CONICET Consejo Nacional de Investigaciones Científicas y Técnicas, Buenos Aires, Argentina.
Departamento de Ciencias Básicas, Programa de Investigación en Ecotoxicología, Universidad Nacional de Luján, Luján, Argentina.
Ecotoxicology. 2021 Jan;30(1):91-103. doi: 10.1007/s10646-020-02312-2. Epub 2020 Nov 25.
The aim of the present study was to investigate the toxicity effects of cadmium-nickel (Cd-Ni) after single and mixtures exposures over the macrophyte Lemna gibba. Effects were assessed on growth, as frond number and fresh weight and biochemical parameters, such as total protein content and activity of antioxidant enzymes. Plants were exposed to single Cd and Ni in concentrations that ranged between 0.13-33 mg/L and 0.18 and 11.82 mg/L, respectively. For binary mixtures, individual metal IC50 values were used for selection of the evaluated concentrations. The experimental design consisted in three different ratios based on the concept of toxic units (TU), each ratio was evaluated by five different concentrations. Both single and mixture treatments were performed for 7 days following the conditions according to OECD (2006). Single and mixture exposures affected plant growth and the biomarkers of the antioxidant response. Growth parameters showed a differential sensitivity after individual metal exposures. Cd was more toxic for L. gibba plants when fresh weight was considered, but on the contrary, considering frond number, Ni was the most toxic metal. IC50-7d, based on growth rate calculated on frond number were 17.8 and 2.47 mg/L, and on fresh weight were 1.08 and 3.89 mg/L, for Cd and Ni respectively. LOEC values for Cd were obtained at 2.06 and 1.03 mg/L, for frond number and fresh weight, respectively; while for Ni, these values were 0.92 and 11.82 mg/L. The three evaluated ratios for binary mixtures resulted in a high toxicity considering the same response variables in single metal exposures. Ratio 1 (2/3 TU Cd-1/3 TU Ni) was the most toxic considering both frond number and fresh weight, showing percentage inhibition of growth rates of 96 and 90%, respectively for the highest concentration. A modification of the protein content was observed in single, but especially in the mixture treatments. The activity of catalase (CAT; EC 1.11.1.6), ascorbate peroxidase (APOX; EC 1.11.1.11) and guaiacol peroxidase (GPOX; EC 1.11.1.7) was also affected in single and mixtures assays. APOX and GPOX showed a higher increase of its activities respect the controls after mixture treatments than for single metal treatments. Such optimization of the antioxidant system could be one of the causes of the antagonistic toxicity observed in mixture exposures. Concentration addition (CA) reference model, based on frond number, in Cd-Ni mixtures was not a good predictor to evaluate toxicity from dissolved metal concentration since the results showed that toxicity was less than additive, with an average of ΣTU = 2.17. The observed antagonisms resulted to be stronger in mixtures with higher metal concentrations.
本研究旨在研究镉镍(Cd-Ni)单一和混合暴露对浮萍(Lemna gibba)的毒性效应。通过测定浮萍的叶数和鲜重等生长参数以及总蛋白含量和抗氧化酶活性等生化参数来评估其毒性效应。研究中使用的 Cd 和 Ni 浓度范围分别为 0.13-33mg/L 和 0.18-11.82mg/L。对于二元混合物,使用单个金属的 IC50 值选择评估浓度。实验设计基于毒性单位(TU)的概念,包括三个不同的比值,每个比值均由五个不同的浓度进行评估。按照 OECD(2006)的规定,分别对单一和混合处理进行了 7 天的暴露实验。单一和混合暴露均影响了植物的生长和抗氧化反应的生物标志物。单独金属暴露后,生长参数表现出不同的敏感性。就鲜重而言,Cd 对浮萍的毒性更大,但相反,就叶数而言,Ni 是最毒的金属。基于 frond number 计算的生长率的 IC50-7d 值分别为 17.8 和 2.47mg/L,基于 fresh weight 的 IC50-7d 值分别为 1.08 和 3.89mg/L,分别对应 Cd 和 Ni。Cd 的 LOEC 值在叶数和鲜重方面分别为 2.06 和 1.03mg/L;而 Ni 的 LOEC 值分别为 0.92 和 11.82mg/L。对于二元混合物,当评估相同的反应变量时,三种评估比值均表现出较高的毒性。比值 1(2/3 TU Cd-1/3 TU Ni)是最毒的,在考虑到叶数和鲜重时,其最高浓度的生长抑制率分别达到了 96%和 90%。在单一和混合处理中均观察到蛋白质含量的改变。CAT(EC 1.11.1.6)、APOX(EC 1.11.1.11)和 GPOX(EC 1.11.1.7)的活性也受到单一和混合处理的影响。与单一金属处理相比,混合物处理后 APOX 和 GPOX 的活性相对于对照均有较高的增加。这种抗氧化系统的优化可能是混合物暴露中观察到的拮抗毒性的原因之一。基于 frond number 的浓度加和(CA)参考模型在 Cd-Ni 混合物中不是评估溶解金属浓度毒性的良好预测模型,因为结果表明毒性低于加和,平均ΣTU=2.17。在金属浓度较高的混合物中,观察到的拮抗作用更强。