Key Laboratory of Groundwater Conservation of MWR, China University of Geosciences (Beijing), Beijing, 100083, China; Beijing Key Laboratory of Water Resources and Environmental Engineering, China University of Geosciences (Beijing), Beijing, 100083, China.
Key Laboratory of Groundwater Conservation of MWR, China University of Geosciences (Beijing), Beijing, 100083, China; Beijing Key Laboratory of Water Resources and Environmental Engineering, China University of Geosciences (Beijing), Beijing, 100083, China.
J Environ Manage. 2024 Nov;370:122404. doi: 10.1016/j.jenvman.2024.122404. Epub 2024 Sep 8.
Determining the contaminants reduction rate by dissolved ferrous iron (Fe(II)) bound to iron oxides is curial for evaluating the abiotic attenuation of contaminants in aquifers. However, few studies have assessed the contaminants reduction rate controlled by thermodynamic parameters in heterogeneous systems with different iron oxides. In this study, a linear free energy relationship (LFER) was established between the nitrobenzene reduction rate and the thermodynamic driving force (reduction potential (E) and pH) in Fe(II)-goethite-hematite co-existing systems. Results showed that the reduction rate of nitrobenzene correlated with the E of the heterogeneous system. The standard reduction potential (E) of the mixed iron oxides could be obtained by a proportionate linear combination of the single iron oxide system E. Based on this, the E of the heterogeneous systems could be calculated theoretically by combining E and the Nernst equation. Furthermore, a parallel LFER with the slope of 1 was established to associate the nitrobenzene reduction rate with E and pH. The intercept term was related to the adsorption capacity of different iron oxides towards Fe(II). The Fe(II) saturation adsorption capacity of hematite was 1.5 times higher than that of goethite. After normalizing the nitrobenzene reduction rate to the Fe(II) saturation adsorption capacity, the maximum difference in intercept terms was reduced from 37% to 15%. These findings would provide an important and feasible methodological support for the quantitative evaluation of abiotic attenuation of contaminants in groundwater.
确定与氧化铁结合的溶解二价铁 (Fe(II)) 去除污染物的速率对于评估含水层中污染物的非生物衰减至关重要。然而,很少有研究评估不同氧化铁异质体系中热力学参数控制的污染物去除速率。在这项研究中,在 Fe(II)-针铁矿-赤铁矿共存系统中,建立了硝基苯还原速率与热力学驱动力(还原电位 (E) 和 pH)之间的线性自由能关系 (LFER)。结果表明,硝基苯的还原速率与异质体系的 E 相关。混合氧化铁的标准还原电位 (E) 可以通过单氧化铁体系 E 的比例线性组合获得。基于此,通过结合 E 和能斯特方程,可以从理论上计算异质体系的 E。此外,建立了斜率为 1 的平行 LFER 来关联硝基苯还原速率与 E 和 pH。截距项与不同氧化铁对 Fe(II) 的吸附能力有关。赤铁矿的 Fe(II) 饱和吸附容量比针铁矿高 1.5 倍。将硝基苯还原速率归一化为 Fe(II) 的饱和吸附容量后,截距项的最大差异从 37%降低到 15%。这些发现将为定量评估地下水污染物的非生物衰减提供重要且可行的方法支持。