Assessment of biological effects of pollutants in a hyper eutrophic tropical water body, Lake Beira, Sri Lanka using multiple biomarker responses of resident fish, Nile tilapia (Oreochromis niloticus)
Abstract:Biomarkers measured at the molecular and cellular level in fish have been proposed as sensitive "early warning" tools for biological effect measurements in environmental quality assessments. Lake Beira is a hypertrophic urban water body with a complex mixture of pollutants including polycyclic aromatic hydrocarbons (PAHs) and Microcystins. In this study, a suite of biomarker responses viz. biliary fluorescent aromatic compounds (FACs), hepatic ethoxyresorufin O-deethylase (EROD) and glutathione S-transferase (… Show more
“…Histopathological biomarkers are valuable as early indicators of the biological damage in fish as they reflect the effects of exposure to a variety of anthropogenic pollutants (Pathiratne et al 2010;Kumar et al 2017). The liver is the main site of biotransformation of foreign chemicals that enter the fish body.…”
Section: Resultsmentioning
confidence: 99%
“…Erythrocytic micronuclei and nuclear abnormalities in fish are cellular level biomarkers for assessing genotoxic effects (Al-Sabti and Metcalfe 1995;Pathiratne 2016, 2017). The liver is a vital organ and analysis of liver histological alterations in fish can be used as a tissue level biomarker for assessing organ damage (Pathiratne et al 2010;Ghisi et al 2016;Kumar et al 2017).…”
Biomarkers can be considered as early warning signals for potential adverse effects on the biota. The present study examined the feasibility of using selected biomarker responses of a model fish, Oreochromis niloticus under laboratory exposure approach for identification of potential biological impacts of pollution in Kelani River. Laboratory acclimated O. niloticus were exposed under static-renewal conditions to water samples collected from selected sites of the Kelani River basin with different anthropogenic influences and biomarker responses (brain and muscle cholinesterase activities for neurotoxicity, erythrocyte micronuclei and nuclear abnormalities for genotoxicity and liver histology for hepatic damage) were evaluated at 5 and 10 days of exposure. Exposed water was physico-chemically characterized using standard analytical methods. The results revealed that exposure of O. niloticus to the water from selected polluted sites which included canals and canal confluences resulted in significant increases (p<0.05) in total erythrocyte nuclear abnormalities, evolution of erythrocyte micronuclei and induction of liver histopathological indices in comparison to the fish exposed to the water from the upper reach of the river (reference site) in most cases and the control fish exposed to the aged tap water in all cases. Brain cholinesterase activity was significantly inhibited (p<0.05) in the fish exposed to the water from the most polluted site compared to the control fish exposed to the aged tap water. Biomarker responses indicated that the fish populations inhabiting the polluted sites in the river may be under stress especially due to hepatic damage and genotoxicity. Evaluation of "effect directed biomarker responses" of the model fish, O. niloticus following laboratory exposure to the contaminated water can be a practically feasible approach for biomonitoring potential pollution impacts associated with the riverine ecosystems.
“…Histopathological biomarkers are valuable as early indicators of the biological damage in fish as they reflect the effects of exposure to a variety of anthropogenic pollutants (Pathiratne et al 2010;Kumar et al 2017). The liver is the main site of biotransformation of foreign chemicals that enter the fish body.…”
Section: Resultsmentioning
confidence: 99%
“…Erythrocytic micronuclei and nuclear abnormalities in fish are cellular level biomarkers for assessing genotoxic effects (Al-Sabti and Metcalfe 1995;Pathiratne 2016, 2017). The liver is a vital organ and analysis of liver histological alterations in fish can be used as a tissue level biomarker for assessing organ damage (Pathiratne et al 2010;Ghisi et al 2016;Kumar et al 2017).…”
Biomarkers can be considered as early warning signals for potential adverse effects on the biota. The present study examined the feasibility of using selected biomarker responses of a model fish, Oreochromis niloticus under laboratory exposure approach for identification of potential biological impacts of pollution in Kelani River. Laboratory acclimated O. niloticus were exposed under static-renewal conditions to water samples collected from selected sites of the Kelani River basin with different anthropogenic influences and biomarker responses (brain and muscle cholinesterase activities for neurotoxicity, erythrocyte micronuclei and nuclear abnormalities for genotoxicity and liver histology for hepatic damage) were evaluated at 5 and 10 days of exposure. Exposed water was physico-chemically characterized using standard analytical methods. The results revealed that exposure of O. niloticus to the water from selected polluted sites which included canals and canal confluences resulted in significant increases (p<0.05) in total erythrocyte nuclear abnormalities, evolution of erythrocyte micronuclei and induction of liver histopathological indices in comparison to the fish exposed to the water from the upper reach of the river (reference site) in most cases and the control fish exposed to the aged tap water in all cases. Brain cholinesterase activity was significantly inhibited (p<0.05) in the fish exposed to the water from the most polluted site compared to the control fish exposed to the aged tap water. Biomarker responses indicated that the fish populations inhabiting the polluted sites in the river may be under stress especially due to hepatic damage and genotoxicity. Evaluation of "effect directed biomarker responses" of the model fish, O. niloticus following laboratory exposure to the contaminated water can be a practically feasible approach for biomonitoring potential pollution impacts associated with the riverine ecosystems.
