We can't find the internet
Attempting to reconnect
Something went wrong!
Hang in there while we get back on track
Adverse Effects of Polystyrene Microplastic Exposure on Daphnia magna: a Comprehensive Assessment of Acute Toxicity, Behavioral Changes, and Oxidative Stress
Summary
Comprehensive toxicity testing of polystyrene microplastics on Daphnia magna showed that 1-µm particles were most toxic (48-h LC50: 23.57 mg/L), reducing swimming speed and feeding behavior while triggering oxidative stress markers including elevated malondialdehyde. These behavioral and biochemical endpoints serve as sensitive early-warning biomarkers for ecological risk, highlighting how nanoscale plastics impair the zooplankton that form the base of aquatic food webs.
Microplastics (MPs) pollution has emerged as a pressing environmental concern. In this study, we comprehensively evaluated the adverse effects of polystyrene microplastic (PSMP) on Daphnia magna, focusing on acute toxicity, behavioral changes, and oxidative stress responses. Exposure experiments demonstrated that the acute toxicity of PSMP (1, 6.5, and 50 µm in size) to D. magna increased with concentration, with 1-µm particles being the most toxic (48-h LC50 value: 23.57 mg/L). Behavioral analyses revealed that PSMP exposure reduced swimming speed from 5.8 ± 0.2 mm/s (control) to 3.7 ± 0.4 mm/s (1/2 LC50) after 24 h, further decreasing to 3.0 ± 0.5 mm/s at 48 h. Similarly, thoracic limb movement frequency, jumping frequency, and mandibular activity were suppressed, with transient hyperactivity observed at low doses (1/16 LC50) followed by inhibition. Furthermore, exposure to smaller-sized PSMP caused significant changes in the levels of superoxide dismutase, catalase, malondialdehyde, and glutathione in D. magna, indicating that PSMP induces oxidative stress by increasing reactive oxygen species levels, ultimately leading to oxidative damage. While particle size is a well-established critical parameter, behavioral endpoints (e.g., reduced swimming speed and feeding efficiency) and oxidative damage at sublethal concentrations serve as more sensitive early-warning biomarkers for environmental risk assessment. Future research should validate these biomarkers in natural ecosystems and investigate the effects of chronic exposure on population dynamics.