원유의 노출이 담치와 조피볼락의 phase II 약물대사효소 UDP-glucoronosyl transferase 및 glutathione S-transferase의 활성에 미치는 영향

Activity Changes in Phase II Drug-metabolizing Enzymes UDP-Glucoronosyl Transferase and Glutathione S-Ttansferase to Crude Oil Exposure in Mussel and Rockfish

  • 박관하 (군산대학교 해양과학대학 수산생명의학과 및 식품공학과) ;
  • 김주완 (군산대학교 해양과학대학 수산생명의학과 및 식품공학과) ;
  • 박음미 (군산대학교 해양과학대학 수산생명의학과 및 식품공학과) ;
  • 임철원 (군산대학교 해양과학대학 수산생명의학과 및 식품공학과) ;
  • 최민순 (군산대학교 해양과학대학 수산생명의학과 및 식품공학과) ;
  • 최선남 (군산대학교 해양과학대학 수산생명의학과 및 식품공학과) ;
  • 황인영 (인제대학교 자연과학대학 환경공학부) ;
  • 김정상 (경북대학교 농업생명과학대학 동물공학과)
  • Park Kwan-Ha (Departments of Aquatic Life Medicine and Food Science & Engineering, Kunsan National University) ;
  • Kim Ju-Wan (Departments of Aquatic Life Medicine and Food Science & Engineering, Kunsan National University) ;
  • Park Eum-Mi (Departments of Aquatic Life Medicine and Food Science & Engineering, Kunsan National University) ;
  • Lim Chul-Won (Departments of Aquatic Life Medicine and Food Science & Engineering, Kunsan National University) ;
  • Choi Min-Soon (Departments of Aquatic Life Medicine and Food Science & Engineering, Kunsan National University) ;
  • Choe Sun-Nam (Departments of Aquatic Life Medicine and Food Science & Engineering, Kunsan National University) ;
  • Hwang In-Young (School of Environmental Science & Engineering, Inje University) ;
  • Kim Jung-Sang (Department of Animal Science & Biotechnology, Kyungpook National University)
  • 발행 : 2006.06.01

초록

This study examined effects of crude oil on the phase II drug-metabolizing enzymes UDP-glucuronosyl transferase (UDPGT) and glutathione S-transferase (GST) in mussel Mytilus edulis and rockfish Sebastes schlegeli, a representative bivalve and a culture fish, respectively. This work also intended indirectly to evaluate the post impact recovery from the massive oil tanker spillage accidents occurred during the summer of 1995 in the sea area off Yosu City, Chonnam. For these, enzyme activities of UDPGT and GST were examined in the fish and mussel following laboratory exposure to fresh crude oil, weathered oil, field-obtained oil residues, or in the field biota samples. Decreased GST activity was observed in rock fish following exposure to oil-soluble fraction (OSF) of fresh oil. A similar diminished GST activity was also observed after OSF of artificially weathered oil. OSF of field oil residues retrieved from the spillage area approximately 1 year later also exerted a slight inhibition of GST to rockfish. There was neither a change in UDPGT in rockfish, nor were there changes in mussel in both enzymes to any oil fractions. We could not observe any difference in the two enzymes either in rockfish or mussel sampled from the field during $1.5{\sim}2.0$ years post spillage, indicating that their enzyme systems might had been recovered by the sampling time. In conclusion, it seems that the inhibition of GST activity in rockfish is a biomarker response to crude oil exposure. The results, however, must be interpreted with care, as the inhibition nay reflect various factors such as oil concentration, duration and water temperature.

