CEA, DSV, Laboratoire de Physiologie Cellulaire Végétale , 17 rue des Martyrs, 38054 Grenoble, France.
CNRS, UMR5168 , 17 rue des Martyrs, 38054 Grenoble, France.
Environ Sci Technol. 2016 Jan 5;50(1):359-67. doi: 10.1021/acs.est.5b03306. Epub 2015 Dec 21.
Microalgae are good candidates for toxic metal remediation biotechnologies. This study explores the cellular processes implemented by the green microalga Coccomyxa actinabiotis to take up and cope with silver over the concentration range of 10(-7) to 10(-2) M Ag(+). Understanding these processes enables us to assess the potential of this microalga for applications for bioremediation. Silver in situ speciation and localization were investigated using X-ray absorption spectroscopy, X-ray diffraction, and transmission electron microscopy. Silver toxicity was evaluated by monitoring microalgal growth and photochemical parameters. Different accumulation mechanisms were brought out depending on silver concentration. At low micromolar concentration, microalgae fixed all silver initially present in solution, trapping it inside the cells into the cytosol, mainly as unreduced Ag(I) bound with molecules containing sulfur. Silver was efficiently detoxified. When concentration increased, silver spread throughout the cell and particularly entered the chloroplast, where it damaged the photosystem. Most silver was reduced to Ag(0) and aggregated to form crystalline silver nanoparticles of face-centered cubic structure with a mean size of 10 nm. An additional minor interaction of silver with molecules containing sulfur indicated the concomitant existence of the mechanism observed at low concentration or nanoparticle capping. Nanoparticles were observed in chloroplasts, in mitochondria, on the plasma membrane, on cytosolic membrane structures, and in vacuoles. Above 10(-4) M Ag(+), damages were irreversible, and photosynthesis and growth were definitely inhibited. However, high silver amounts remained confined inside microalgae, showing their potential for the bioremediation of contaminated water.
微藻是修复有毒金属的生物技术的良好候选者。本研究探索了绿色微藻 Coccomyxa actinabiotis 吸收和应对银的细胞过程,银的浓度范围为 10(-7) 至 10(-2) M Ag(+)。了解这些过程使我们能够评估这种微藻在生物修复应用中的潜力。使用 X 射线吸收光谱、X 射线衍射和透射电子显微镜研究了银的原位形态和定位。通过监测微藻生长和光化学参数来评估银的毒性。根据银的浓度,提出了不同的积累机制。在低微摩尔浓度下,微藻固定了溶液中最初存在的所有银,将其困在细胞质中,主要以与含硫分子结合的未还原的 Ag(I)形式存在。银被有效地解毒。当浓度增加时,银遍布整个细胞,特别是进入叶绿体,在那里它破坏了光合作用系统。大部分银被还原为 Ag(0)并聚集形成面心立方结构的结晶银纳米粒子,平均粒径为 10nm。银与含硫分子的另一个次要相互作用表明,在低浓度或纳米粒子帽存在的同时存在这种机制。纳米粒子在叶绿体、线粒体、质膜、胞质膜结构和液泡中观察到。在 10(-4) M Ag(+)以上,损伤是不可逆的,光合作用和生长肯定受到抑制。然而,大量的银仍然局限在微藻内部,显示出它们在受污染水的生物修复中的潜力。