Korean Journal of Ecology and Environment (생태와환경)

The Korean Society of Limnology (한국수생태학회)
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Effect on Early Life Stage of Three Freshwater Fish (Carassius auratus, Cyprinus carpio, Oryzias latipes) Exposed to Suspended Solids

부유토사가 담수 어류 3종(붕어, 잉어, 송사리)의 초기 생활사에 미치는 영향

  • Moon, Seong-Dae (Institute of Environmental Protection and Safety, NeoEnBiz Co.) ;
  • Kang, Sin-Kil (Institute of Environmental Protection and Safety, NeoEnBiz Co.) ;
  • Lee, Chang-Hoon (Institute of Environmental Protection and Safety, NeoEnBiz Co.) ;
  • Sung, Chan-Gyoung (Institute of Environmental Protection and Safety, NeoEnBiz Co.) ;
  • An, Kwang-Guk (Department of Biological Science, College of Biosciences and Biotechnology, Chungnam National University) ;
  • Choi, Tae Seob (Institute of Environmental Protection and Safety, NeoEnBiz Co.)
  • 문성대 ((주)네오엔비즈 환경안전연구소) ;
  • 강신길 ((주)네오엔비즈 환경안전연구소) ;
  • 이창훈 ((주)네오엔비즈 환경안전연구소) ;
  • 성찬경 ((주)네오엔비즈 환경안전연구소) ;
  • 안광국 (충남대학교 생명과학과) ;
  • 최태섭 ((주)네오엔비즈 환경안전연구소)
  • Received : 2014.03.28
  • Accepted : 2014.06.13
  • Published : 2014.06.30
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Abstract

To assess the adverse effects of suspended solids on fishes, the hatching rate of embryo, and survival and growth of larvae were measured with common fish species of river such as crusian carp (Carassius auratus), common carp (Cyprinus carpio) and medaka (Oryzias latipes). Bioassay on hatching rate of embryo was conducted with a range of turbidity as 10 levels from 0.2 to 8,080 NTU. Another bioassay on 4-day larval survival and 21-day larval growth were also conducted with a range of turbidity as 8 levels from 0.1 to 8,260 NTU, and 6 levels from 0.7 to 2,030 NTU, respectively. The hatching rate of C. auratus was not significantly different from that of control at turbidity below 4,040 NTU, whereas it decreased when turbidity was 8,080 NTU (p<0.05). The hatching rate of C. carpio was not affected by concentration of suspended solids. For O. latipes, the hatching rate significantly decreased from 254 NTU (p<0.001) and it was zero when turbidity was 8,080 NTU. The 4-day survival of larvae of all 3 species was not affected by turbidity, while the larval growth of all 3 species was significantly affected. The turbidity effect on the growth of C. auratus and C. carpio was observed from 7 days after the exposure at turbidity level of 145, 143 NTU, respectively. The turbidity effect on the growth of O. latipes was observed from 14 days after the exposure at turbidity level of 254 NTU. The results of this study will provide the basic information for the derivation of water quality criteria on suspended solids for the protection of aquatic ecosystem and the quantitative ecological risk assessment of freshwater environment.

본 연구에서는 부유토사로 인한 탁도 증가가 어류에게 미치는 영향에 대해 실험실 모의실험을 수행하였다. 국내 강 또는 호소에서 출현 비율이 높은 붕어, 잉어, 송사리를 대상으로 수정란 부화율 평가를 수행한 결과 붕어, 잉어는 4,040 NTU 수준까지 수정란 부화에 미치는 영향이 없었지만, 송사리는 254 NTU 이상의 구간에서 부화율이 저해되는 영향을 보였다. 붕어, 잉어, 송사리 치어의 4일간 노출 결과 생존에 미치는 영향은 없었다. 반면 성장률 결과에서 잉어와 붕어는 7일, 14일, 21일 모두 143 NTU 구간부터 성장저해 영향을 보였다. 송사리는 14일 노출 시 254 NTU, 21일간 노출 시 501 NTU 구간부터 성장저해 영향을 보였다. 따라서 강 또는 호소에서 143 NTU 이상의 탁도가 발생할 경우 붕어, 잉어의 성장을 저해시킬 수 있고, 250 NTU 이상의 탁도는 송사리와 같이 민감 어종의 부화율이 저해될 수 있을 것으로 사료된다.

