Impacts of Impoundments by Low-head and Large Dams on Benthic Macroinvertebrate Communities in Korean Streams and Rivers

소형 보와 대형 댐에 의해 형성된 저수역이 저서성 대형무척추동물 군집에 미치는 영향

  • Kil, Hye-Kyung (Seoul Metropolitan Government Research Institute of Public Health and Environment) ;
  • Kim, Dong-Gun (College of Life Sciences and Biotechnology, Korea University) ;
  • Jung, Sang-Woo (College of Life Sciences and Biotechnology, Korea University) ;
  • Jin, Young-Hun (Korean Entomological Institute, Korea University) ;
  • Hwang, Jeong-Mi (College of Life Sciences and Biotechnology, Korea University) ;
  • Bae, Kyung-Seok (Seoul Metropolitan Government Research Institute of Public Health and Environment) ;
  • Bae, Yeon-Jae (College of Life Sciences and Biotechnology, Korea University)
  • 길혜경 (서울시 보건환경연구원) ;
  • 김동건 (고려대학교 생명과학대학) ;
  • 정상우 (고려대학교 생명과학대학) ;
  • 진영헌 (고려대학교 한국곤충연구소) ;
  • 황정미 (고려대학교 생명과학대학) ;
  • 배경석 (서울시 보건환경연구원) ;
  • 배연재 (고려대학교 생명과학대학)
  • Received : 2010.03.06
  • Accepted : 2010.04.17
  • Published : 2010.06.30

Abstract

This study was conducted to examine the effects of dams on benthic macroinvertebrate communities in Korean streams and rivers. Four low-head dams and three large dams were studied throughout South Korea. Sampling was taken at immediately upper (impoundment), lower (riffle area), and control (riffle area) sites from the dams during 2004-2007. The upper sites, of which substrate heterogeneity and velocity were relatively low, showed a lower degree of species richness, density, and diversity indices, which is very different from the lower and control sites. Heavily polluted streams showed a lesser degree of community differences between the upper and lower sites. In the large dams, the upper and lower sites showed very low values of species diversity indices and very high values of dominance indices compared to the control sites. In the low-head dams, however, the difference of degree of the values was relatively smaller. Compositions of the functional feeding groups and the habitat orientation groups were relatively simpler at the upper sites than at the lower sites and the degree of difference was greater in the large dams. Species richness and community indices of benthic macroinvertebrates were more significantly affected by habitat characteristics than water quality at the upper sites; however, those were more significantly related with water quality at the lower sites. In conclusion, large and low-head dams could simplify stream habitats particularly at the upper sites (impoundment), and they negatively affected on the benthic macroinvertebrate communities inhabited the habitats. The impact was larger in the large dams than in the low-head dams.

본 연구는 우리나라의 하천과 강에 설치된 댐(보)이 저서성 대형무척추동물 군집에 미치는 영향을 알아보고자 전국의 대표적인 하천과 강에 설치된 4개의 소형 보와 3개의 대형 댐을 대상으로 댐의 상류(저수역: impoundment), 하류(유수역) 및 대조지점(유수역)에서 2004~2007년에 걸쳐 저서성 대형무척추동물의 군집을 조사하였다. 바닥물질이 단순하고 유속이 상대적으로 낮은 상류지점은 종풍부도, 개체수밀도 및 다양도지수가 상대적으로 낮았으며, 하류지점과는 큰 차이를 보였다. 수질오염이 심한 도시하천에서는 보의 상류와 하류지점 간의 군집의 차이가 거의 없었다. 대형 댐의 상류와 하류지점은 대조지점에 비해 다양도지수가 훨씬 낮았고, 우점도지수는 훨씬 높았다. 반면, 소형 보의 하류지점은 대조지점과 유사하였다. 서식 및 섭식 기능군은 상류지점이 하류지점에 비해 더욱 단순하였으며, 대형 댐의 상류지점은 소형 보의 상류지점에 비해 더욱 단순하였다. 저서성 대형무척추동물의 종풍부도와 군집지수는 상류지점에서는 수질오염보다는 서식처 특성에 더 큰 영향을 받는 것으로 나타났으며, 하류지점에서는 수질오염과 더 높은 상관성을 보였다. 결론적으로, 하천과 강에 설치된 보와 댐은 상류지점(저수역)의 서식처를 단순화시켜 저서성 대형무척추동물 군집에 부정적인 영향을 미치며, 규모가 큰 댐이 소형보에 비해 더 큰 악영향을 미칠 수 있음을 시사하였다.

