Wu Hanyu, Li Ping, Pan Duoqiang, Yin Zhuoxin, Fan Qiaohui, Wu Wangsuo
Radiochemistry Laboratory, School of Nuclear Science and Technology, Lanzhou University, Lanzhou, Gansu, 730000, China.
Key Laboratory of Special Function Materials and Structure Design, Ministry of Education, Lanzhou, Gansu, 730000, China.
PLoS One. 2016 Mar 1;11(3):e0149632. doi: 10.1371/journal.pone.0149632. eCollection 2016.
The interactions between contaminations of U(VI) and silicon oxide nanoparticles (SONPs), both of which have been widely used in modern industry and induced serious environmental challenge due to their high mobility, bioavailability, and toxicity, were studied under different environmental conditions such as pH, temperature, and natural organic matters (NOMs) by using both batch and spectroscopic approaches. The results showed that the accumulation process, i.e., sorption, of U(VI) on SONPs was strongly dependent on pH and ionic strength, demonstrating that possible outer- and/or inner-sphere complexes were controlling the sorption process of U(VI) on SONPs in the observed pH range. Humic acid (HA), one dominated component of NOMs, bounded SONPs can enhance U(VI) sorption below pH~4.5, whereas restrain at high pH range. The reversible sorption of U(VI) on SONPs possibly indicated that the outer-sphere complexes were prevalent at pH 5. However, an irreversible interaction of U(VI) was observed in the presence of HA (Fig 1). It was mainly due to the ternary SONPs-HA-U(VI) complexes (Type A Complexes). After SONPs adsorbed U(VI), the particle size in suspension was apparently increased from ~240 nm to ~350 nm. These results showed that toxicity of both SONPs and U(VI) will decrease to some extent after the interaction in the environment. These findings are key for providing useful information on the possible mutual interactions among different contaminants in the environment.
铀(VI)污染物与氧化硅纳米颗粒(SONPs)之间的相互作用已得到研究。这两种物质在现代工业中均被广泛使用,因其具有高迁移率、生物可利用性和毒性,给环境带来了严峻挑战。研究采用了批次法和光谱法,在不同环境条件下,如pH值、温度和天然有机物(NOMs)等条件下进行。结果表明,U(VI)在SONPs上的累积过程,即吸附,强烈依赖于pH值和离子强度,这表明在观察到的pH范围内,可能的外层和/或内层络合物控制着U(VI)在SONPs上的吸附过程。腐殖酸(HA)是NOMs的主要成分之一,结合SONPs在pH值约4.5以下可增强U(VI)的吸附,而在高pH范围内则起抑制作用。U(VI)在SONPs上的可逆吸附可能表明在pH为5时外层络合物占主导。然而,在HA存在的情况下观察到U(VI)发生了不可逆相互作用(图1)。这主要是由于三元SONPs-HA-U(VI)络合物(A型络合物)。SONPs吸附U(VI)后,悬浮液中的粒径明显从约240nm增加到约350nm。这些结果表明,SONPs和U(VI)在环境中相互作用后毒性会在一定程度上降低。这些发现对于提供有关环境中不同污染物之间可能的相互作用的有用信息至关重要。