Department of Civil and Environmental Engineering, Duke University, Box 90287, Durham, North Carolina 27708, United States.
Environ Sci Technol. 2012 Jul 3;46(13):7037-45. doi: 10.1021/es3001757. Epub 2012 Apr 6.
The persistence of silver nanoparticles in aquatic environments and their subsequent impact on organisms depends on key transformation processes, which include aggregation, dissolution, and surface modifications by metal-complexing ligands. Here, we studied how cysteine, an amino acid representative of thiol ligands that bind monovalent silver, can alter the surface chemistry, aggregation, and dissolution of zero-valent silver nanoparticles. We compared nanoparticles synthesized with two coatings, citrate and polyvinylpirrolidone (PVP), and prepared nanoparticle suspensions (approximately 8 μM total Ag) containing an excess of cysteine (400 μM). Within 48 h, up to 47% of the silver had dissolved, as indicated by filtration of the samples with a 0.025-μm filter. Initial dissolution rates were calculated from the increase of dissolved silver concentration when particles were exposed to cysteine and normalized to the available surface area of nanoparticles in solution. In general, the rates of dissolution were almost 3 times faster for citrate-coated nanoparticles relative to PVP-coated nanoparticles. Rates tended to be slower in solutions with higher ionic strength in which the nanoparticles were aggregating. X-ray absorption spectroscopy analysis of the particles suggested that cysteine adsorbed to silver nanoparticles surfaces through the formation of Ag(+I)--sulfhydryl bonds. Overall, the results of this study highlight the importance of modifications by sulfhydryl-containing ligands that can drastically influence the long-term reactivity of silver nanoparticles in the aquatic environment and their bioavailability to exposed organisms. Our findings demonstrate the need to consider multiple interlinked transformation processes when assessing the bioavailability, environmental risks, and safety of nanoparticles, particularly in the presence of metal-binding ligands.
银纳米粒子在水生环境中的持久性及其对生物体的后续影响取决于关键的转化过程,包括聚集、溶解和由金属配合物配体引起的表面修饰。在这里,我们研究了半胱氨酸(一种代表与单价银结合的硫醇配体的氨基酸)如何改变零价银纳米粒子的表面化学、聚集和溶解。我们比较了用两种涂层(柠檬酸和聚乙烯吡咯烷酮(PVP))合成的纳米粒子,并制备了含有过量半胱氨酸(400 μM)的纳米粒子悬浮液(约 8 μM 总 Ag)。在 48 小时内,高达 47%的银已经溶解,这表明样品通过 0.025-μm 的过滤器进行了过滤。根据暴露在半胱氨酸中时溶解银浓度的增加,从初始溶解速率计算出初始溶解速率,并归一化为溶液中纳米粒子的可用表面积。一般来说,相对于 PVP 涂层的纳米粒子,柠檬酸涂层的纳米粒子的溶解速率快近 3 倍。在聚集的情况下,离子强度较高的溶液中的溶解速率往往较慢。对颗粒的 X 射线吸收光谱分析表明,半胱氨酸通过形成 Ag(+I)--硫醇键吸附在银纳米颗粒表面上。总的来说,这项研究的结果强调了含巯基配体的修饰的重要性,这些修饰可以极大地影响银纳米粒子在水生环境中的长期反应性及其对暴露的生物体的生物利用度。我们的研究结果表明,在评估纳米颗粒的生物利用度、环境风险和安全性时,特别是在存在金属结合配体的情况下,需要考虑多个相互关联的转化过程。