4.2 Article

Using native fish in eco-genotoxic assessment of heavy metal contamination pollution arising from nearby large Brazilian rivers

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TAYLOR & FRANCIS INC
DOI: 10.1080/15287394.2022.2164754

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Ecotoxicology; biomarkers; Water pollution; Cichlasoma fish; Environmental risk

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Worldwide water quality has worsened due to continuous pollution by agrochemicals, especially heavy metals. Fish genotoxicity biomarkers are important for evaluating the environmental risk of pollutants. In this study, Cichlasoma paranaense fish were used as a model to assess the genotoxic effects of water pollution in Brazilian rivers. Samples from different river sites showed contamination by metals, with the highest concentrations of Cu in areas with forest fragmentation caused by intensive agriculture. The fish exposed to samples from agricultural areas exhibited significantly higher genotoxic effects. The results suggest that C. paranaense fish can serve as a reliable model for detecting genotoxic effects of agrochemicals.
Worldwide water quality has declined progressively due to continuous pollution of aquatic resources by agrochemicals in particular heavy metals. Fish genotoxicity biomarkers are vital to identify and complement chemical parameters for determining environmental risk of adverse effects. Therefore, it was of interest to examine the eco-genotoxicity attributed to water pollution over different stream sections of Brazilian rivers by using Cichlasoma paranaense (Teleostei: Cichlidae), a neotropical freshwater cichlid ?sh, as a biological model. Chemical analysis of water and sediments collected from different Brazilian rivers sites demonstrated contamination by metals. Cichlasoma paranaense were collected at a reference location (a permanent water preservation area), maintained in the lab under standard conditions (controlled temperature, lighting, daily feeding, and constant aeration) and exposed to environmental samples of water and sediments. Subsequently, micronucleus (MN) and nuclear abnormalities (NA) frequencies were assessed in erythrocytes obtained from the caudal and gill regions. The highest concentrations of Cu were found in samples from river sites with forest fragmentation attributed to intensive agriculture practices. Similarly, exposure of fish to samples from agricultural areas induced significantly higher number of genotoxic effects. There was no marked difference between the tissues (tail and gill) regarding the observed frequencies of MN and NA. Thus C. paranaense fish served as a reliable model for detecting genotoxic effects, especially when water samples were collected near the discharge of agrochemicals. Evidence indicates that this method be considered for other global river sites which are also exposed to agrochemicals discharges containing Cu.

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