키워드

참고문헌

  1. Arif JM, Khan SG, Mahmood N, Aslam M and Rahman Q. Effect of coexposure to asbestos and kerosene soot on pulmonary drug-metabolizing enzyme system. Environ Health Perspect 1994; 102: 181-183 https://doi.org/10.1289/ehp.94102s5181
  2. Bobra AM, Shiu WY, MacKay D and Goodman RH. Acute toxicity of dispersed fresh and weathered crude oil and dispersants to Dapnhia magna. Chemosphere 1989; 19: 1199-1222 https://doi.org/10.1016/0045-6535(89)90068-4
  3. Clark AG. The comparative enzymology of the glutathione S-transferases from non-vertebrate organisms. Comp. Biochem. Physiol. 1989; B92: 419-446
  4. Collier TK, Krone CA, Krahn MM, Stein JE, Chan S-L and Varanasi U. Petroleum exposure and associated biochemical effects in subtidal fish after the Exxon Valdez oil spill. Am Fish Soc Symp 1996; 18: 671-683
  5. Collodi P, Stekoll MS and Rice SD. Hepatic aryl hydrocarbon hydroxylase activities in coho salmon (Oncorhynchus kisutch) exposed to petroleum hydrocarbons. Comp Biochem Physiol 1984; 97C: 447-341
  6. Croce B and Stagg RM. Exposure of Atlantic salmon parr (Salmo salar) to a combination of resin acids and a water soluble fraction of diesel fuel oil: a model to investigate the chemical causes of pigmented salmon syndrome. Environ Toxicol 1997; 9: 1921-1929
  7. Cunha I, Garcia LM and Guilhermino L. Sea-urchin (Paracentrotus lividus) glutathione S-transferase and cholineraterase activities as biomarkers of environmental contamination. J Environ Monit 2005; 7: 288-294 https://doi.org/10.1039/b414773a
  8. Da Silva AZ, Zanette J, Fernando-Ferreira J, Guzenski J, Marques MR and Bainy AC. Effects of salinity on biomarker responses in Crassostrea rhizophorae (Mollusca, Bivalvia) exposed to diesel oil. Ecotoxicol Environ Saf 2005; 62: 376-382 https://doi.org/10.1016/j.ecoenv.2004.12.008
  9. Gagnon MM and Holdway DA. MFO induction in Atlantic salmon (Salmo salar) during and after exposure to Bass Strait crude oil. Aus J Ecotox 1998; 4: 29-35
  10. Gagnon MM and Holdway DA. EROD induction and biliary metabolite excretion following exposure to the water accommodated fraction of crude oil and to chemically dispersed crude oil. Arch Environ Contam Toxicol 2000; 38: 70-772 https://doi.org/10.1007/s002449910009
  11. Georgiades ET, Danis B, Gillan DC, Dubois Ph., Temara A and Holdway DA. Effect of crude oil contaminated sediment exposure on cytochrome P450 enzymes in the Auatralian asteroid Coscinasterias muricata. Chemesphere, in press
  12. Habig WH, Pabst MJ and Jacoby WB. Glutathione transferases: The first enzymatic step in mercapturic acid formation. J Biol Chem 1974; 249: 7130-7139
  13. Heras H, Ackman RG and MacPherson EJ. Tainting of Atlantic salmon (Salmo salar) by petroleum hydrocarbons during a short-term exposure. Mar Poll Bull 1992; 24: 310-315 https://doi.org/10.1016/0025-326X(92)90592-T
  14. Khan S, Rahman AM, Payne JF and Rahimtula AD. Mechanisms of petroleum hydrocarbon toxicity: studies on the response of rat liver mitochondria to Prudhoe Bay crude oil and its aliphatic, aromatic and hetrocyclic fractions. Toxicology 1986; 42: 131-1422 https://doi.org/10.1016/0300-483X(86)90004-1
  15. Krahn MM, Rhodes LD, Myers MS, Moore LK, MacLeod WD Jr and Malins DC. Association between metaboliters of aromatic compounds in bile and the occurrence of hepatic lesions in English sole (Paophyrus vetulus) from Puget Sound, Washington. Arch Environ Contam Toxicol 1986; 15: 61-76 https://doi.org/10.1007/BF01055249
  16. Lee RF and Anderson JW. Significance of cytochrome P450 system responses and level of bile fluorescent aromatic compounds in marine wildlife following oil spills. Mar Poll Bull 2005; 50: 705-723 https://doi.org/10.1016/j.marpolbul.2005.04.036
  17. Lindstrom-Seppa P. Biomonitoring of oil spill in a boreal archipelago by xenobiotic biotransfomation in perch (Perca fluviatilis). Ecotoxicol Environ Saf 1988; 15: 161-170
  18. Moreira SM, Moreira-Santos M, Ribeira R and Giulhermino L. The 'Coral Bulker' fuel oil spill on the north coast of Portugal: spatial and temporal biomarker responses in Mytilus galloprovincialis. Ecotoxicology 2004; 13: 619-630 https://doi.org/10.1007/s10646-003-4422-3
  19. Neff JM. Composition and fate of petroleum and sill-treating agents in the marine environment. In: Geraci JR and St. Aubin DJ (eds) Sea mammals and oil: confronting the risks. Academic Press, London, 1990; pp. 1-12
  20. Neff JM and Anderson JW. Responses of marine animals to petroleum and specific petroleum hydrocarbons. Applied Science Publishers, Essex, 1981; 177pp
  21. Nusetti O, Zapata-Vivenes E, Esclapes MM and Rojas A. Antioxidant enzymes and tissue regeneration in Eurythoe complanata (Polychaeta: Amphinomidae) exposed to used vehicle crankcase oil. Arch Envion Contam Toxicol 2005; 48: 509-514 https://doi.org/10.1007/s00244-004-0041-0
  22. Payne JR, Phillips CR and Hom W. Transport and transformations: Water column processes. In: Boesch DF and Rabalais NN (eds). Long-term environmental effects of offshore oil and gas development. Elsevier Applied Publishers, London, 1987; pp. 175-231
  23. Peters LD, Shaw JP, Nott M, O'Hara SCM and Livingstone DR. Development of cytochrome P450 as a biomarker of organic pollution in Mytilus sp.: Field studies in United Kingdom (Sea Empress's oil spill) and the Mediterranean Sea. Biomarkers 1999; 4: 425-441 https://doi.org/10.1080/135475099230598
  24. Raja H, Qureshi MM and Montague W. Alteration, glutathione S-transferase and lipid peroxidation in mouse skin and extracutaneous tissues after topical application of gasoline. Int J Biochem Cell Biol 1995; 27: 271-277 https://doi.org/10.1016/1357-2725(95)93663-I
  25. Saeed T and Al-Mutairi M. Comparative composition of polycyclic aromatic hydrocarbons (PAHs) in the sea water-soluble fractions of different Kuwaiti crude oil. Adv Environ Res 2000; 4: 141-145 https://doi.org/10.1016/S1093-0191(00)00018-6
  26. Siron R, Giusti G, Berland B, Morales-Loo R and Pelletier E. Water-soluble petroleum compounds: chemical aspects and effects on the growth of microalgae. Sci Total Environ 1991; 104: 211-227 https://doi.org/10.1016/0048-9697(91)90073-N
  27. Stromgren T. Effect of oil and dispersants on the growth of mussels. Mar Environ Res 1987; 21: 239-246 https://doi.org/10.1016/0141-1136(87)90048-1
  28. Thomas RE and Rice SD. Excretion of aromatic hydocarbons and their metabolites by freshwater and seawater Dolly Varden char. In: Verbnberg FJ, Calabrese A, Thurberg F and Venberg W (eds) Biological monitoring of marine pollutants. Academic Press, New York, NY, 1981; pp. 425-448