Department of Ecology and Coastal Management, Institute of Marine Sciences of Andalusia (CSIC), Campus Río S. Pedro, 11510 Puerto Real, Cádiz, Spain.
Department of Material Science, Metallurgical Engineering and Inorganic Chemistry, Faculty of Sciences, University of Cadiz, E-11510 Puerto Real, Cádiz, Spain.
Sci Total Environ. 2017 Aug 15;592:403-411. doi: 10.1016/j.scitotenv.2017.03.127. Epub 2017 Mar 18.
TiO nanoparticles (TiO NPs) are employed in many products (paints, personal care products, especially sunscreens, plastics, paper, water potabilization and food products) and are then released into the environment from these products. These nanoparticles present potential risk to freshwater and marine microalgae. The primary toxicity mechanism is adsorption between NPs and microalgae (heteroagglomeration); however, studies of interactions of this kind are scarce. We investigated the heteroagglomeration process that occurs between two forms of TiO material, nanoparticles and bulk, and three different microalgae species, and under different environmental conditions (freshwater and marine water), in order to assess the influence of pH and ionic strength (IS). The heteroagglomeration process was examined by means of co-settling experiments and the Derjaguin-Landau-Verwey-Overbeek (DLVO) approach. The homoagglomeration process (only NPs to NPs) did not show differences between culture media (freshwater and marine water). However, in the heteroagglomeration process between NPs and cells, IS played an important role. Ions can compress the electro-double layer between NPs and microalgae, allowing a heteroagglomeration process to take place, as shown by settling experiments. TiO NPs presented a settling rate higher than bulk TiO. The DLVO theory could only partially explain heteroagglomeration because, in this model, it is not considered that NP-NP and Cell-Cell homoagglomeration co-occur. In this study neither the role of exopolymeric substances in the interaction between NPs and cells nor detoxification are considered. The authors suggest that the interaction between NPs and microalgae could be considered as the first stage in the process by which nanoparticles affect microalgae.
TiO 纳米颗粒 (TiO NPs) 被广泛应用于许多产品(如涂料、个人护理产品、尤其是防晒霜、塑料、纸张、水净化和食品产品)中,然后从这些产品中释放到环境中。这些纳米颗粒对淡水和海洋微藻存在潜在风险。主要的毒性机制是 NPs 与微藻之间的吸附(异凝聚);然而,这种相互作用的研究还很缺乏。我们研究了两种 TiO 材料(纳米颗粒和块状)与三种不同微藻物种之间的异凝聚过程,并在不同的环境条件(淡水和海水)下,评估了 pH 和离子强度 (IS) 的影响。通过共沉降实验和德加古林-兰德维韦尔-奥弗贝克 (DLVO) 方法研究了异凝聚过程。同凝聚过程(仅 NPs 到 NPs)在培养基(淡水和海水)之间没有显示出差异。然而,在 NPs 和细胞之间的异凝聚过程中,IS 起着重要作用。离子可以压缩 NPs 和微藻之间的电动双层,从而允许异凝聚过程发生,如沉降实验所示。TiO NPs 的沉降速率高于块状 TiO。DLVO 理论只能部分解释异凝聚,因为在这个模型中,没有考虑到 NP-NP 和 Cell-Cell 同凝聚同时发生。在这项研究中,没有考虑到细胞之间 NPs 相互作用的胞外聚合物物质的作用或解毒作用。作者建议,可以将 NPs 与微藻之间的相互作用视为纳米颗粒影响微藻的过程的第一阶段。