Simansky Samuel, Holub Jiří, Márová Ivana, Cuaresma María, Garbayo Ines, Torronteras Rafael, Vílchez Carlos, Gojkovic Zivan
Algal Biotechnology Group, Centro de Investigación y Desarrollo de Recursos y Tecnologías Agroalimentarias (CIDERTA), University of Huelva, 21007 Huelva, Spain.
Faculty of Chemistry, Brno University of Technology, Purkyñova 118, 61200 Brno, Czech Republic.
Microorganisms. 2024 Feb 21;12(3):434. doi: 10.3390/microorganisms12030434.
The main entrance point of highly toxic organic Hg forms, including methylmercury (MeHg), into the aquatic food web is phytoplankton, which is greatly represented by various natural microalgal species. Processes associated with MeHg fate in microalgae cells such as uptake, effects on cells and toxicity, Hg biotransformation, and intracellular stability are detrimental to the process of further biomagnification and, as a consequence, have great importance for human health. The study of MeHg uptake and distribution in cultures of marine halophile and freshwater acidophilic alga demonstrated that most of the MeHg is imported inside the cell, while cell surface adhesion is insignificant. Almost all MeHg is removed from the culture medium after 72 h. Significant processes in rapid MeHg removal from liquid medium are its abiotic photodegradation and volatilization associated with algal enzymatic activity. The maximum intracellular accumulation for both species was in 80 nM MeHg-exposed cultures after 24 h of exposure for (from 27 to 34 µg/g) and at 48 h for (up to 138 µg/g). The different Hg intakes in these two strains could be explained by the lack of a rigid cell wall in and the higher chemical ability of MeHg to pass through complex cell wall structures in . Electron microscopy studies on the ultrastructure of both strains demonstrated obvious microvacuolization in the form of many very small vacuoles and partial cell membrane disruption in 80 nM MeHg-exposed cultures. Results further showed that is a good candidate for MeHg-contaminated water reclamation due to its great robustness at nanomolar concentrations of MeHg coupled with its very high intake and almost complete Hg removal from liquid medium at the MeHg levels tested.
剧毒有机汞形态,包括甲基汞(MeHg),进入水生食物网的主要入口是浮游植物,浮游植物主要由各种天然微藻物种构成。与微藻细胞中甲基汞归宿相关的过程,如吸收、对细胞的影响和毒性、汞的生物转化以及细胞内稳定性,对进一步的生物放大过程不利,因此对人类健康至关重要。对海洋嗜盐藻和淡水嗜酸藻培养物中甲基汞吸收和分布的研究表明,大部分甲基汞被导入细胞内,而细胞表面的吸附作用微不足道。72小时后,几乎所有甲基汞都从培养基中去除。甲基汞从液体培养基中快速去除的重要过程是其非生物光降解以及与藻类酶活性相关的挥发。两种藻类在暴露24小时后,对于[具体藻类1],在80 nM甲基汞暴露的培养物中达到最大细胞内积累量(从27至34 µg/g);对于[具体藻类2],在48小时达到最大细胞内积累量(高达138 µg/g)。这两种菌株中不同的汞摄入量可以通过[具体藻类1]缺乏坚硬细胞壁以及甲基汞穿过[具体藻类2]复杂细胞壁结构的化学能力更强来解释。对两种菌株超微结构的电子显微镜研究表明,在80 nM甲基汞暴露的培养物中,呈现出许多非常小的液泡形式的明显微液泡化以及部分细胞膜破坏。结果进一步表明,[具体藻类2]是受甲基汞污染水回收的良好候选者,因为它在纳摩尔浓度的甲基汞下具有很强的耐受性,同时在测试的甲基汞水平下具有很高的摄入量且几乎能从液体培养基中完全去除汞。