پیوندهای مفید
آمار
| تعداد نشریات | 31 |
| تعداد شماره‌ها | 748 |
| تعداد مقالات | 7,112 |
| تعداد مشاهده مقاله | 10,245,980 |
| تعداد دریافت فایل اصل مقاله | 6,899,753 |
Impact of silver nanoparticles on hepatic enzymes and thyroid hormones in striped catfish, Pangasianodon hypophthalmus (Pisces: Pangasiidae) | ||
| Caspian Journal of Environmental Sciences | ||
| دوره 18، شماره 3، مهر 2020، صفحه 265-275 اصل مقاله (1.09 M) | ||
| نوع مقاله: Research Paper | ||
| شناسه دیجیتال (DOI): 10.22124/cjes.2020.4138 | ||
| نویسندگان | ||
| Saleh Ghazanfari1؛ Ruhollah Rahimi* 1؛ Rasool Zamani-Ahmadmahmoodi1؛ Ali Momeninejad2؛ Amirreza Abed-Elmdoust3 | ||
| 1Department of Fisheries and Environmental Sciences, Faculty of Natural Resources and Earth Sciences, Shahrekord University, Shahrekord, Iran | ||
| 2Shahid Momeni Nejad Ornamental Fish Education and Research Center, Qom, Iran | ||
| 3Department of Fisheries Sciences, Faculty of Natural Resources, University of Tehran, Karaj, Iran | ||
| چکیده | ||
| Nanotechnology is the exploitation of physical, chemical, and biological characteristics of the particles with less than 100 nanometers in size. The most of the produced nanoparticles (56%) are composed of silver. The high consumption of these materials in industry and household products has led to their frequent release in aquatic ecosystems. The median lethal concentration (LC50) and the impact of silver nanoparticles on liver enzymes (ALP, LDH, AST, ALT) and thyroid hormones (T4 and T3) in Pangasius hypophthalamus wereinvestigated in the present study in three steps: At first, OECD (The Organization for Economic Cooperation and Development) protocols were used to determine the fatal levels of the silver nanoparticles (Ag NPs) in striped catfish. Second, semi-lethal concentration was found as 37.32 µg L-1 via regression test. In the last step, 168 fish received 0, 3.37, 7.46, 18.66 µg l-1 Ag NPs with three replicate. Six fish were randomly selected after 14 days from each replicate. Whole fish body extraction was used to measure the liver enzymes and thyroid hormones. The results suggested that due to the lower LC50 of Ag NPs in striped catfish, this species is more susceptible compared to various other fish species. Exposure to the silver nanoparticles with different concentrations significantly increased the levels of liver enzymes (ALP, LDH, AST, ALT) and also significantly decreased the T3, but no effect on T4. | ||
| کلیدواژه‌ها | ||
| Silver nanoparticles؛ Pangasianodon hypophthalmus؛ LC50؛ Liver enzymes؛ Thyroid hormones | ||
| مراجع | ||
|
Afkhami-Ardakani, M, Shirband, A, Golzade, J, Asadi-Samani, M, Latifi, E, Kheylapour, M & Jafari, N 2013, The effect of iron oxide nanoparticles on liver enzymes (ALT, AST and ALP), thyroid hormones (T3 and T4) and TSH in rats. Journal of Shahrekord Uuniversity of Medical Sciences, 14 (6): 82-88. Aldrin, J, Messager, J & Laurencin, FB 1982, Clinical biochemistry in aquaculture. Interest and perspective. CNEXO (Actes de Colloques), 14: 291-326.
Arora, S, Jain, J, Rajwade, J & Paknikar, K 2008, Cellular responses induced by silver nanoparticles: in vitro studies. Toxicology letters, 179: 93-100.
Bar‐Ilan, O, Albrecht, RM, Fako, VE & Furgeson, DY 2009, Toxicity assessments of multisized gold and Ag NPs in zebrafish embryos. Small, 5: 1897-1910.
Bilberg, K, Døving, KB, Beedholm, K & Baatrup, E 2011. Silver nanoparticles disrupt olfaction in Crucian carp (Carassius carassius) and Eurasian perch (Perca fluviatilis). Aquatic Toxicology, 104: 145-152.
Borm, PJ, Robbins, D, Haubold, S, Kuhlbusch, T, Fissan, H, Donaldson, K & Lademann, J 2006, The potential risks of nanomaterials: a review carried out for ECETOC. Particle and Fibre Toxicology, 3: 11.
Cabaud, PG., Wróblewski, F & Ruggiero, V 1958, Colorimetric measurement of lactic dehydrogenase activity of body fluids. American Journal of Clinical Pathology, 30: 234-236.
Carew, AC, Hoque, ME, Metcalfe, CD, Peyrot, C, Wilkinson, KJ & Helbing, CC 2015, Chronic sublethal exposure to silver nanoparticles disrupts thyroid hormone signaling during Xenopus laevis metamorphosis. Aquatic Toxicology, 159: 99-108.
Carletta, M, Weis, P & Weis, J 2002, Development of thyroid abnormalities in mummichogs, Fundulus heteroclitus, from a polluted site. Marine Environmental Research, 54: 601-604.
Chae, YJ, Pham, CH, Lee, J, Bae, E, Yi, J & Gu, MB 2009, Evaluation of the toxic impact of silver nanoparticles on Japanese medaka (Oryzias latipes). Aquatic Toxicology, 94: 320-327.
Chen, X & Schluesener, HJ 2008, Nanosilver: a nanoproduct in medical application. Toxicology Letters, 176: 1-12.
Choi, O 2009, Effect of silver nanoparticles on planktonic and biofilm cell growth. PhD Dissertation, Faculty of the Graduate School at the University of Missouri-Columbia, Columbia.
