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The use of selected biomarkers to determine the effects of veterinary growth stimulants in the Mozambique tilapia (Oreochromis mossambicus)

M.Sc. (Zoology) / There has been an increasing concern worldwide regarding the possible adverse effects of pharmaceutical supplements present in our aquatic ecosystems and whether or not they modify the physiological functioning in humans and wildlife. Trenbolone acetate (TBA) and zeranol (Z) for example, are two commonly used synthetic anabolic growth promoting hormones in cattle production. TBA is metabolized into trenbolone-β and excreted as both trenbolone-α and -β. In liquid manure trenbolone-β has a half-life of over 270 days and Z, 120 days. Therefore if released into the surrounding environment there is the possibility for long-term severe ecological impacts i.e. fish reproduction and general health. The aim of this study was to determine the physiological effects of several growth promoting hormones used as growth promoting hormones in cattle production on the Mozambique Tilapia – Oreochromis mossambicus. The growth promoting hormones assessed in this study were; Trenbolone acetate, Methyltestosterone, Diethylstilbestrol and Zeranol. The aim was accomplished by making use of histology (gills, liver and gonads) and three biomarker assays; Glutathione-S-transferase (GST), Uridine-Diphosphate Glucuronosyltransferase (UDPGT) and Cellular Energy Allocation (CEA). Stock solutions of Trenbolone acetate (14 μg/l and 15 μg/l), Methyltestosterone (7 μg/l and 7.5 μg/l), Zeranol (2.8 μg/l and 3 μg/l) and Diethylstilbestrol (0.28 μg/l and 0.29 μg/l) were prepared. Fish were exposed under controlled conditions for a period of 24-hours, 4-, 15- and 30-days respectively using a flow-through system. The aquarium water was changed (45 L removed and replaced with 45 L of prepared growth hormone containing bore-hole water) every 48 – 72 hours to remove all waste material thus ensuring the aquariums were clean. Upon performing the necropsies, gills, liver and gonads were removed and examined using standard histological techniques. Muscle tissue was used to determine the CEA, liver and kidney tissue was used for both GST and UDPGT assays. The results obtained from the histology revealed that the gills and liver were not severely affected by exposure to the growth promoting hormones although possible exposure related alterations were evident. The gonads results indicated that exposure to the growth promoting hormones severely affected the morphology and functioning of the organs to the point where reproduction is questionable. The results obtained from the hepatosomatic index (HSI) and gonadosomatic index (GSI) revealed no significant differences (p<0.05) although a trend of increasing HSI and decreasing GSI was evident in the male fish exposed to the androgens. With regards to the biomarker assays there were minor decreases in CEA in the exposed fish but no significant differences (p<0.05) could be established. The GST assay revealed that Zeranol prompted a significant increase (p<0.05) in GST activity in the kidney after 4- and 15-days of exposure while the liver displayed no change in GST activity. The UDPGT assay revealed minor fluctuation in UDPGT activity in both the kidney and liver throughout the study, however, no significant differences (p<0.05) could be established. To conclude, exposure to these growth promoting hormones at the selected concentrations and exposure periods severely compromised the fish’s reproductive capabilities thus challenging the fish’s fitness. Further studies examining the energy metabolism and xenobiotic detoxification pathways of the Mozambique tilapia and other indigenous fish species are recommended to better comprehend the effects that these growth promoting hormones may possess.

Identiferoai:union.ndltd.org:netd.ac.za/oai:union.ndltd.org:uj/uj:11659
Date15 July 2014
CreatorsTresise, Michael Marc
Source SetsSouth African National ETD Portal
Detected LanguageEnglish
TypeThesis
RightsUniversity of Johannesburg

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