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Water Quality Assessment at Coastal Area of the East Sea of Korea

한국 동해연안의 수질 평가

  • Kim, Young-Sug (National Fisheries Research & Development Institute, Marine Environment Research Division) ;
  • Lee, Yong-Hwa (National Fisheries Research & Development Institute, Marine Environment Research Division) ;
  • Choi, Hee-Gu (National Fisheries Research & Development Institute, Marine Environment Research Division)
  • 김영숙 (국립수산과학원 어장환경과) ;
  • 이용화 (국립수산과학원 어장환경과) ;
  • 최희구 (국립수산과학원 어장환경과)
  • Received : 2011.09.06
  • Accepted : 2012.02.23
  • Published : 2012.02.28

Abstract

This study aims to investigate characteristics of water quality factors by using survey results of national marine environmental monitoring system from 2004 to 2010 at coastal area of the East Sea of Korea. In this study, we chose statistical methods to analyze the correlation among water quality parameters and principal component analysis for characteristics of each water environment. In addition to this, we evaluated each water's pollution level based on eutrophication standard of OECD, Eutrophication Index(EI), and Organic Pollution Index(OPI). Major factors were chlorophyll a and salt according to the analysis at coastal area of the East Sea. The sea was divided into the south and the central part by Jukbyeon. Also, Jukbyeon in the central part of the East Sea and Gampo in the southern sea coastal waters have been classified separately. The nutritional status of coastal area of East Sea presented Mesotrophic to Oligotrophic level and EI showed less than 1. OPI in all of the coastal area at the East Sea represented that the water quality condition was favorable.

동해연안의 수질특성 및 상태를 파악하기 위하여 2004년부터 2010년까지의 국가해양환경측정망 조사결과를 이용하여 수질인자의 거동을 분석하였다. 본 연구에서는 통계적 방법을 이용한 수질인자간의 상관관계 및 주성분 분석을 통하여 해역별 수질환경 특성을 파악하였으며, OECD의 부영양화 기준과 부영양도, 그리고 유기오염도 지수의 산정으로 해역별 오염상태를 평가하였다. 수질인자간의 주성분 분석에서 동해연안은 클로로필 a와 염분이 주요인자로 설명되는 2개의 요인으로 구분되었다. 해역별로는 죽변을 경계로 남부와 중부로 분류되었으며, 동해 중부 해역에서는 죽변, 그리고 남부해역에서는 감포연안이 별도로 분류되었다. 동해연안의 영양상태는 Oligotrophic~Mesotrophic 수준으로 구분되었으며, 부영양화도는 1 이하로 평가되었다. 유기오염지수는 동해연안 전 해역에서 양호한 수질상태로서 평가되었다.

Keywords

References

  1. 국립수산과학원(2005), 한국해양환경조사연보 2004, 제 9권, 국립수산과학원, 예문사, 부산, p. 400.
  2. 국립수산과학원(2006), 한국해양환경조사연보 2005, 제 10권, 국립수산과학원, 예문사, 부산, p. 400.
  3. 국립수산과학원(2007), 한국해양환경조사연보 2006, 제 11권, 국립수산과학원, 예문사, 부산, p. 396.
  4. 국립수산과학원(2008), 한국해양환경조사연보 2007, 제 12권, 국립수산과학원, 예문사, 부산, p. 408.
  5. 국립수산과학원(2009), 한국해양환경조사연보 2008, 제 13권, 국립수산과학원, 예문사, 부산, p. 400.
  6. 국립수산과학원(2010), 한국해양환경조사연보 2009, 제 14권, 국립수산과학원, 예문사, 부산, p. 422.
  7. 국립수산과학원(2011), 한국해양환경조사연보 2010, 제 15권, 국립수산과학원, 예문사, 부산, p. 434.
  8. 유춘만, 위인선, 이종빈, 위성욱(1999), Scaphechinus brevis의 생물검정에 의한 동해해역 연안해수의 수질평가, 15(1), pp. 127-134.
  9. 이인철(2001), 부영양화해역의 내부생산효율에 대한 계절 변동예측, 한국해양공학회지, 15(4), pp. 53-59.
  10. 최용규, 정희동, 권기영(2010), 2006년 동해연안의 수괴분포, 한국환경과학회지, 19(4), pp. 399-406.
  11. 罔市友利(1972), 內滿赤潮の發生機構-III 淺海の汚染と赤潮の發生", 水産硏究寶書, 제 23권, 日本水産資源保護協會, pp. 58-76.
  12. 李英植, 山田崇央, 淸水徹水徹, 向井徹雄, 瀧本和人, 罔田光正(1996), 廣島灣における植物プランクトンの增殖に對する集中降雨にともなう陸水の影響 水環境學會誌 19(12), pp. 995-1003
  13. Adams, G. and S. Spotte(1980), Effects of tertiary methods on total organic carbon removal in saline, closed-system marine mammal pools, Am. J. Vet. Res., 41, pp. 1470-1474.
  14. Fisher, T. R., E. R. Peele, J. W. Ammerman and L. Harding(1992), Nutrients limitation of phytoplankton in Chesapeake Bay, marine Ecology progress series, 82, pp. 51-63. https://doi.org/10.3354/meps082051
  15. Hakanson, L.(1994), A review of effect-dose sensitivity models for aquatic ecosystems, Internationale Revue der Gesamten Hydrobiologie, 79, pp. 621-667. https://doi.org/10.1002/iroh.19940790412
  16. Nemerow, N. L.(1991), Stream, lake, estuary and ocean pollution, 2nd ed. Van Nostrand Reinhold, New York, pp. 271-286.
  17. Quan, W. M., X. Q. Shen and J. D. Han(2005), Analysis and assessment on eutrophication status and developing trend in Changjiang Estuary and adjacent sea, Marine Environmental Science, 24, (3), pp. 13-16.
  18. Rosenberg, R., H. C. Nilsson and R. J. Diaz(2001), Response of benthic fauna and changing sediment redox profiles over a hypoxic gradient. Estuarine, Coastal and Shelf Science, 53, pp. 343-350. https://doi.org/10.1006/ecss.2001.0810
  19. Redfield, A. C., B. H. Ketchum and F. A. Richards (1963), The influence of organisms on the composition of sea water, In: The Sea, Vol 2, M.H. Hill, ed. Wiley, New York, pp. 26-77.
  20. Styro D., R. Morkuniene and S. Vdovinskiene(2006), The Process of Self-Purification of the Baltic Sea Waters from Artificial Radionuclides, Oceanology, 46, (3), pp. 358-367. https://doi.org/10.1134/S0001437006030076
  21. Swedish EPA(2000): Environmental quality criteria: Coasts and seas. Swedish Environmental Protection Agency Report 5052, Stockholm, Sweden. p. 138.
  22. Vollenweider, R. A. and J. J. Kerekes(1982), Eutrophication of waters, monitoring, assessment and control, OECD, paris, pp. 301-315.
  23. Wang, X. L., Z. G. Cui, Q. Guo and X. R. Han(2009), Distribution of nutrients and eutrophication assessment in the Bohai Sea of China, Chinese Journal of Oceanology and Limnology, 27(1), pp. 177-183. https://doi.org/10.1007/s00343-009-0177-x

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