IMBECU   20882
INSTITUTO DE MEDICINA Y BIOLOGIA EXPERIMENTAL DE CUYO
Unidad Ejecutora - UE
congresos y reuniones científicas
Título:
Acute toxicity of the herbicide Maleic Hydrazide to the tadpoles of Bufo arenarum Hensel, 1867
Autor/es:
MAMANI MORENO C.; BURBA J.L.; STADLER T.
Lugar:
Ribeirão Preto, Sao Paulo, Brasil
Reunión:
Congreso; 1st Ibero-American Meeting On Toxicology And Environmental Health; 2009
Resumen:
Introduction: Maleic hydrazide (CAS: 1,2-dihydro-3,6-pyridazinedione) (MH), is widely used as a plant growth retardant, applied as a foliar spray for control of undesired sprouting of potatoes, carrots, garlic, etc. during storage. Bufo arenarum is a natural inhabitant in South American agricultural ecosystems, commonly found in irrigation water tanks, drainage channels and ditches. As much of the MH application is likely to coincide with the aquatic larval phase of B. arenarum, tadpoles can be exposed to MH through spray drift and contaminated water. Given the important roles B. arenarum plays in aquatic and terrestrial food webs, investigating the effects of MH residues on this organism is environmentally relevant. Objective: The aim of this study was to evaluate the acute toxicity of MH in immature forms of B. arenarum. Methodology: Toxicity tests were conducted by exposing groups of ten tadpoles in 96-h static bioassays to concentrations of 0.005; 0.01; 0.05; 0.1; 0.12; 0.14; 0.16; 0.18; and 0.20 g/L MH and using three replicates per treatment. Mortality was assessed once every 15 minutes in the first hour and after 2, 12, 24, 48, 72 and 96 hours. Tadpole mortality was used as bioassay endpoint and malformations in bioassay surviving tadpoles and young frogs were recorded for up to 38 days after treatment. The dose-response data were analyzed by using a probit procedure. Results: Tadpoles of B. arenarum responded in a concentration-dependent manner to increasing concentrations of waterborne MH and mortality occurred always within the first 30 minutes of exposure. The estimated 96 h LC50 of MH was 0.118 g/L and the calculated NOEC was 0.08g/L. Morphological abnormalities in bioassay surviving tadpoles and young frogs were not observed. Conclusion: Exposure of amphibian tadpoles to varying concentrations of MH resulted in mortality. Toxicity was observed even with concentrations that were smaller than those used in agricultural ecosystems. Thus, chemical pollution from MH could be one of the causes for the decline of amphibian populations.