“…GPx, glutathione‐S‐transferase (GST), free radicals and peroxides play a central role in the defence mechanisms against many xenobiotics and carcinogens (Data, Sinha & Chattopadhyay ). Further studies addressing changes in antioxidant and detoxification enzymes such as GPx and GST activities and gene expression of these markers would elucidate mechanisms of action in the antioxidant defence system alterations in tilapia (Pathiratne, Pathiratne & De Seram ; Puerto, Gutierrez‐Praena, Prieto, Pichardo, Jos, Miguel‐Carrasco, Vazquez & Camean ). We found that liver GSH levels were unchanged after DBP exposure during 24 and 96 h in all groups ( P > 0.05, Table ).…”
Section: Resultsmentioning
confidence: 99%
“…GSH is an important intracellular tripeptide with diverse functions, ranging from antioxidant protection to regulation of cell proliferation. Further studies addressing changes in antioxidant and detoxification enzymes such as GPx and GST activities and gene expression of these markers would elucidate mechanisms of action in the antioxidant defence system alterations in tilapia (Pathiratne, Pathiratne & De Seram 2010;Puerto, Gutierrez-Praena, Prieto, Pichardo, Jos, Miguel-Carrasco, Vazquez & Camean 2011). Further studies addressing changes in antioxidant and detoxification enzymes such as GPx and GST activities and gene expression of these markers would elucidate mechanisms of action in the antioxidant defence system alterations in tilapia (Pathiratne, Pathiratne & De Seram 2010;Puerto, Gutierrez-Praena, Prieto, Pichardo, Jos, Miguel-Carrasco, Vazquez & Camean 2011).…”
Section: Tissue Lipid Peroxidation and Glutathione As Oxidative Stresmentioning
Phthalates such as di-n-butyl phthalate (DBP) and their esters are widely used plasticizers, their ubiquitous presence in daily life, inevitably leads to their restricted use due to important environmental pollution and health impacts and endocrine disruption potential. The aim of this study was to examine the effects of a sublethal concentration of 10 mg L À1 DBP on haematocrit (HCT) values, gills and liver histology, malondialdehyde (MDA, 2-thiobarbituric acid-TBA reactivity) and reduced glutathione (GSH) levels in gills and liver tissue as oxidative stress biomarkers in the aquaculture fish species Nile tilapia (Oreochromis niloticus) after 24 (DBP-24) and 96 (DBP-96) h exposure. No differences were found between per cent HCT values in the 24 h exposure groups (P > 0.05). Response of antioxidant defence systems in liver and gill tissues of the fish were dependent on exposure duration and changed to a higher extent during 96 h. MDA levels in liver tissue increased in DBP treated fish in comparison to the control fish. However, the differences between the exposure and control groups were not significant (P > 0.05). A statistically significant decrease (P > 0.05) was recorded in gill MDA levels in the DBP-96 group when compared to the control and DBP-24 groups. The liver GSH levels were unchanged in the DBP treated fish. However, GSH levels were significantly lower in the gill tissue of the DBP-96 group. Exposure to DBP caused several degenerative changes in the histology of gill and liver tissue. Gills displayed hyperaemia, epithelial lifting, oedema, talengiectasia, epithelial hyperplasia and fusion of secondary lamellae, whereas in liver several circulatory anomalies (hyperaemia, blood congestion and sinosoid dilatation) and vacuolization of hepatocytes were observed. Histopathological results demonstrated that the gills were more affected than the liver perhaps due to their direct contact with DBP.
“…The ICD, which utilizes NADP + is present in large amounts in the liver, cardiac/skeletal muscle and kidney tissues, and alterations in its serum levels have been reported to be both sensitive and specific to injuries of hepatic parenchymal cells. SDH is mainly found in the liver, though it is also present in low levels in kidney, brain, heart and spleen tissues (46,47). Therefore, serum SDH levels may serve as a sensitive and specific biomarker for predicting liver injury.…”
Section: Time -------------------------------------------------------mentioning
Drug-induced liver injury (DILI) is a common hepatic disease. The identification of biomarkers for DILI prediction is critical for rational drug use. The aim of the present study was to investigate liver injury caused by binaprofen and identify proteins that may serve as early biomarkers to predict DILI. For in vivo DILI assays, zebrafish were exposed to acetaminophen (APAP) and binaprofen for 12-96 h before lethal concentration 50 (LC 50), histopathological analysis, conventional and non-conventional biomarker measurements were conducted. In vitro assays were performed in cultured liver cells; after 6-24 h treatment with APAP and binaprofen the same measurements were conducted as aforementioned. The in vivo assays indicated that the LC 50 of APAP was 5.2 mM, whereas the LC 50 of binaprofen was 1.2 mM; 12-48 h post-treatment, liver cells exhibited mild to moderate vacuolization in a time-and concentration-dependent manner in response to both drugs. During this time, conventional and non-conventional biomarkers were also altered in a time-and concentration-dependent manner; however, alterations in the levels of non-conventional biomarkers occurred at an earlier time point compared with conventional biomarkers. The in vitro assays indicated that the half maximal inhibitory concentration (IC 50) of APAP was 16.2 mM, whereas the IC 50 of binaprofen was 5.3 mM; 12-48 h post-treatment, cultured liver cells exhibited mild to moderate swelling in a time-and concentration-dependent manner. Alterations in the levels of conventional and non-conventional biomarkers were similar to those observed in the in vivo assays. As a non-steroidal anti-inflammatory drug, binaprofen exhibited expected levels of liver toxicity in in vitro and in vivo assays, which were similar to APAP. Total bile acid and argininosuccinate lyase were identified as early biomarkers, which could accurately predict onset of binaprofen-induced liver injury.
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