College of Natural Resources and Environment, Northwest A & F University, Yangling, Shaanxi 712100, China; Department of Civil & Environmental Engineering, University of Houston, Houston, TX 77204, United States.
Department of Civil & Environmental Engineering, University of Houston, Houston, TX 77204, United States.
Environ Res. 2019 May;172:552-560. doi: 10.1016/j.envres.2019.03.008. Epub 2019 Mar 4.
To better understand the fate and transport of ferrihydrite nanoparticles (FNPs), which carry many contaminants in natural and engineered aquatic environments, the aggregation of FNPs was systematically investigated in this study. The pH isoelectric point (pH), surface zeta potential, and particle size evolutions of FNPs were measured under varied aqueous conditions using dynamic light scattering (DLS). The influence of pH (5.0 ± 0.1 and 7.0 ± 0.1), ionic strength (IS), electrolytes (NaCl, CaCl and NaSO), and organics (humic acid, fulvic acid and CHCOONa) on the aggregation behaviors of FNPs were explored. Meanwhile, Derjaguin-Landau-Verwey-Overbeek (DLVO) theory was employed to better understand the controlling mechanisms of FNP aggregation. In the presence of sulfate, the surface charge of FNPs was neutralized under varied pH and ionic strength due to ion adsorption and FNPs phase transformation to schwertmannite based on FT-IR results. This phase transformation resulted in rapid aggregation in all water chemistries tested, whereas other salt species affected the aggregation primarily by ion adsorption and charge screening. Presence of increasing concentrations of the organic acids significantly shifted the pH of FNPs (7.0 ± 0.2) to lower pH (< 4.0) due to adsorption of organics on FNPs surfaces making them negatively charged. The adsorption of HA/FA inhibited FNP aggregation significantly while CHCOONa did not, due to different effects on steric and/or electrosteric interactions among FNPs by organics with varied pK values and molecular weights. After accounting for the important effects of pH, electrolytes, and organics in modifying FNPs' surface charge, DLVO calculations agreed well with measured critical coagulation concentrations (CCC) values of FNPs at both pH 5.0 ± 0.1 and 7.0 ± 0.1 in the presence of NaCl. This study will hence be useful to better predict and control the fate and transport of FNPs in the presence of electrolytes and organics with different molecular weights, as well as the fate of the associated contaminants in natural and engineered systems.
为了更好地了解铁氢氧化物纳米颗粒(FNPs)的命运和迁移,这些颗粒在自然和工程水生环境中携带许多污染物,本研究系统地研究了 FNPs 的聚集。使用动态光散射(DLS)测量了在不同水相条件下 FNPs 的 pH 等电点(pH)、表面 ζ 电位和粒径演变。研究了 pH(5.0±0.1 和 7.0±0.1)、离子强度(IS)、电解质(NaCl、CaCl 和 NaSO)和有机物(腐殖酸、富里酸和 CHCOONa)对 FNPs 聚集行为的影响。同时,采用德贾金-兰德维厄-奥弗贝克(DLVO)理论更好地理解了 FNP 聚集的控制机制。在硫酸盐存在下,根据 FT-IR 结果,FNPs 的表面电荷由于离子吸附和 FNPs 向水铁矿的相转变而在不同 pH 和离子强度下中和。这种相转变导致在所有测试的水化学条件下迅速聚集,而其他盐种类主要通过离子吸附和电荷屏蔽影响聚集。有机酸浓度的增加显著地将 FNPs 的 pH 值(7.0±0.2)降低到较低的 pH 值(<4.0),这是由于有机物在 FNPs 表面的吸附使其带负电荷。由于有机物具有不同的 pK 值和分子量,对 FNPs 之间的空间和/或电动空间相互作用有不同的影响,因此 HA/FA 的吸附显著抑制了 FNP 的聚集,而 CHCOONa 则没有。在考虑 pH、电解质和有机物对 FNPs 表面电荷的重要影响后,DLVO 计算与 NaCl 存在下在 pH 5.0±0.1 和 7.0±0.1 时测量的 FNPs 的临界凝聚浓度(CCC)值吻合较好。因此,本研究将有助于更好地预测和控制在具有不同分子量的电解质和有机物存在下 FNPs 的命运和迁移,以及在自然和工程系统中与相关污染物的命运。