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Transformation kinetics of silver nanoparticles and silver ions in aquatic environments revealed by double stable isotope labeling

机译:双稳定同位素标记显示银纳米粒子和银离子在水环境中的转化动力学

摘要

Silver nanoparticles (AgNPs) are rather mutable in water columns, and the oxidation of AgNPs to release Ag+ and reduction of Ag+ to regenerate AgNPs exist simultaneously in certain environments, making it rather difficult to monitor the reaction kinetics. In this study, we synthesized isotopically labeled AgNPs (99.5% Ag-107, (107)AgNPs) and AgNO3 (99.81% Ag-109, (AgNO3)-Ag-109). For the first time, two stable Ag isotopes were used in the same experiment to track the transformation kinetics of AgNPs and Ag+ independently in aquatic environments. It was found that the oxidation of AgNPs dominated the reaction in simple water solutions containing both (107)AgNPs and Ag-109(+). Sunlight significantly accelerated the dissolution of the (107)AgNPs, but longer solar irradiation (8 h) triggered aggregation of the (107)AgNPs and therefore reduced the reaction rate. With the addition of 5 mg C L-1 dissolved organic matter, the reduction of Ag-109(+) played the leading role. The corrected concentration of dissolved Ag-107(+) began to decrease after some time, indicating other reduction mechanisms were happening. An elevated pH (pH 8.5) could even completely inhibit the oxidation of (107)AgNPs. All the reactions seemed stalled at low temperature (6 degrees C) except the dissolution of (107)AgNPs under solar irradiation, suggesting a non-negligible effect of sunlight. The presence of divalent cations induced agglomeration of (107)AgNPs, but the reduction of Ag-109(+) was not significantly affected. These findings implied that the transformation between AgNPs and Ag+ was rather complex and greatly depended on the external conditions. Given the fact that Ag+ has been shown to be much more toxic than AgNPs, the speciation change may dramatically impact the final toxicity and bioavailability of AgNPs, so there is a high demand for assessing the environmental risks of AgNPs under more realistic conditions.
机译:银纳米颗粒(AgNPs)在水柱中非常易变,并且在某些环境中同时存在AgNPs的氧化以释放Ag +和Ag +的还原以再生AgNPs,这使得监测反应动力学相当困难。在这项研究中,我们合成了同位素标记的AgNPs(99.5%Ag-107,(107)AgNPs)和AgNO3(99.81%Ag-109,(AgNO3)-Ag-109)。首次在同一实验中使用了两个稳定的Ag同位素,以独立跟踪水生环境中AgNPs和Ag +的转化动力学。发现在包含(107)AgNPs和Ag-109(+)的简单水溶液中,AgNPs的氧化作用占主导地位。日光显着促进了(107)AgNPs的溶解,但是更长的太阳辐射(8 h)触发了(107)AgNPs的聚集,因此降低了反应速率。加入5 mg C L-1溶解的有机物后,Ag-109(+)的还原起主要作用。一段时间后,校正后的溶解的Ag-107(+)浓度开始降低,表明正在发生其他还原机理。 pH值升高(pH 8.5)甚至可以完全抑制(107)AgNP的氧化。除了(107)AgNP在太阳辐射下溶解之外,所有反应似乎都在低温(6摄氏度)下停止,这表明日光的作用不可忽略。二价阳离子的存在诱导了(107)AgNPs的团聚,但Ag-109(+)的减少并未受到明显影响。这些发现表明,AgNPs和Ag +之间的转化相当复杂,并且很大程度上取决于外部条件。鉴于事实证明,Ag +比AgNPs具有更大的毒性,物种变化可能会极大地影响AgNPs的最终毒性和生物利用度,因此迫切需要在更现实的条件下评估AgNPs的环境风险。

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