Keywords

References

  1. Abraham, M. and M. Kattenfeld. 1997. The role of turbidity as a constraint on predator-prey interactions in aquatic environments. Behavioral Ecology and Sociobiology 40: 169-174. https://doi.org/10.1007/s002650050330
  2. Anadu, D.I., G.I. Scott and M.H. Fulton. 1999. Toxicity of DDT to the different life stages of the mummichog Fundulus heteroclitus (Wabum). Bulletin of Environmental Contamination and Toxicology 63: 181-187. https://doi.org/10.1007/s001289900964
  3. Banasiak, R. and R. Verhoeven. 2006. Quantification of the erosion resistance of undisturbed and remoulded cohesive sediments. Water, Air, and Soil Pollution 6: 17-27. https://doi.org/10.1007/s11267-005-9010-5
  4. Bash, J., C. Berman and S. Bolton. 2001. Effects of turbidity and suspended solids on Salmonids. University of Washington Water Center.
  5. Bentivegna, C.S. and T. Piatkowski. 1998. Effects of tributyltin on medaka (Oryzias latipes) embryos at different stages of development. Aquatic Toxicology 44: 117-128. https://doi.org/10.1016/S0166-445X(98)00065-4
  6. Berry, W., N. Rubenstein, B. Melzian and B. Hill. 2003. The biological effects of suspended and bedded sediments (SABS) in aquatic systems: A review. Internal report to US EPA, Office of Research and Development, National Health and Environmental Effects Laboratory, Narragansett, RI.
  7. Burton, T.A., G.W. Harbey and M.L. McHenry. 1990. Protocols for assessment of dissolved oxygen, fine sediment and salomonid embryo survival in an artificial redd. Idaho Depertmaent of Health and Welfare, Division of Environmental Quality, Water Quality Monitoring Protocols Report 1, Boise.
  8. Choi, J.S. 2005. Fish fauna and community in Cheongpyeong reservoir. Korean Journal of Limnology 38(1): 63-72.
  9. Finney, D.J. 1978. Statistical Method in Biological Assay, 3rd edition. Griffin, London.
  10. Gradall, K.S. and W.A. Swenson. 1982. Response of brook trout and creek chubs to turbidity. Transactions of American Fisheries Society 111: 392-395. https://doi.org/10.1577/1548-8659(1982)111<392:ROBTAC>2.0.CO;2
  11. Gregory, R.S. 1993. Effects of turbidity on the predator avoidance behavior of juvenile chinook salmon (Oncorhynchus tshawytscha). Canadian Journal of Fisheries and Aquatic Sciences 50: 241-264. https://doi.org/10.1139/f93-027
  12. Han, S.C. 2008. The Influence of Muddy Water on the Community of Benthic Macroinvertebrates and Ichthyofauna. Department of Biology Graduate School Andong National University, p. 80.
  13. Han, S.C., H.Y. Lee, E.W. Seo, J.H. Shim and J.E. Lee. 2007. The influence of muddy water in Imha Reservoir on the ichthyofauna and fish growth. Journal of Life Science 17(8): 1104-1110. https://doi.org/10.5352/JLS.2007.17.8.1104
  14. Hellawell, J.M. 1986. Biological Indicator of Freshwater Pollution and Environmental Management. Elsevier Applied Science Publishers, New York, p. 546.
  15. Hunter, J.W. 1973. A Discussion of Game Fish in the State of Washington as Related to Water Requirements. Washington State Department of Ecology. Olympia, Wa.
  16. Kim, J.H., J.W. Seo, Y.E. Na and K.G. An. 2007a. Ecological health assessments on turbidwater in the downstream after a construction of Yongdam Dam. Korean Journal of Limnology 40(1): 130-142.
  17. Kim, J.K., J.S. Choi, Y.S. Jang, G.Y. Lee and B.C. Kim. 2007b. Effect of turbid water on fish community: case studies of the Daegi stream and the Bongsan Stream. Korean Journal of Limnology 40(3): 459-467.
  18. Lee, C., M.J. Shin, J.E. Lee and E.W. Seo. 2006b. Tissues and plasma proteins of Hemiculter eigenmanni in muddy water of Imha reservoir. Korean Journal of Environmental Biology 24(3): 213-220.
  19. Lee, J.Y., J.S. Choi, J.K. Kim, Y.S. Jang, K.Y. Lee and B.C. Kim. 2008. Ecological effects of Kumgang fat minnow (Rhynchocypris kumgangensis) on turbid water. Korean Journal of Environment and Ecology 22(2): 184-191.
  20. Lee, K.S. 2008. The effects of suspended solids on the mortality and the glycogen content of abalone, Haliotis discus hannai. Journal of the Korean Society of Marine Environment & Safety 14(3): 183-187.
  21. Lee, S.H., J.S. Choi, K.Y. Lee, Y.S. Jang, I.S. Lim, W.M. Heo, J.K. Kim and B.C. Kim. 2006a. A study of water quality and fish community in lake Doam. Korean Journal of Limnology 49(2): 167-177.
