본문 바로가기
KERD
논문KCI 등재

주요 하천 및 호수에 서식하는 붕어(Carassius auratus and Carassius cuvieri) 근육에 축적된 2,3,7,8-치환 PCDDs, PCDFs 및 DL-PCBs분석

Analysis of 2,3,7,8-substituted PCDDs, PCDFs, and DL-PCBs in muscle of crucian carp (Carassius auratus and Carassius cuvieri) from major rivers and lakes

2

조회

0

다운로드

0

인용

0

참고문헌

키워드

주제분류화학

초록

우리나라 주요 하천수계의 대표적인 지점 한 곳씩 선정하여 이곳에 서식하는 붕어에 대한 PCDDs,PCDFs 및 DL-PCBs의 체내 축적 정도를 분석하고 분포특성을 살펴보았다. 회수율은 PCDDs 및 PCDFs 는 50.6%~88.3%, DL-PCBs는 52.3%~93.2%이었으며, 붕어 체내에 축적된 PCDDs, PCDFs 및 DL-PCBs 를 모두 합한 Σdioxins은 평균 0.39 pg TEQ g^(−1) wet wt., 중앙값 0.14 pg TEQ/g wet wt., 그리고 농도 범위는 0.047-1.0 pg TEQ/g wet wt.으로 나타났다. PCDDs 및 PCDFs는 일부 시료에서 검출된 반면, DLPCBs는모든 시료에서 검출되었으며 Σdioxins에 대한 기여도가 83.6%로서 가장 높았다. 다음으로 PCDFs 와 PCDDs가 각각 Σdioxins의 12.7%와 3.7%를 기여하고 있었다.

Abstract

Bioaccumulation status and distribution characteristics of PCDDs, PCDFs and DL-PCBs in cruian carp collected from the four representative sites of major river systems in Korea were investigated. The recovery rates of PCDDs and PCDFs ranged from 50.6% to 88.3%, and those of DL-PCBs ranged from 52.3% to 93.2%. The mean, median and concentration range of Σdioxins, which represents the total concentratons of PCDDs,PCDFs and DL-PCBs accumulated in the muscle of crucian carp, were 0.39, 0.14 and 0.047-1.0 pg TEQ/g wet wt., respectively. DL-PCBs were detected above the detection limit from all the samples, whereas PCDDs and PCDFs were detected from limited crucian samples. The relative contribution of DL-PCBs to Σdioxins was remarkably larger than those for PCDDs and PCDFs. The percent contribution was 83.6% for DL-PCBs,and followed by 12.7% and 3.7% for PCDFs and PCDDs, respectively.

참고문헌 (17)

  1. "Stockholm Convention on Persistent Organic Pollutants (POPs)"[URL]
  2. M. J. DeVito, , Environ. Health Perspect, 103, pp.820~831 (1995)
  3. B. Birmingham, , Chemosphere, 19, pp.637~642 (1989)
  4. J. Sweetman, , Environ. Int, 26, pp.37~47 (2000)
  5. US Environmental Protection Agency (USEPA), "Draft Exposure and Human Health Risk Assessment of 2,3,7,8-Tetrachlorodibenzo-p-Dioxin (TCDD) and Related Compounds, Parts I, II, and III" (2003), US Environmental Protection Agency, Office of Research and Development, National Center for Environmental Assessment, Exposure Assessment and Risk Characterization Group
  6. G. H. Jeong, , Chemosphere, 75, pp.1221~1225 (2009)
  7. S. Adu-Kumi, , Chemosphere, 81, pp.675~684 (2010)
  8. L. L. F. Scott, , Chemosphere, 74, pp.1002~1010 (2009)
  9. B. Stachel, , J. Hazardoud Materials, 148, pp.199~209 (2007)
  10. P. Isosaari, , Environ. Pollut, 141, pp.213~225 (2006)
  11. "National Lake Fish Tissue Study (Online). US Environmental Protection Agency, Office of Water, Office of Science and Technology, Washington, D.C"[URL]
  12. S. H. Man, "Hong Kong Freshwater Fishes", pp.75~ (1981), Urban Council, Wishing Printing Company
  13. W. Naito, , Chemosphere, 53, pp.347~362 (2003)
  14. T. Sakurai, , Chemosphere, 37, pp.2211~2224 (1998)
  15. S. Masunaga, , Chemosphere, 44, pp.873~885 (2001)
  16. Y. Kajiwara, , Chemosphere, 69, pp.1177~1187 (2007)
  17. EC, "Council Regulation (EC) No 2375", 2001 of 29 November 2001 amending Commission Regulation (EC) No 466, Official Journal of the European Communities L, pp.2001 (2001), 321[DOI]

관련 논문AI추천

이 간행물의 다른 논문 (17건)