Department of Hydrobiology, Federal University of São Carlos (UFSCar), Rodovia Washington Luís, Km 235, 13565-905, São Carlos, SP, Brazil; Post-Graduate Program in Ecology and Natural Resources (PPGERN), Federal University of São Carlos (UFSCar), Rodovia Washington Luís, Km 235, 13565-905, São Carlos, SP, Brazil.
Department of Hydrobiology, Federal University of São Carlos (UFSCar), Rodovia Washington Luís, Km 235, 13565-905, São Carlos, SP, Brazil; Post-Graduate Program in Ecology and Natural Resources (PPGERN), Federal University of São Carlos (UFSCar), Rodovia Washington Luís, Km 235, 13565-905, São Carlos, SP, Brazil.
Chemosphere. 2022 Feb;288(Pt 2):132536. doi: 10.1016/j.chemosphere.2021.132536. Epub 2021 Oct 9.
Silver-based materials have microbicidal action, photocatalytic activity and electronic properties. The increase in manufacturing and consumption of these compounds, given their wide functionality and application, is a source of contamination to freshwater ecosystems and causes toxicity to aquatic biota. Therefore, for the first time, we evaluated the toxicity of the silver tungstate (α-AgWO), in different morphologies (cube and rod), for the microalga Raphidocelis subcapitata. To investigate the toxicity, we evaluated the growth rate, cell complexity and size, reactive oxygen species (ROS) production and chlorophyll a (Chl a) fluorescence. The α-AgWO - R (rod) was 1.7 times more toxic than α-AgWO-C (cube), with IC and IC values of, respectively, 8.68 ± 0.91 μg L and 13.72 ± 1.48 μg L for α-AgWO - R and 18.60 ± 1.61 μg L and 23.47 ± 1.16 μg L for α-AgWO-C. The release of silver ions was quantified and indicated that the silver ions dissolution from the α-AgWO - R ranged from 34 to 71%, while the Ag ions from the α-AgWO-C varied from 35 to 97%. The α-AgWO-C induced, after 24 h exposure, the increase of ROS at the lowest concentrations (8.81 and 19.32 μg L), whereas the α-AgWO - R significantly induced ROS production at 96 h at the highest concentration (31.76 μg L). Both microcrystal shapes significantly altered the cellular complexity and decreased the Chl a fluorescence at all tested concentrations. We conclude that the different morphologies of α-AgWO negatively affect the microalga and are important sources of silver ions leading to harmful consequences to the aquatic ecosystem.
银基材料具有杀菌作用、光催化活性和电子特性。由于这些化合物具有广泛的功能和应用,其制造和消费的增加是淡水生态系统污染的来源,并对水生生物区系造成毒性。因此,我们首次评估了不同形态(立方体和棒状)的钨酸银(α-AgWO)对微藻莱茵衣藻的毒性。为了研究毒性,我们评估了生长速率、细胞复杂性和大小、活性氧(ROS)产生和叶绿素 a(Chl a)荧光。α-AgWO-R(棒状)比α-AgWO-C(立方体)毒性高 1.7 倍,α-AgWO-R 的 IC 和 IC 值分别为 8.68±0.91μg/L 和 13.72±1.48μg/L,α-AgWO-C 的 IC 和 IC 值分别为 18.60±1.61μg/L 和 23.47±1.16μg/L。定量释放银离子表明,α-AgWO-R 中的银离子溶解率在 34%至 71%之间,而α-AgWO-C 中的 Ag 离子溶解率在 35%至 97%之间。α-AgWO-C 在暴露 24 小时后,在最低浓度(8.81 和 19.32μg/L)下会增加 ROS,而α-AgWO-R 在最高浓度(31.76μg/L)下在 96 小时时会显著增加 ROS 产生。两种微晶形状都显著改变了细胞复杂性,并降低了所有测试浓度下的 Chl a 荧光。我们得出结论,α-AgWO 的不同形态对微藻有负面影响,是导致水生生态系统产生有害后果的银离子的重要来源。