School of Ecology and Environment, Inner Mongolia University, Hohhot 010021, Inner Mongolia, China.
School of Ecology and Environment, Inner Mongolia University, Hohhot 010021, Inner Mongolia, China.
Sci Total Environ. 2024 Mar 20;917:170441. doi: 10.1016/j.scitotenv.2024.170441. Epub 2024 Jan 28.
The bioavailability of cerium (Ce) and its toxic effects on aquatic organisms are still unclear, which limits the toxicity prediction and pollution control for this element. Here, the acute toxicity of Ce to Daphnia magna neonates and the responses of the antioxidant system were investigated, and the quantitative relationships between the toxicity of Ce and environmental factors were determined. The 24 and 48 h EC50 values based on the dissolved concentration of Ce in Daphnia magna were 60.6 and 10.9 μM, respectively, and the EC50 values were 23.4 and 3.73 μM, respectively. After Ce exposure at environmentally relevant concentrations (0.5-3.5 μM), significant increases in superoxide dismutase activity and malondialdehyde content were observed in Daphnia magna, while significant decreases in catalase activity and HO content occurred. Low levels of Ce cause oxidative damage to Daphnia magna and adverse impacts on the antioxidant system; however, further molecular-based studies are needed. The addition of Ca or Na reduced the acute toxicity of Ce to Daphnia magna. In contrast, Mg (MgSO) promoted Ce toxicity, which is a new finding related to the interaction effects between cations and rare earth elements on biological ligands; however, the effects of SO could not be distinguished. Complexation with organic ligands could significantly reduce the toxicity of Ce to Daphnia magna; however, complexes of Ce with citric acid and malic acid might be bioavailable to Daphnia magna. In the absence of organic ligands and competing metals, the binding constant of Ce to Daphnia magna at toxic concentrations was 5.83. The log K values for the competitive effects of Ca and Na were 3.73 and 2.59, respectively, while the log K value for the protective effect of fulvic acid was 3.76. These results contribute to understanding the toxicity of Ce and will help predict the toxicity of Ce in freshwater.
铈的生物利用度及其对水生生物的毒性效应尚不清楚,这限制了该元素的毒性预测和污染控制。在这里,研究了铈对大型溞幼体的急性毒性及其抗氧化系统的反应,并确定了铈毒性与环境因素之间的定量关系。基于大型溞中铈的溶解浓度,24 和 48 h 的 EC50 值分别为 60.6 和 10.9 μM,EC50 值分别为 23.4 和 3.73 μM。在环境相关浓度(0.5-3.5 μM)下暴露于铈后,大型溞中超氧化物歧化酶活性和丙二醛含量显著增加,而过氧化氢酶活性和羟自由基含量显著降低。低浓度的铈会对大型溞造成氧化损伤,并对其抗氧化系统产生不良影响;然而,还需要进一步的基于分子的研究。添加 Ca 或 Na 会降低铈对大型溞的急性毒性。相比之下,Mg(MgSO4)促进了 Ce 的毒性,这是与阳离子和稀土元素对生物配体的相互作用效应有关的新发现;然而,SO 的影响无法区分。与有机配体络合可显著降低铈对大型溞的毒性;然而,柠檬酸和苹果酸与 Ce 的络合物可能对大型溞具有生物利用度。在没有有机配体和竞争金属的情况下,Ce 在有毒浓度下与大型溞的结合常数为 5.83。Ca 和 Na 的竞争效应的 log K 值分别为 3.73 和 2.59,而富里酸的保护效应的 log K 值为 3.76。这些结果有助于了解 Ce 的毒性,并将有助于预测淡水环境中 Ce 的毒性。