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Toxic effects of fenvalerate in tadpoles of Fejervarya limnocharis: a multiparametric study.
Das, Indranil; Patar, Arabinda; Singha, Erom Romi; Paul, Sagorika; Singh, Bishal Kumar; Giri, Sarbani; Giri, Anirudha.
Afiliação
  • Das I; Environment and Human Toxicology Laboratory, Department of Life Science and Bioinformatics, Assam University, Silchar, 788011, Silchar, India.
  • Patar A; Environment and Human Toxicology Laboratory, Department of Life Science and Bioinformatics, Assam University, Silchar, 788011, Silchar, India.
  • Singha ER; Environment and Human Toxicology Laboratory, Department of Life Science and Bioinformatics, Assam University, Silchar, 788011, Silchar, India.
  • Paul S; Environment and Human Toxicology Laboratory, Department of Life Science and Bioinformatics, Assam University, Silchar, 788011, Silchar, India.
  • Singh BK; Environment and Human Toxicology Laboratory, Department of Life Science and Bioinformatics, Assam University, Silchar, 788011, Silchar, India.
  • Giri S; Molecular Genetics Laboratory, Department of Life Science and Bioinformatics, Assam University, Silchar, 788011, Silchar, India.
  • Giri A; Environment and Human Toxicology Laboratory, Department of Life Science and Bioinformatics, Assam University, Silchar, 788011, Silchar, India. agiri123@yahoo.com.
Environ Sci Pollut Res Int ; 31(37): 49656-49669, 2024 Aug.
Article em En | MEDLINE | ID: mdl-39080175
ABSTRACT
Pyrethroids are among the most widely used insecticides. Fenvalerate (FEN), a synthetic pyrethroid, is frequently used in domestic and agricultural settings to control insects which ultimately find its way into the aquatic ecosystems. The larval stages of amphibians, which are experiencing a rapid population decline, are spent in aquatic habitats, thus making them vulnerable to FEN exposure. The potential toxic effects of pyrethoids in general and FEN in particular are not well understood. The present study was carried out to assess the toxicity of FEN in tadpoles of Fejervarya limnocharis. FEN at different concentrations (0, 4, 5, 6, 7, and 8 mg/L) induced substantial lethal effects. The estimated LC50 values were 8.54, 6.73, 5.44, and 4.44 mg/L at 24, 48, 72, and 96 h respectively. Exposure to environmentally relevant sub-lethal concentrations delayed metamorphosis and reduced survivality. FEN was found to be genotoxic in erythrocyte micronucleus and comet assay. Further, sub-lethal concentrations of FEN adversely affected the antioxidant defense mechanism of the exposed individuals with parallel increase oxidative damage to membrane lipids. The swimming behavior in the form of startle response, swirl response, and total movements was decreased with a concomitant decrease in AChE activity. In addition, FEN exhibited significant cardiotoxicity by decreasing the cardiac rate of the exposed individuals. The present findings clearly indicate that FEN can cause significant toxicity to the tadpoles of F. limnocharis affecting their survival and fitness in the natural environment.
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Texto completo: 1 Base de dados: MEDLINE Assunto principal: Piretrinas / Inseticidas / Larva / Nitrilas Idioma: En Ano de publicação: 2024 Tipo de documento: Article

Texto completo: 1 Base de dados: MEDLINE Assunto principal: Piretrinas / Inseticidas / Larva / Nitrilas Idioma: En Ano de publicação: 2024 Tipo de documento: Article