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  • P-ISSN1225-0163
  • E-ISSN2288-8985
  • SCOPUS, ESCI, KCI

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  • P-ISSN 1225-0163
  • E-ISSN 2288-8985

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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

분석과학 / Analytical Science and Technology, (P)1225-0163; (E)2288-8985
2011, v.24 no.6, pp.484-492
https://doi.org/10.5806/AST.2011.24.6.484
정기호 (부산대학교)
문지용 (부산대학교)
문동호 (환경관리공단)
정기호, 문지용, & 문동호. (2011). 주요 하천 및 호수에 서식하는 붕어(Carassius auratus and Carassius cuvieri) 근육에 축적된 2,3,7,8-치환 PCDDs, PCDFs 및 DL-PCBs분석. 분석과학, 24(6), 484-492, https://doi.org/10.5806/AST.2011.24.6.484
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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.

keywords
PCDDs, PCDFs, DL-PCBs, freshwater fish, carp

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.

keywords
PCDDs, PCDFs, DL-PCBs, freshwater fish, carp


참고문헌

1

1. Stockholm Convention on Persistent Organic Pollutants (POPs), 2004. <http://chm.pops.int/Convention/ThePOPs/tabid/673/language/en-US/Default.aspx>.

2

2. M. J. DeVito, L. S. Birnbaum, W. H. Farland and T. A. Gasiewicz, Environ. Health Perspect., 103, 820-831 (1995).

3

3. B. Birmingham, A. Gilman, D. Grant, J. Salminen, M. Boddington, B. Thorpe, I. While, P. Toft and V. Armstrong, Chemosphere, 19, 637-642 (1989).

4

4. J. Sweetman, R. E. Alcock, J. Wittsiepe and K. C. Jones, Environ. Int., 26, 37-47 (2000).

5

5. US Environmental Protection Agency (USEPA), 2003. Draft Exposure and Human Health Risk Assessment of 2,3,7,8-Tetrachlorodibenzo-p-Dioxin (TCDD) and Related Compounds, Parts I, II, and III. US Environmental Protection Agency, Office of Research and Development, National Center for Environmental Assessment, Exposure Assessment and Risk Characterization Group, Washington, D.C.

6

6. G. H. Jeong, H. J. Kim, J. Y. Moon, S. K. Jeon, C. H. Joo, K. Choi and Y. S. Chang, Chemosphere, 75, 1221-1225 (2009).

7

7. S. Adu-Kumi, M. Kawano, Y. Shiki, P. O. Yoboah, D. Carboo, J. Pwamang, M. Morita and N. Suzuki, Chemosphere, 81, 675-684 (2010).

8

8. L. L. F. Scott, D. F. Staskal, E. S. Williams, W. J. Luksemburg, J. D. Urban, L. M. Nguyen, L. C. Haws, L. S. Birnbaum, D. J. Paustenbach and M. A. Harris, Chemo sphere, 74, 1002-1010 (2009).

9

9. B. Stachel, E. H. Christoph, R. Götz, T. Herrmann, F. Krüger, T. Kühn, J. Lay, J. Löffler, O. Päpke, H. Reincke, C. Schröter-Kermani, R. Schwartz, E. Steeg, D. Stehr, S. Uhlig and G. Umlauf, J. Hazardoud Materials, 148, 199-209 (2007).

10

10. P. Isosaari, A. Hallikainen, H. Kiviranta, P. Vuorinen, R. Parmanne, J. Koistinen and T. Vartiainen, Environ. Pollut., 141, 213-225 (2006).

11

11. US Environmental Protection Agency (USEPA), 2007. National Lake Fish Tissue Study (Online). US Environmental Protection Agency, Office of Water, Office of Science and Technology, Washington, D.C. <http://www.epa.gov/waterscience/fish/study>.

12

12. S. H. Man, I. J. Hodgkiss, 1981. Hong Kong Freshwater Fishes. Urban Council, Wishing Printing Company, Hong Kong, p. 75 <http://www.fishbase.org/References/ FBRefsummary.cfm>.

13

13. W. Naito, J. Jin, Y. S. Kang, M. Yamamuro, S. Masunaga and J. Nakanishi, Chemosphere, 53, 347-362 (2003).

14

14. T. Sakurai, N. Suzuki, S. Masunaga and J. Nakanishi, Chemosphere, 37, 2211-2224 (1998).

15

15. S. Masunaga, T. Takasuga and J. Nakanishi, Chemosphere, 44, 873-885 (2001).

16

16. Y. Kajiwara, N. Kashiwagi and K. Kadokami, Chemosphere, 69, 1177-1187 (2007); Environmental Agency, Japan (EAJ), 1999. Nationwide survey on dioxins in fiscal year 1988 (Japanese). <http://www.env.go.jp/chemi/dioxin/report/result1998/incex.html>.

17

17. EC, 2001. Council Regulation (EC) No 2375/2001 of 29 November 2001 amending Commission Regulation (EC) No 466/2001 setting maximum levels for certain contaminants in foodstuffs. Official Journal of the European Communities L 321:1e5.

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