Christ-Crain, M, Huber, PR, Keller, U, Meier, C, Müller, B, Puder, J & Staub, JJ 2004. Changes in liver function correlate with the improvement of lipid profile after restoration of euthyroidism in patients with subclinical hypothyroidism. Experimental and Clinical Sciences, 3:1-9.
Clark, NJ, Shaw, BJ, & Handy, RD 2018, Low hazard of silver nanoparticles and silver nitrate to the haematopoietic system of rainbow trout. Ecotoxicology and Environmental Safety, 152: 121-131.
Directive, C 1967, Council Directive 67/548/EEC of 27 June 1967 on the approximation of laws, regulations and administrative provisions relating to the classification, packaging and labelling of dangerous substances. Official Journal of the European Communities, 196: 1.
Du, J, Wang, S, You, H & Liu, Z 2016, Effects of ZnO nanoparticles on perfluorooctane sulfonate induced thyroid-disrupting on zebrafish larvae. Journal of Environmental Sciences, 47: 153-164.
Farkas, J, Christian, P, Gallego-Urrea, JA, Roos, N, Hassellöv, M, Tollefsen, KE & Thomas, KV 2011), Uptake and effects of manufactured silver nanoparticles in rainbow trout (Oncorhynchus mykiss) gill cells. Aquatic Toxicology, 101: 117-125.
Fırat, Ö, Cogun, HY, Yüzereroğlu, TA, Gök, G, Fırat, Ö, Kargin, F & Kötemen, Y 2011, A comparative study on the effects of a pesticide (cypermethrin) and two metals (copper, lead) to serum biochemistry of Nile tilapia, Oreochromis niloticus. Fish Physiology and Biochemistry, 37: 657-666.
Gill, S, Löbenberg, R, Ku, T, Azarmi, S, Roa, W & Prenner, EJ 2007, Nanoparticles: characteristics, mechanisms of action, and toxicity in pulmonary drug delivery—a review. Journal of Biomedical Nanotechnology, 3: 107-119.
Griffitt, RJ, Luo, J, Gao, J, Bonzongo, JC & Barber, DS 2008, Effects of particle composition and species on toxicity of metallic nanomaterials in aquatic organisms. Environmental Toxicology and Chemistry: An International Journal, 27: 1972-1978.
Guyton, AC & Hall, JE 2012, Pocket companion to Guyton and Hall textbook of medical physiology: Elsevier Health Sciences., p 1120.
Hedayati, A, Shaluei, F & Jahanbakhshi, A 2012, Comparison of toxicity responses by water exposure to silver nanoparticles and silver salt in common carp (Cyprinus carpio). Global Veterinaria, 8: 179-184.
Hori, TSF, Avilez, IM, Inoue, LK & Moraes, G 2006, Metabolical changes induced by chronic phenol exposure in matrinxã Brycon cephalus (teleostei: characidae) juveniles. Comparative Biochemistry and Physiology Part C: Toxicology & Pharmacology, 143: 67-72.
Imani, M, Halimi, M & Khara, H 2015, Effects of silver nanoparticles (AgNPs) on hematological parameters of rainbow trout, Oncorhynchus mykiss. Comparative Clinical Pathology, 24: 491-495.
Johari, S, Kalbassi, M, Soltani, M & Yu, I 2013, Toxicity comparison of colloidal silver nanoparticles in various life stages of rainbow trout (Oncorhynchus mykiss). Iranian Journal of Fisheries Sciences, 12: 76-95.
Johari, S, Asghari, S & Yu, I 2016, Toxicity of various silver nanoparticles compared to silver ions in the Ponto-Caspian amphipod Pontogammarus maeoticus (Sowinsky, 1894). Caspian Journal of Environmental Sciences. 14(1): 249-258.
Khan, MS, Jabeen, F, Qureshi, NA, Asghar, MS, Shakeel, M & Noureen, A 2015, Toxicity of silver nanoparticles in fish: a critical review. Journal of Biodiversity and Environmental Sciences, 6: 211-227.
Kolayli, S & Keha, E 1999, A comparative study of antioxidant enzyme activities in freshwater and seawater‐adapted rainbow trout. Journal of Biochemical and Molecular Toxicology, 13: 334-337.
Lasagna-Reeves, C, Gonzalez-Romero, D, Barria, M., Olmedo, I, Clos, A., Ramanujam, VS, Urayama, A, Vergara, L, Kogan, MG & Soto, C 2010, Bioaccumulation and toxicity of gold nanoparticles after repeated administration in mice. Biochemical and Biophysical Research Communications, 393: 649-655.
Lee, B, Duong, CN, Cho, J, Lee, J, Kim, K, Seo, Y, Kim, P, Choi, K & Yoon, J 2012, Toxicity of citrate-capped silver nanoparticles in common carp (Cyprinus carpio). BioMed Research International, 2012: 1-14.
Monfared, A. L & Soltani, S 2013, Effects of silver nanoparticles administration on the liver of rainbow trout (Oncorhynchus mykiss): histological and biochemical studies. European Journal of Experimental Biology, 3: 285-289.
Nemcsok, J & Benedeczky, I 1990, Effect of sublethal concentrations of phenol on some enzyme activities and blood sugar level of carp (Cyprinus carpio L.). Environmental Monitoring and Assessment, 14: 377-383.
Tugulea, A. M, Bérubé, D, Giddings, M, Lemieux, F, Hnatiw, J, Priem, J & Avramescu, M. L 2014, Nano-silver in drinking water and drinking water sources: stability and influences on disinfection by-product formation. Environmental Science and Pollution Research, 21: 11823–11831. | ||
|
آمار تعداد مشاهده مقاله: 1,091 تعداد دریافت فایل اصل مقاله: 1,021 |
||