Animal Research International (2005) 2(1): 231 – 234 231EFFECT OF EXPOSURE TO SUBLETHAL CONCENTRATIONS OF GAMMALIN20 AND ACTELLIC 25 EC ON THE LIVER AND SERUM LACTATEDEHYDROGENASE ACTIVITY IN THE FISH Clarias albopunctatusOLUAH, Ndubuisi Stanley, EZIGBO, Joseph Chukwura and ANYA, Nnenna CatherineFisheries and Hydrobiology Research Unit, Department of <strong>Zoo</strong>logy, University of Nigeria, NsukkaCorresponding Author: OLUAH, N. S. Fisheries and Hydrobiology Research Unit, Department of <strong>Zoo</strong>logy,University of Nigeria, NsukkaABSTRACTOne hundred and eighty adult Clarias albopunctatus (mean weight 160±2.7g) were subjectedto sublethal concentrations of Gammalin 20 and Actellic 25 EC (0, 0.3;and 1.0 µg/l) in a staticbioassay renewal system for 18 days. The changes in the activities of the liver and serumlactate dehydrogenase (LDH) during the period of exposure were studied. The exposure of C.albopunctatus to these pesticides evoked significant increase (P< 0.05) in both the liver andserum LDH activities. There was a progressive increase in both the liver and serum LDHactivities following exposure to the pesticides. When compared with the control, the LDHactivities were significantly higher (p < 0.05) in the treatment groups. The LDH activities inboth the liver and the serum were higher in the fish exposed to Gammalin 20 than in the fishtreated with similar concentrations of Actellic 25 EC. The serum LDH activity in the groupexposed to a mixture of 0.3µg/l of Gammalin 20 and Actellic 25 EC was significantly higherthe activities in the fish exposed the either 0.3 µg/l Gammalin 20 or Actellic 25 EC. Theseobservations suggest that these pesticides affect the energy metabolism of the fish.Keywords: Clarias, Liver, Serum, Lactate dehydrogenase, Gammalin 20, Actellic 25 ECINTRODUCTIONActellic 25 EC is an <strong>org</strong>anophosphorous pesticidealso known as Primiphos-methyl. It is a broadspectrumpesticide against stored product pests(Worthing and Hance, 1991). On the other hand,Gammalin 20, a widely applied pesticide in Nigeria,is an <strong>org</strong>anochloride pesticide containing 20 %lindane. The application of pesticides, either foragricultural purposes or for the control of pests ofpublic health interests, contaminates theenvironment or hence endangers the non-target<strong>org</strong>anisms in both terrestrial and aquatic habitats.The value of tissue enzyme activities inthe diagnosis of the effects of pollutants is one ofthe emerging areas of interest in aquatictoxicology, monitoring and remediationprogrammes. Thirugnam and F<strong>org</strong>ash (1977)studied the anticholinesterase effect of chlorpyrifosto the fish Fundulus heteroclistis. Increasedglucose-6-phosphatase and glycogenphosphorylase activities were observed in Cyprinuscarpio exposed to paraquat (Simon et al., 1983).Also, Rashatwar and Ilyas (1983), noted thatBasalin, a herbicide affected the activities oflactate dehydrogenase, alkaline phosphatase aswell as glutamic pyruvate transaminase in thefreshwater fish Nemachelinus sp. Increasedactivities of alanine and aspartateaminotransferases were reported in Claraisalbopunctatus exposed to copper (Oluah andAmalu, 1998), zinc and mercury (Oluah, 1999).Verma et al. (1981) observed that pesticidesinhibited alkaline phosphatase and glucose-6-phosphatase activities in the fish Mytulus vittatus.The purpose of this study was toinvestigate the effect of the pesticides - Actellic 25EC and Gammalin 20, widely used in Nigeria, onthe activities of liver and serum lactatedehydrogenases in the catfish, Clariasalbopunctatus.MATERIALS AND METHODSThe one hundred and eighty fish (mean weight110 ± 2.6 g) used in the study was collected fromAnambra River at Otuocha, Anambra East LocalGovernment Area of Nigeria. The fish wastransported to our laboratory in a plastic containerand was acclimatized for two weeks in plasticaquaria before the commencement of the study.The fish were divided randomly into six(6) groups (1 – 6) of 30 fish per group. Eachgroup was further divided into three replicategroups of 10 fish per replicate. The fish in group Iwere exposed to tap water only as the controlwhile the fish in groups 2 and 3 were treated with0.3 µg/l and 1.0 µg/l of Actellic 25 EC,respectively. Groups 4 and 5 were exposed to 0.3µg/l and 1.0 µg/l Gammalin 20, respectively. The6 th group was exposed to a mixture of equalconcentrations (0.3 µg/l) of Actellic 25 EC and
OLUAH, Ndubuisi Stanley et al. 232Gammalin 20.The fish were exposed to thesesublethal concentrations of the pesticide in arenewal bioassay system in which the water andthe pesticides were changed every two days tomaintain the toxicant concentrations. The fishwere fed 30 % crude protein diet at 3% bodyweight daily at 8.00 h. The Experiment lasted for18 days and the lactate dehydrogenase activitywas assayed every six days.Tissue Collection and Enzyme Assay: Theblood samples were collected by both the cardiacpuncture method and the severance of the caudalpeduncle using the disposable hypodermic syringe(Oluah, 1999). The liver was excised and washedin distilled water to remove traces of blood. Theliver samples were macerated and homogenized asdescribed by Devi et al. (1993). The liver washomogenized in ice-cold 0.25 M sucrose. The liverhomogenate was centrifuged at 5000 rpm for 15minutes at 4 o C.The blood was similarly centrifugedfor 15 minutes at 1000 rpm to obtain the serum.The liver supernatant and serum were used for thelactate dehydrogenase (LDH) assay. The lactatedehydrogenase activity was calorimetricallydetermined at 445 nm using Sigma protocolnumber 500 (Sigma Chemical Company, St Louis,MO). The data from the replicate experimentswere averaged and the mean (± SD) presented.The analysis of variance (ANOVA) was used toanalyze the data for statistical significance (P
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EYO, Joseph Effiong 286Cyprinidae,