Abstract

Semi-static bioassay experiment was conducted to ascertain Butrylacetycholinesterase enzyme activity in liver and plasma, liver glycogen and plasma glucose content, haematology as well as behaviour of Clarias gariepinus (mean weight 24.52±1.64 g) to varying concentrations (0, 0.4, 0.8, 1.6 mg L -1 ) of Dichlorvos for 96 hours. Butrylacetycholinesterase activity in liver was significantly (P <0.05) inhibited all through the exposure duration to 0.4, 0.8 and 1.6 mg L -1 of DDVP compared with control group of fish. Similarly, plasma BuChE activity was inhibited all through the exposure duration to 1.6 mg L -1 DDVP compared to control. There was a significant (P <0.05) inhibition in HB, RBC and MCV of exposed fish after 24,48, 72 and 96h to 1.6 mg L -1 DDVP compared to the control but PCV and WBC were significantly elevated after 72 and 96h to 1.6 mg L -1 DDVP compared to the control. Plasma cortisol and liver glycogen were significantly inhibited after 72 and 96 h to 0.8 and 1.6 mg L -1 compared to the control but plasma glucose was elevated after 24, 48, 72 and 96 h exposure to 0.4, 0.8 and 1.6 mg L -1 compared to the control group of fish. The 96 h LC 50 of DDVP to the exposed fish was found to be 0.66 mg L − 1 with safety value estimated to be 0.01 mg L -1 while lower and upper confidence limits gave 0.29 and 1.49 mg L − 1 , respectively. The 96 h LT 50 values for 0.8 and 1.6 mg L -1 was shown to be 79.23 and 60.26 hours with safety values of 3.98 and 3.01 hours respectively. WBC value was inversely related to HB (r=-0.997, p <0.05, RBC (r=-0.999, p <0.05) and PCV (r=-0.953, p <0.05). RBC related positively to HB (r=0.998 and PCV (r=0.959), and inversely to MCH (r=-0.996) and MCHC (r=0.995). Plasma BuChE activity related positively to PCV (r=0.979) and inversely to MCHC (r=-0.995 and TBF (r=984). Liver BuChE related positively with plasma BuChE (r=0.978), plasma cortisol (r= 0.970) and liver glycogen (r= 0.975) and inversely to TBF (r=-0.998). Changes in BuChE activity may serve as surrogate information for projecting potential hazards in the health status of C. gariepinus.

Highlights

  • Majority of insecticides used today in many developing countries are organophosphorus insecticides (Ops) including dichlorvos which were developed as a substitute for nicotine (Costa, 1987) because of IJAFAS – An Open Access Journal (ISSN 2348-5132)their relatively nonpersistent characteristics in the environment

  • At 0.8 mg L−1 and 1.6 mg L−1 of DDVP, 60% and 90% mortalities respectively were observed in exposed fish (Table 2, Figure 2) while no mortality was recorded in the control group

  • The present study has demonstrated that organophosphate insecticides available in aquatic ecosystem can elicit various damages to freshwater fish in aquatic environment

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Summary

Introduction

Majority of insecticides used today in many developing countries are organophosphorus insecticides (Ops) including dichlorvos which were developed as a substitute for nicotine (Costa, 1987) because of IJAFAS – An Open Access Journal (ISSN 2348-5132). Their relatively nonpersistent characteristics in the environment. Secondary response occurs as a consequence of the released stress hormone causing changes in the blood and tissue chemistry (Babujanarthanam et al, 2010) such as increase in plasma glucose (Begg and Pankhurst, 2004). The present study was designed to determine butrylacetycholinesterase enzyme activity in liver and plasma, liver glycogen and plasma glucose content, haematology and behaviour of C. gariepinus to Dichlorvos

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