IJSTR

International Journal of Scientific & Technology Research

Home About Us Scope Editorial Board Contact Us
CONTACT

IJSTR >> Volume 1 - Issue 10, November 2012 Edition



International Journal of Scientific & Technology Research  
International Journal of Scientific & Technology Research

Website: http://www.ijstr.org

ISSN 2277-8616



Impact of Nanoparticle On Enzymes Activity In Oreochromis Mossambicus

[Full Text]

 

AUTHOR(S)

M. Karthigarani, Dr. P. S. Navaraj

 

KEYWORDS

Key words: TiO2 nanoparticles; tilapia; sub-acute toxicity; oxidative stress, antioxidant enzymes.

 

ABSTRACT

Abstract: Toxicity of Titanium dioxide nanoparticles (TiO2-NPs) to freshwater fish, Oreochromis mossambicus is assessed in this work. The endpoint of this study has focussed the disturbances in the vital enzyme profile of fish exposed to TiO2-NPs. Superoxide dismutase (SOD), Catalase (CAT), Peroxidase (POD) and Lipid per Oxidation (LPO) levels in brain, gill and liver tissues of tilapia were analysed and observed that these values were concentration and duration dependent. The results obtained in this study have projected a statistically significant decrease (P < 0.05) in SOD, CAT and POD activities and an increase (P < 0.05) in LPO levels in selected tissues of fish exposed to 50, 100 and 150 ppm TiO2-NPs. Further, this finding suggests that there is an oxidative stress in fish. Moreover, the depletion of antioxidant enzymes activities and the elevation of LPO in liver tissue are higher indicating that the liver might be the most susceptible organ to TiO2-NPs exposure. Thus hepatotoxicity is underlined in this work.

 

REFERENCES

[1] Beauchamp C, Fridovich I, 1971. Superoxide dismutase: improved assays and an assay applicable to acrylamide gels. Analytical Biochemistry, 44: 276–287.

[2] Federici G, Shaw BJ, Handy RD. 2007. Toxicity of titanium dioxide nanoparticles to rainbow trout (Oncorhynchus mykis): Gill injury, oxidative stress, and other Physiological effects. Aqua. Toxicol 84:415-430, 2007.

[3] Hussain, S. M., K. L. Hess, J. M. Gearhart, K. T. Geiss, and J. J. Schlager. 2005. In vitro toxicity of nanoparticles in BRL 3Arat liver cells. Toxicology in Vitro 19(7): 975–983.

[4] Kong X H, Wang G Z, Li S J, 2007. Antioxidation and ATPase activity in the gill of mud crab Scylla serrata under cold sress. Chinese Journal of Oceanology and Limnology, 25(2): 221–226.

[5] Lin, W., Y. Huang, X. Zhou, and Y. Ma. 2006. Toxicity of cerium oxide nanoparticles in human lung cancer cells. International Journal of Toxicology 25(6): 451–457.

[6] Lockman, P. R., J. M. Koziara, R. J. Mumper, and D.D. Allen. 2004. Nanoparticle surface charges alter blood-brain barrier integrity and permeability. Journal of Drug Targeting 12(9-10): 635–641.

[7] Oberdorster E, 2004. Manufactured nanomaterials (fullerenes, C60) induce oxidative stress in the brain of juvenile Largemouth Bass. Environmental Health Perspectives, 112: 1058–1062.

[8] Pane, E. F., A. Haque, and C. M. Wood. 2004. Mechanistic analysis of acute,Ni-induced respiratory toxicity in the rainbow trout (Oncorhynchus mykiss): An exclusively branchial phenomenon. Aquatic Toxicology 69(1): 11–24.

[9] Rombough, P. J. and B. M. Moroz. 1997. The scaling and potential importance of cutaneous and branchial surfaces in respiratory gas exchange in larval and juvenile walleye Stizostedion vitreum. Journal of Experimental Biology 200(18): 2459–2468.

[10] Sayeed I, Parvez S, Pandey S, Bin-Hafeez B, Haque R, Raisuddin S, 2003. Oxidative stress biomarkers of exposure to deltamethrin in freshwater fish, Channa punctatus Bloch. Ecotoxicology and Environmental Safety, 56: 295–301.

[11] Sayes CM, Fortner LD, Guo W, Lyon D, Boyd AM, Ausman KD, et al. The differential cytotoxicity of water soluble fullerenes. Nanoletters 4:1881-1887, 2004.

[12] Silva, G. A. 2007. Nanotechnology approaches for drug and small molecule delivery across the blood brain barrier. Surgical Neurology 67(2): 113–116.

[13] Smedsrud T, Dannevig BH, Tolleshaug H, Berg T. Endocytosis of a mannose terminated glycoprotein and formaldehyde-treated human serum albumin in liver and kidney cells from fish (salmo alpinus L.). Dev Comp Immunol 8:579-588, 1984.

[14] Tsuji, J. S., A. D. Maynard, P. C. Howard, J. T. James, C. Lam, D. B. Warheit, and A. B. Santamaria. 2006. Research strategies for the evaluation of nanomaterials, part IV: Risk assessment of nanoparticles. Toxicological Sciences 89(1): 42– 50.

[15] Tyson, J. MamacCrmack and Greg G. Goss 2008 .Identifying and Predicting Biological Risks Associated With Manufactured Nanoparticles in Aquatic Ecosystems. Journal of Industrial Ecology 12(3): 286-296.

[16] Vander O R, Beyer J, Vermeulen N P E, 2003. Fish bioaccumulation and biomarkers in environmental risk assessment: A review. Environmental Toxicology and Pharmacology, 13: 57–149.

[17] Zhu, X et al.; Acute toxicities of six manufactured nanomaterial suspensions to Daphnia magna. Journal of Nanoparticle Research, 2009, Vol 11, Number 1, pg 67-75.

[18] Zhu X S, Zhu L, Lang Y P, Chen Y S, 2008b. Oxidative stress and growth inhibition in the freshwater fish Carassius Auratus induced by chronic exposure to sublethal fullerene aggregates. Environmental Toxicology and Chemistry, 27(9): 1979–1985.

[19] Zhu X S, Zhu L, Li Y, Duan Z H, Chen W, Alvarez P J J, 2007. Developmental toxicity in zebrafish embryos after exposure to manufactured nanomaterials: Buckminsterfullerene aggregates (nC60) and fullerol. Environmental Toxicology and Chemistry, 26: 976–979