Key Laboratory of Original Agro-Environmental Pollution Prevention and Control, Ministry of Agriculture and Rural Affairs (MARA), Agro-Environmental Protection Institute, MARA, Tianjin 300191, China; Tianjin Key Laboratory of Agro-Environment and Agro-Product Safety, Agro-Environmental Protection Institute, MARA, Tianjin 300191, China.
Tianjin Key Laboratory of Agro-Environment and Agro-Product Safety, Agro-Environmental Protection Institute, MARA, Tianjin 300191, China.
Sci Total Environ. 2020 Oct 20;740:140009. doi: 10.1016/j.scitotenv.2020.140009. Epub 2020 Jun 10.
In order to simultaneously improve the remediation capability of Cd contaminated water and soil, hydroxy iron-ABsep (HyFe/ABsep) was synthesized by a two-step modified (acid-base composite treatment, and hydroxy group was by using NaOH and Fe (NO)·9HO). Results showed that HyFe/ABsep had developed pores and a rougher surface morphology, and the salt-soluble ion content was increased, surface-loaded iron species was mainly composed of FeOOH. Adsorption process of Cd by HyFe/ABsep conformed best to the preudo-second-order model and Redlich-Paterson models, respectively. The behavior over a whole range of adsorption was consistent with chemical adsorption being the rate-controlling step and the theoretical maximum adsorption capacity obtained for the HyFe/ABsep was 220.9 mg·g at 298 K, which was 4.87 times than Sep. HyFe/ABsep also had a more excellent passivation effect on available Cd in soil, being 36.83%-48.46% under the treatments of 0.5%-4% HyFe/ABsep, The structure and morphology of HyFe/ABsep were characterized through SEM-EDS, TEM, FTIR, XRD and XPS indicated that the mainly mechanisms of Cd sorption may include precipitates, ion exchange and complexation of active silanol groups. Therefore, HyFe/ABsep can employ as an effective agent for immobilization remediation of Cd contaminated water and soil.
为了同时提高 Cd 污染水和土壤的修复能力,通过两步改性(酸碱复合处理和用 NaOH 和 Fe(NO₃)₃·9H₂O 引入羟基)合成了羟基铁-ABsep(HyFe/ABsep)。结果表明,HyFe/ABsep 具有发达的孔和更粗糙的表面形态,盐溶性离子含量增加,表面负载的铁物种主要由 FeOOH 组成。HyFe/ABsep 对 Cd 的吸附过程分别最符合准二级模型和 Redlich-Paterson 模型。整个吸附范围内的行为与化学吸附一致,化学吸附是速率控制步骤,在 298 K 下,HyFe/ABsep 的理论最大吸附容量为 220.9 mg·g,是 Sep 的 4.87 倍。HyFe/ABsep 对土壤中有效 Cd 也具有更优异的钝化效果,在 0.5%-4%HyFe/ABsep 的处理下,有效 Cd 的钝化率为 36.83%-48.46%。SEM-EDS、TEM、FTIR、XRD 和 XPS 等方法对 HyFe/ABsep 的结构和形态进行了表征,Cd 吸附的主要机制可能包括沉淀、离子交换和活性硅醇基团的络合。因此,HyFe/ABsep 可作为一种有效的固定化修复 Cd 污染水和土壤的试剂。