenin responses in zebrafish and rainbow trout following exposure to environmental estrogens. Ecotoxicol. Environ. Safety, 56: 271-281, 2003. https://doi.org/10.1016/S0147-6513(03)00004-6
  26. Yamamoto, T.: Artificially induced sex-reversal in genotypic males of the medaka, Oryzias latipes, J. Exp. Zool., 123: 571-594, 1953. https://doi.org/10.1002/jez.1401230309
  27. Yokota, H., Tsuruda, Y., Maeda, M., Oshima, Y., Tadokoro, H., Nakazono, A., Honjo, T. and Kobayashi, K.: Effect of bisphenol A on the early life stage in Japanese medaka (Oryzias latipes). Environ. Toxicol. Chem., 19: 1925-1930, 2000. https://doi.org/10.1897/1551-5028(2000)019<1925:EOBAOT>2.3.CO;2
  28. Zha, J. and Wang, Z.: Acute and early life stage toxicity of industrial effulent on Japanese medaka (Oryzias latipes). Sci. Total Environ., 357: 112-119, 2006. https://doi.org/10.1016/j.scitotenv.2005.04.038