NRC Postdoctoral Research Fellow with the U.S. Environmental Protection Agency, Athens, GA 30605, USA.
Departments of Biology and Environmental Science & Studies, Washington College, Chestertown, MD 21620, USA.
Sci Total Environ. 2021 Jul 20;779:146358. doi: 10.1016/j.scitotenv.2021.146358. Epub 2021 Mar 11.
Pesticides are being applied at a greater extent than in the past. Once pesticides enter the ecosystem, many environmental factors can influence their residence time. These interactions can result in processes such as translocation, environmental degradation, and metabolic activation facilitating exposure to target and non-target species. Most anurans start off their life cycle in aquatic environments and then transition into terrestrial habitats. Their time in the aquatic environment is generally short; however, many important developmental stages occur during this tenure. Post-metamorphosis, most species spend many years on land but migrate back to the aquatic environment for breeding. Due to the importance of both the aquatic and terrestrial environments to the life stages of amphibians, we investigated how the route of exposure (i.e., uptake from contaminated soils vs. uptake from contaminated surface water) influences pesticide bioavailability and body burden for four pesticides (bifenthrin (BIF), chlorpyrifos (CPF), glyphosate (GLY), and trifloxystrobin (TFS)) as well as the impact on the hepatic metabolome of adult leopard frogs (Gosner stage 46 with 60-90 days post-metamorphosis). Body burden concentrations for amphibians exposed in water were significantly higher (ANOVA p < 0.0001) compared to amphibians exposed to contaminated soil across all pesticides studied. Out of 80 metabolites that were putatively identified, the majority expressed a higher abundance in amphibians that were exposed in pesticide contaminated water compared to soil. Ultimately, this research will help fill regulatory data gaps, aid in the creation of more accurate amphibian dermal uptake models and inform continued ecological risk assessment efforts.
农药的使用范围比过去更广。一旦农药进入生态系统,许多环境因素都会影响它们的停留时间。这些相互作用可能导致转移、环境降解和代谢激活等过程,从而使目标和非目标物种暴露在其中。大多数无尾两栖动物从水生环境开始其生命周期,然后过渡到陆地栖息地。它们在水生环境中的时间通常很短;然而,许多重要的发育阶段都发生在这个阶段。变态后,大多数物种在陆地上生活多年,但为了繁殖会迁移回水生环境。由于水生和陆地环境对两栖动物生命阶段都很重要,我们研究了暴露途径(即从受污染的土壤中摄取与从受污染的地表水摄取)如何影响四种农药(联苯菊酯(BIF)、毒死蜱(CPF)、草甘膦(GLY)和三氟甲磺隆(TFS))的生物利用度和体内负荷,以及对成年豹蛙(Gosner 阶段 46,变态后 60-90 天)肝脏代谢组的影响。暴露在水中的两栖动物的体内负荷浓度明显高于(ANOVA p < 0.0001)暴露在受污染土壤中的两栖动物,所有研究的农药均如此。在假定鉴定的 80 种代谢物中,大多数在暴露于受农药污染的水中的两栖动物中的丰度更高,而不是在土壤中。最终,这项研究将有助于填补监管数据空白,帮助创建更准确的两栖动物皮肤吸收模型,并为持续的生态风险评估工作提供信息。