A common tire additive of N-(1,3-dimethylbutyl)-N′-phenyl-p-phenylenediamine (6PPD) is frequently detected in freshwater. To date, the toxicity of 6PPD to aquatic organisms has mainly been based on partial life-cycle test results. However, it remains unclear whether this approach leads to an underestimation of the true environmental risk of 6PPD. Here, the effects of environmentally relevant or greater concentrations of 6PPD on the reproduction and growth of Daphnia magna were specifically compared between day 21 and the day all the maternal daphnia died, with the underlying toxic mechanisms of 6PPD also explored. 6PPD at environmental or near-natural water concentrations (5.68 and/or 9.20 µg/L) significantly decreased the total number of offspring and net reproductive rate after whole-life-stage exposure. However, such adverse effects were not observed on day 21, indicating that environmental levels of 6PPD exerted reproductive toxicity on D. magna, and short-term exposure may underestimate the environmental risk of 6PPD. Elevated malondialdehyde levels in the 5.68, 9.20 and 44.58 µg/L treatment groups, coupled with reactive oxygen species (ROS) emerging as the dominant contributors to the biomarker response index, indicated that ROS overproduction induced by 6PPD triggered lipid peroxidation despite antioxidant capacity was enhanced. Downregulation of the vitellogenin expression in D. magna exposed to 5.68, 9.2 and 44.58 µg/L 6PPD, likely resulting from competitive binding to ecdysteroid receptor based on molecular docking and molecular dynamics simulation, might compromise nutrient provisioning during embryogenesis. Coupled with oxidative stress, these dual mechanisms appeared to mediate 6PPD-induced reproductive toxicity.
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