Keywords

References

  1. 노태호, 전동준. 2004. 한국산 수서곤충류 섭식기능군 유형 및 군집 안정성 분석. 한국육수학회지 37: 137-148.
  2. 오용남, 전태수. 1991. 배내천 중류의 저서성 대형무척추동물에 대한 연구 II. 봇둑상하에서의 군집 및 환경비교. 한국생태학회지 14: 399-413.
  3. 윤일병. 1995. 수서곤충검색도설. 정행사, 서울.
  4. 윤일병, 공동수, 유재근. 1992. 저서성 대형무척추동물에 의한 생물학적 수질평가 연구; 오탁계급치 및 지표가중치 산정을 중심으로. 환경생물 10: 24-39.
  5. 환경부. 2000. 제2차 전국자연환경 조사 지침. 저서성 대형무척추동물 p. 85-143.
  6. Allan, D.J. 1995. Stream Ecology; Structure and Function of Running Waters. Champman & Hall, London.
  7. Baxter, R.M. 1977. Environmental effects of dams and impoundments. Annual Review of Ecololgy and Systematics 8: 255-283. https://doi.org/10.1146/annurev.es.08.110177.001351
  8. Benke, A.C. 1990. A perspective on America's vanishing streams. Journal of the North American Benthological Society 9: 77-88. https://doi.org/10.2307/1467936
  9. Camargo, J.A. and N.J. Voelz. 1998. Biotic and abiotic changes along the recovery gradient of two impounded rivers with different impoundment use. Environmental Monitoring and Assessment 50: 143-158. https://doi.org/10.1023/A:1005712024049
  10. Craig, D.A. 1987. Some of what you should know about water: or K.I.S.S. for hydrodynamics. Bulletin of North American Benthological Society 4: 178-182.
  11. Doeg, T.J. and J.D. Koehn. 1994. Effects of draining and desilting a small weir on downstream fish and macroinvertebrates. Regulated Rivers: Research and Management 9: 263-277. https://doi.org/10.1002/rrr.3450090407
  12. Dynesius, M. and C. Nilsson. 1994. Fragmentation and flow regulation of river systems in the northern third of the world. Science 266: 753-762. https://doi.org/10.1126/science.266.5186.753
  13. Hynes, H.B.N. 1970. The Ecology of Running Waters. Liverpool University Press, Liverpool.
  14. Kawai, T. and K. Tanida. 2005. Aquatic Insects of Japan: Manual with Keys and Illustrations. Tokai University Press, Kanagawa.
  15. Kondorf, G.M. 1997. Hungry water: Effects of dams and gravel mining on river channels. Environmental Management 21: 533-551. https://doi.org/10.1007/s002679900048
  16. Magilligan, F.J. and K. Nislow. 2001. Long-term changes in the regional hydrologic regime following impoundment in a humid-climate watershed. Journal of the American Water Resources Association 37: 1551-1570. https://doi.org/10.1111/j.1752-1688.2001.tb03659.x
  17. McCafferty, W.P. 1981. Aquatic Entomology, John & Bartlett, Boston.
  18. Merritt, R.W. and K.W. Cummins. 2008. An Introduction to the Aquatic Insects of North America. 4th ed. Kendall/ Hunt Publishing Company, Dubuque, Iowa.
  19. Pennak, R.W. 1989. Fresh-water Invertebrates of the United States. 3rd ed. John Wiley & Sons, New York.
  20. Petts, G.E. 1984. Impounded Rivers. Perspectives for Ecological Management. John Wiley & Sons. Chichester.
  21. Poff, N.L. and D.D. Hart. 2002. How dams vary and why it matters for the emerging science of dam removal. Bioscience 52: 659-668. https://doi.org/10.1641/0006-3568(2002)052[0659:HDVAWI]2.0.CO;2
  22. Stanley, E.H. and A.L. Michelle, M.W. Doyle and D.W. Marshall. 2002. Short-term changes in channel form and macroinvertebrate communities following low-head dam removal. Journal of North American Benthological Society 21: 172-187. https://doi.org/10.2307/1468307
  23. Throp, J.H. and A.P. Covich. 2001. Ecology and Classification of North American Freshwater Invertebrates. Academic Press, San Diago.
  24. Tiemann, J.S., D.P. Gillette, M.L. Wildhaber and D.R. Edds. 2004. Effects of lowhead dams on riffle-dwelling fishes and macroinvertebrates in a midwestern river. Transactions of the American Fisheries Society 133: 705-717. https://doi.org/10.1577/T03-058.1
  25. Ward, J.V. 1992. Aquatic Insect Ecology. John Wiley & Sons, New York.
  26. Ward, J.V. and J.A. Stanford. 1979. The Ecology of Regulated Streams. Plenum Press, New York.
  27. Waters, T.F. 1995. Sediment in Streams: Sources, Biological Effects, and Control. American Fisheries Society, Monograph 7, Bethesda, Maryland.
  28. Wiederholm, T. 1983. Chironomidae of the Holarctic Region. Part 1. Larvae. Entomologica Scandinavica Suppliments. No. 19.
  29. Williams, D.D. and B.W. Feltmate. 1992. Aquatic Insects. CBA International, Oxon.