The Key Laboratory of Water and Sediment Sciences, Ministry of Education, State Environmental Protection Key Laboratory of All Material Fluxes in River Ecosystems, College of Environmental Sciences and Engineering, Peking University, Beijing 100871, P. R. China.
Southwest United Graduate School, Kunming 650092, P. R. China.
Environ Sci Technol. 2024 May 14;58(19):8501-8509. doi: 10.1021/acs.est.4c01245. Epub 2024 May 2.
Iron/chromium hydroxide coprecipitation controls the fate and transport of toxic chromium (Cr) in many natural and engineered systems. Organic coatings on soil and engineered surfaces are ubiquitous; however, mechanistic controls of these organic coatings over Fe/Cr hydroxide coprecipitation are poorly understood. Here, Fe/Cr hydroxide coprecipitation was conducted on model organic coatings of humic acid (HA), sodium alginate (SA), and bovine serum albumin (BSA). The organics bonded with SiO through ligand exchange with carboxyl (-COOH), and the adsorbed amounts and p values of -COOH controlled surface charges of coatings. The adsorbed organic films also had different complexation capacities with Fe/Cr ions and Fe/Cr hydroxide particles, resulting in significant differences in both the amount (on HA > SA(-COOH) ≫ BSA(-NH)) and composition (Cr/Fe molar ratio: on BSA(-NH) ≫ HA > SA(-COOH)) of heterogeneous precipitates. Negatively charged -COOH attracted more Fe ions and oligomers of hydrolyzed Fe/Cr species and subsequently promoted heterogeneous precipitation of Fe/Cr hydroxide nanoparticles. Organic coatings containing -NH were positively charged at acidic pH because of the high p value of the functional group, limiting cation adsorption and formation of coprecipitates. Meanwhile, the higher local pH near the -NH coatings promoted the formation of Cr(OH). This study advances fundamental understanding of heterogeneous Fe/Cr hydroxide coprecipitation on organics, which is essential for successful Cr remediation and removal in both natural and engineered settings, as well as the synthesis of Cr-doped iron (oxy)hydroxides for material applications.
铁/ 铬氢氧化物共沉淀控制着许多自然和工程系统中有毒铬 (Cr) 的归宿和迁移。土壤和工程表面的有机涂层无处不在;然而,这些有机涂层对铁/ 铬氢氧化物共沉淀的机械控制机制还了解甚少。在此,在腐殖酸 (HA)、海藻酸钠 (SA) 和牛血清白蛋白 (BSA) 的模型有机涂层上进行了铁/ 铬氢氧化物共沉淀实验。有机物通过与羧基 (-COOH) 的配体交换与 SiO 键合,而 -COOH 的吸附量和 p 值控制着涂层的表面电荷。吸附的有机膜对 Fe/Cr 离子和 Fe/Cr 氢氧化物颗粒也具有不同的络合能力,导致异质沉淀物的量(在 BSA(-NH) > HA > SA(-COOH))和组成(Cr/Fe 摩尔比:BSA(-NH) > HA > SA(-COOH))有显著差异。带负电荷的 -COOH 吸引更多的 Fe 离子和水解的 Fe/Cr 物种的低聚物,从而促进 Fe/Cr 氢氧化物纳米颗粒的异质沉淀。含 -NH 的有机涂层在酸性 pH 下带正电荷,因为官能团的 p 值较高,限制了阳离子的吸附和共沉淀的形成。同时,-NH 涂层附近较高的局部 pH 值促进了 Cr(OH) 的形成。本研究深入了解了异质 Fe/Cr 氢氧化物在有机物上的共沉淀,这对于成功进行自然和工程环境中的 Cr 修复和去除,以及用于材料应用的 Cr 掺杂铁(氧)氢氧化物的合成都至关重要。