  22. McDonald, D.D., C.G. Ingersoll and T.A. Berger. 2000. Development and evaluation of consensus-based sediment quality guidelines for freshwater ecosystems. Archives of Environmental Contamination and Toxicology 39(1): 20-31. https://doi.org/10.1007/s002440010075
  23. Moon, W.K., D.Y. Bae, M.S. Jung, S.D. Lee and J.K. Kim. 2012. Comparison of larval fish survival of pale chub (Zacco platypus) exposed to different levels turbidity. Korean Journal of Limnology 45(3): 314-321.
  24. Newcombe, C.P. and J.O.T. Jensen. 1996. Channel suspended sediment and fisheries: a synthesis for quantitative assessment of risk and impact. North American Journal of Fisheries management 16: 693-727. https://doi.org/10.1577/1548-8675(1996)016<0693:CSSAFA>2.3.CO;2
  25. Newcombe, C.P. and D.D. MacDonald. 1991. Effects of suspended sediments on aquatic ecosystems. North American Journal of Fisheries Management 11: 72-82. https://doi.org/10.1577/1548-8675(1991)011<0072:EOSSOA>2.3.CO;2
  26. NIER (National Institute of Environmental Research). 2011. Baseline Concentrations of Heavy Metals in River Sediments in Korea. p. 107.
  27. OECD. 1992a. Test Guideline 203 Fish, acute toxicity test.
  28. OECD. 1992b. Test Guideline 210 Fish, early-life stage toxicity test.
  29. OECD. 1998. Test Guideline 212 Fish, short-term toxicity test on embryo and sac-fry stages.
  30. OECD. 2000. Test Guideline 215 Fish, juvenile growth test.
  31. Park, C.G. and M.A. Kang. 2006. Impact assessment of turbidity water caused clays on algae growth. The Journal of Engineering Geology 16(4): 403-409.
  32. Park, J.W., K.L. Lee, J.S. Choi and H.S. Kim. 2005. Dynamics of phytoplankton community after formation of turbid water in lake Imha. Korean Journal of Limnology 38(3): 429-434.
  33. Park, J.W., S.H. Yu, S.Y. Kim, J.E. Lee and E.W. Seo. 2008. Effect of turbid water on the phytoplankton community in Imha Reservoir. Journal of Life Science 18(12): 1671-1678. https://doi.org/10.5352/JLS.2008.18.12.1671
  34. Shin, M.J., J.E. Lee and E.W. Seo. 2007. The tissues and blood components of Opsariichthys uncirostris amurensis in the muddy water area. Journal of Life Science 17(1): 97-104. https://doi.org/10.5352/JLS.2007.17.1.097
  35. Shin, M.J., J.E. Lee and E.W. Seo. 2009. Effect of muddy water on the fishes in Imha reservoir. Journal of Life Science 19 (8): 1112-1118.
  36. Shin, M.J., J.S. Kim, Y.H. Hwang, J.E. Lee and E.W. Seo. 2008. Effect of turbidity changes on tissues of Zacco kireanus. Korean Journal of Limnology 41(1): 73-80.
  37. Shin, U.G. 2005. Influence of turbidity on zooplankton dynamics in the Nakdong River. Pusan University, p. 114.
  38. Sigler, J.W., T.C. Bjornn and F.H. Everest. 1984. Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113: 142-150. https://doi.org/10.1577/1548-8659(1984)113<142:EOCTOD>2.0.CO;2
  39. U.S. Environmental Protection Agency. 1996. Microwave assisted acid digestion of siliceous and organically based matrices. Method 3052, Office of Solid Waste and Emergency Response, U.S. Government Printing Office, Washington, DC.
  40. U.S. Environmental Protection Agency. 2002a. Short-term methods for estimating the chronic toxicity of effluents and receiving waters to freshwater organisms. Fourth Edition.
  41. U.S. Environmental Protection Agency. 2002b. Methods for measuring the acute toxicity of effluents and receiving waters to freshwater and marine organisms. Fifth Edition.
  42. Utne-Palm, A.C. 1999. The effect of prey mobility, prey contrast, turbidity and spectral composition on the reaction distance of Gobiusculus flavescens to its planktonic prey. Journal of Fish Biology 54: 1244-1258. https://doi.org/10.1111/j.1095-8649.1999.tb02052.x
  43. Wilber, D.H. and D.G. Clarke. 2001. Biological effects of suspended sediments: A review of suspended sediment impacts on fish and shellfish with relation to dredging activities in estuaries. North American Journal of Fisheries Management 21(4): 855-875. https://doi.org/10.1577/1548-8675(2001)021<0855:BEOSSA>2.0.CO;2
  44. Yu, S.H., J.S. Kim, M.J. Shin, J.E. Lee and E.W. Seo. 2009. Effect of turbid water on fishes in the streams of Imha reservoir. Journal of Life Science 19(10): 1410-1416. https://doi.org/10.5352/JLS.2009.19.10.1410
  45. Zar, J.H. 1984. Biostatistical Analysis 3rd ed. Prentice-Hall, New Jersey, p. 718.