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      Acute toxicity of the insecticide Imidacloprid and the herbicide 2,4-D in two species of tropical anurans

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          Abstract

          The use of pesticides has notably increased in recent years globally. However, sensitive organisms exposed to these environmental pollutants, such as amphibians, may experience adverse effects. The insecticide imidacloprid (IM) and the herbicide 2,4-dichlorophenoxyacetic acid (2,4-D) are two pesticides commonly used in Colombia, but their toxic impacts on tropical anurans remain poorly understood. In this study, we tested the acute toxic effects of IM and 2,4-D on the survival, total length, and burst swimming speed of tadpoles from two anuran species. Under laboratory conditions, the tadpoles of Boana platanera and Engystomops pustulosus were independently exposed to each pesticide for 96 h. We found that the tadpoles of E. pustulosus were more sensitive to both IM and 2,4-D than those of B. platanera. However, the LC 50 values were higher than the reported field concentrations for these pesticides. IM led to a reduction in the total length of B. platanera tadpoles and induced total immobility in surviving individuals of both species. In contrast, the herbicide 2,4-D did not affect the total length or the swimming speed of tadpoles from the two species. In conclusion, based on the results and the reported field concentrations, IM and 2,4-D are not lethal to the studied anurans. Nevertheless, it is important to consider that IM caused strong negative sublethal effects on tadpoles, which could compromise their survival in the future. Finally, we also found that the insecticide IM showed notably greater toxicity to the tested species than did the herbicide 2,4-D.

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          An international database for pesticide risk assessments and management

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            A simplified table for staging anuran embryos and larvae with notes on identification

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              Neonicotinoid contamination of global surface waters and associated risk to aquatic invertebrates: a review.

              Neonicotinoids, broad-spectrum systemic insecticides, are the fastest growing class of insecticides worldwide and are now registered for use on hundreds of field crops in over 120 different countries. The environmental profile of this class of pesticides indicate that they are persistent, have high leaching and runoff potential, and are highly toxic to a wide range of invertebrates. Therefore, neonicotinoids represent a significant risk to surface waters and the diverse aquatic and terrestrial fauna that these ecosystems support. This review synthesizes the current state of knowledge on the reported concentrations of neonicotinoids in surface waters from 29 studies in 9 countries world-wide in tandem with published data on their acute and chronic toxicity to 49 species of aquatic insects and crustaceans spanning 12 invertebrate orders. Strong evidence exists that water-borne neonicotinoid exposures are frequent, long-term and at levels (geometric means=0.13μg/L (averages) and 0.63μg/L (maxima)) which commonly exceed several existing water quality guidelines. Imidacloprid is by far the most widely studied neonicotinoid (66% of the 214 toxicity tests reviewed) with differences in sensitivity among aquatic invertebrate species ranging several orders of magnitude; other neonicotinoids display analogous modes of action and similar toxicities, although comparative data are limited. Of the species evaluated, insects belonging to the orders Ephemeroptera, Trichoptera and Diptera appear to be the most sensitive, while those of Crustacea (although not universally so) are less sensitive. In particular, the standard test species Daphnia magna appears to be very tolerant, with 24-96hour LC50 values exceeding 100,000μg/L (geometric mean>44,000μg/L), which is at least 2-3 orders of magnitude higher than the geometric mean of all other invertebrate species tested. Overall, neonicotinoids can exert adverse effects on survival, growth, emergence, mobility, and behavior of many sensitive aquatic invertebrate taxa at concentrations at or below 1μg/L under acute exposure and 0.1μg/L for chronic exposure. Using probabilistic approaches (species sensitivity distributions), we recommend here that ecological thresholds for neonicotinoid water concentrations need to be below 0.2μg/L (short-term acute) or 0.035μg/L (long-term chronic) to avoid lasting effects on aquatic invertebrate communities. The application of safety factors may still be warranted considering potential issues of slow recovery, additive or synergistic effects and multiple stressors that can occur in the field. Our analysis revealed that 81% (22/27) and 74% (14/19) of global surface water studies reporting maximum and average individual neonicotinoid concentrations respectively, exceeded these thresholds of 0.2 and 0.035μg/L. Therefore, it appears that environmentally relevant concentrations of neonicotinoids in surface waters worldwide are well within the range where both short- and long-term impacts on aquatic invertebrate species are possible over broad spatial scales.
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                Author and article information

                Contributors
                tmtrianav@ut.edu.co
                Journal
                Ecotoxicology
                Ecotoxicology
                Ecotoxicology (London, England)
                Springer US (New York )
                0963-9292
                1573-3017
                1 February 2025
                1 February 2025
                2025
                : 34
                : 3
                : 392-400
                Affiliations
                Grupo de Herpetología, Eco-Fisiología & Etología, Departamento de Biología, Universidad del Tolima, ( https://ror.org/011bqgx84) Ibagué, Colombia
                Author information
                http://orcid.org/0000-0001-7798-2514
                http://orcid.org/0000-0003-0940-4514
                Article
                2843
                10.1007/s10646-024-02843-y
                11910441
                39893353
                4210b9f5-b123-4049-89d2-c9627c96bc8e
                © The Author(s) 2025

                Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.

                History
                : 28 November 2024
                Funding
                Funded by: FundRef http://dx.doi.org/10.13039/100022965, Ministerio de Ciencia, Tecnología e Innovación;
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                © Springer Science+Business Media, LLC, part of Springer Nature 2025

                Toxicology
                amphibians,lc50,pesticides,sublethal effects,toxicity
                Toxicology
                amphibians, lc50, pesticides, sublethal effects, toxicity

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