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Modeling ferricyanide adsorption on goethite: Basics and applications

机译:模拟铁氰化物在针铁矿上的吸附:基础和应用

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Ferricyanicle, [Fe-III(CN)(6)](3-), is an anthropogenic and potentially toxic contaminant in soil. Its adsorption on goethite has been previously studied, but not evaluated with a surface complexation model (SCM) considering the effects of pH and ionic strength. Therefore, we carried out batch experiments with ferricyanide and goethite suspensions with different ferricyanide concentrations (0.075 mM and 0.15 mM), ionic strengths (0.01 and 0.1 M), and pH (ranging from 4 to 7.4). Adsorption data were then interpreted with the 1-pK Stern and the charge distribution model assuming monodentate inner-sphere ferricyanide surface complexes on goethite (Ig K = 10.6), which are known from infrared spectroscopy. Furthermore, we applied the SCM to ferricyanide adsorption in previous studies on ferricyanide adsorption in the presence of sulfate and on the solubility of Fe-cyanide complexes in a suspension of a loess loam. The SCM correctly reflected ferricyanide adsorption in the batch experiments as well as the effects of pH and ionic strength. The SCM also described ferricyanide adsorption in the presence of sulfate, because the ferricyanide adsorption measured and that modeled were significantly correlated (R-2 = 0.80). Furthermore, we applied the SCM to a study on the solubility of Fe-cyanide complexes in soil under varying redox conditions so that ferricyanide adsorption on goethite and precipitation of Fe-cyanide complexes were considered. The actual ferricyanide concentrations were rather reflected when applying the SCM compared to those modeled in an approach in which exclusively precipitation was taken into account. We conclude that ferricyanide adsorption on goethite should be included into geochemical modeling approaches on the mobility of Fe-cyanide complexes in subsoils.
机译:铁yan [Fe-III(CN)(6)](3-)是人为和潜在有毒的土壤污染物。先前已经研究了其在针铁矿上的吸附,但考虑到pH和离子强度的影响,尚未使用表面络合模型(SCM)对其进行评估。因此,我们对具有不同铁氰化物浓度(0.075 mM和0.15 mM),离子强度(0.01和0.1 M)以及pH(范围从4到7.4)的铁氰化物和针铁矿悬浮液进行了批量实验。然后用1-pK Stern和电荷分布模型解释吸附数据,该模型假定针铁矿上的单齿内球铁氰化物表面配合物(Ig K = 10.6),这是红外光谱已知的。此外,我们在以前的研究中将SCM应用于铁氰化物的吸附,研究了硫酸盐存在下铁氰化物的吸附以及黄土壤土悬浮液中Fe-氰化物配合物的溶解度。 SCM正确反映了分批实验中铁氰化物的吸附以及pH和离子强度的影响。 SCM还描述了在硫酸盐存在下的铁氰化物吸附,因为所测量的铁氰化物吸附和模拟的铁氰化物吸附具有显着相关性(R-2 = 0.80)。此外,我们将SCM应用于研究不同氧化还原条件下铁氰化物配合物在土壤中的溶解度,从而考虑了铁氰化物在针铁矿上的吸附和铁氰化物配合物的沉淀。与仅考虑降水的方法所模拟的浓度相比,应用SCM时实际的铁氰化物浓度相当好。我们得出的结论是,铁-氰化物在针铁矿上的吸附应被包括在地球化学模型方法中,以研究铁-氰化物在地下土壤中的流动性。

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