The present study was conducted to assess the toxicity of thermal power plant effluent containing heavy metals (Fe > Cu > Zn > Mn > Ni > Co > Cr) on haematological indices, micronuclei, lobed nuclei and activity of pathological marker enzymes [alkaline phosphatase (ALP), aspartate transferase (AST), alanine transferase (ALT) and creatine kinase (CK)] in Channa punctatus. Total erythrocyte count (−54.52 %), hemoglobin (−36.98 %), packed cell volume (−36.25 %), mean corpuscular hemoglobin concentration (−1.41 %) and oxygen (O2) carrying capacity (−37.04 %) declined significantly over reference fish, however total leukocyte count (+25.43 %), mean corpuscular hemoglobin (+33.52 %) and mean corpuscular volume (+35.49 %) showed elevation. High frequency of micronuclei (1133.3 %) and lobed nuclei (150 %) were observed in exposed fish which may indicate mutagenesis. Activities of pathological marker enzymes ALP, AST, ALT and CK increased significantly in serum of exposed fish. The ratio of ALT: AST in exposed fish was beyond 1 which indicates manifestation of pathological processes. These biomarkers show that fish have macrocytic hypochromic anemia. Leukocytosis showed general defence response against heavy metal toxicity and marker enzymes showed tissue degeneration. In conclusion, thermal power plant effluent has strong potential to induce micronuclei, tissue pathology, making the fish anemic, weak, stressed and vulnerable to diseases.

Pendimethalin (PND) is a systemic herbicide widely used on rice, cotton, peas, wheat, potatoes, fruits, nuts and other residential and non-residential crops; however, it concurrently exerts toxic effects on beneficial organisms like earthworms, aquatic invertebrates and other non-targeted animals including humans. Most likely, the genotoxicity of agrochemicals/drugs is modulated through cellular distribution of bound DNA. Therefore, the in vitro interaction of PND with calf thymus DNA (ctDNA) has been investigated using various sensitive biophysical techniques to ascertain its binding mechanism. UV-visible absorption and fluorescence spectra suggested the formation of a complex between PND and ctDNA. The binding constant of the PND–ctDNA complex was found to be around 10⁴ M⁻¹ using steady state fluorescence titration. The calculated positive values of enthalpy and entropy changes suggested that the binding reaction was predominantly driven by hydrophobic interactions. Competitive displacement studies using acridine orange (AO), ethidium bromide (EB) and Hoechst dye suggested intercalation of PND molecules into the double helix of ctDNA by replacing the bound AO and EB probes. An increase in the viscosity and melting temperature of ctDNA and a decrease in iodine-quenching also support the intercalative binding of PND with ctDNA. Molecular docking analysis further confirmed the specific binding mode of PND between adjacent ‘G–C’ base pairs of ctDNA.