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Analysis of polycyclic aromatic hydrocarbons in cooked fish and shellfish

조리어패류 중 다환방향족탄화수소 분석

  • Hu, Soojung (New Hazard Chemical Division, Korea Food & Drug Administration) ;
  • Park, Sungkuk (New Hazard Chemical Division, Korea Food & Drug Administration) ;
  • Jin, Sunhee (New Hazard Chemical Division, Korea Food & Drug Administration) ;
  • Choi, Dongmi (New Hazard Chemical Division, Korea Food & Drug Administration)
  • 허수정 (식품의약품안전청 신종유해물질과) ;
  • 박성국 (식품의약품안전청 신종유해물질과) ;
  • 진선희 (식품의약품안전청 신종유해물질과) ;
  • 최동미 (식품의약품안전청 신종유해물질과)
  • Received : 2009.01.07
  • Accepted : 2009.01.21
  • Published : 2009.02.25

Abstract

The following concentrations of some PAHs were investigated; [benzo(a)anthracene, chrysene, benzo (b)fluoranthene, benzo(k)fluoranthene, benzo(a)pyrene, dibenzo(a,h)anthracene, benzo(g, h, i)perylene, indeno (1,2,3-c,d)pyrene] in fish(n=168) and shellfish(n=40). The methodology involved saponification and extraction with n-hexane, clean-up on Sep-Pak Florisil Cartridges and determination by HPLC/FLD (High Performance Liquid Chromatograph/Fluorescence Detector). Overall method recoveries for 8 PAHs spiked into these products ranged from 88 to 112%. The mean level of benzo(a)anthracene, chrysene, benzo(b)fluoranthene, benzo(k) fluoranthene, benzo(a)pyrene, dibenzo(a,h)anthracene, benzo(g,h,i)perylene and indeno(1,2,3-c,d)pyrene in cooked fish was ND, ND, 0.0009, ND, 0.01, ND, ND, ND and in cooked shellfish was 1.84, 3.51, 0.81, 0.38, 0.39, 0.04, 0.20, ND, respectively.

조리 어패류 중 8종의 PAHs 실태파악을 위하여 어류 168건, 패류 40건을 분석하였다. 시료를 알칼리분해하여 n-hexane으로 추출하고 세척한 후 Sep-Pak Florisil Cartridge로 정제하여 HPLC/FLD로 정량 분석하였다. 각각의 PAHs에 대한 회수율은 약 88~112%였다. 조리어류에서 개별 PAH 평균 농도는 benzo(a)anthracene 불검출, chrysene 불검출, benzo(b)fluoranthene $0.0009{\mu}g/kg$, benzo(k)fluoranthene 불검출, benzo(a)pyrene $0.01{\mu}g/kg$, dibenzo(a,h)anthracene 불검출, benzo(g,h,i)perylene 불검출, indeno(1,2,3-c,d) pyrene 불검출이었다. 조리패류에서 개별 PAH 평균 농도는 benzo(a)anthracene $1.84{\mu}g/kg$, chrysene $3.51{\mu}g/kg$, benzo(b)fluoranthene $0.81{\mu}g/kg$, benzo(k)fluoranthene $0.38{\mu}g/kg$, benzo(a)pyrene $0.39{\mu}g/kg$, dibenzo(a,h)anthracene $0.04{\mu}g/kg$, benzo(g,h,i)perylene $0.20{\mu}g/kg$, indeno(1,2,3-c,d)pyrene 불검출이었다.

Keywords

References

  1. R. Dabestani and I. N. Ivanov, Photochemical. Phorobiology., 41, 10-17, 1999
  2. T. Vo-Dinh, J. Fetzer and A. D. Campiglia, Talant., 47, 943-951, 1998 https://doi.org/10.1016/S0039-9140(98)00162-3
  3. 식품공전, 식품의약품안전청, 2008
  4. 제3기 국민건강영양조사, 보건복지부, 2006
  5. 허수정, 이효민, 채영주, 유은아, 분석과학, 18(5), 403-409(2005)
  6. 허수정, 김미혜, 오남수, 하진, 최광식, 권기성, 한국식품과학, 37(6), 866-872(2005)
  7. Commission. Directive 2005/10/EC of 4 February, European Commission, 2005 (http://ec.europa.eu/food/efsa_en.htm)
  8. U.S. EPA Method TO-13A Polycyclic Aromatic Hydrocarbons, U.S. EPA, 1999
  9. K. Takatsuki, S. Suzuki, N.i Sato and I. Ushizawa, J. ASSOC. OFF. ANAL. CHEM., 68(5), 945-949(1985)
  10. A. Stolyhwo and Z. E. Sikorski, Food Chemistry, 91, 303-311(2005) https://doi.org/10.1016/j.foodchem.2004.06.012
  11. I. Noh and K. S. Lee, Marine Science and Technology, 9, 121-134(2000)
  12. U.S. Department of Health and Human Servies, Toxicological Profiles for Polycyclic Aromatic Hydrocarbons, USA, 1995
  13. I. Vives, J. O. Grimalt, P. Fernandez and B. Rosseland, Science of the Total Environment, 324, 67-77(2004) https://doi.org/10.1016/j.scitotenv.2003.10.026
  14. R. J. Law and J. A. Whinnett, Marine Pollution Bull., 24(11), 550-553(1992) https://doi.org/10.1016/0025-326X(92)90707-D
  15. P. Simko, Journal of Chromatography B, 770, 3-18 (2002) https://doi.org/10.1016/S0378-4347(01)00438-8