Department of Agroenvironmental Research, IMIDRA, Alcalá de Henares, 28800, Madrid, Spain.
Department of Agroenvironmental Research, IMIDRA, Alcalá de Henares, 28800, Madrid, Spain.
J Environ Manage. 2020 Dec 15;276:111073. doi: 10.1016/j.jenvman.2020.111073. Epub 2020 Sep 8.
This work investigates the mechanisms determining Cr speciation and availability in two different soils polluted with two chromium sources (an industrial sludge, highly polluted with Cr, and Cr(VI) solution) and the influence of these parameters on the recovery of the soil functions related with biological quality and plant growth. The experiment was carried out in greenhouse conditions using 36 pots of 17 kg for the growth of Silene vulgaris for 21 months. Logistic Regression Model using Lasso estimator shows that soil organic matter (SOM) and pH control Cr availability in studied soils. In soils treated with the sludge, X ray Absorption spectroscopy showed that Cr was present as Cr(III), biological quality indicators increased and plants were able to grow. However, in soils polluted with Cr(VI), Cr availability was significantly different in the two soils. In the alkaline and poor in organic matter soil, 12% of Cr(VI) remained in the soil leading to the decrease of soil quality indicators and the total inhibition of plant growth. In the neutral soil, Cr(VI) was totally reduced to Cr(III) by soil organic matter (SOM), quality indicators were not affected and plants grown properly. Infrared Spectroscopy showed that different functional groups reacted with Cr in the two soils. This study highlights the importance to understand the mechanisms underlaying Cr redox and adsorption reactions in Cr polluted soils as they determine the potential recovery of the functions related with biological quality indicators and plant growth. The methodology proposed allows this study in complex soil samples at realistic concentrations and may be useful for risk assessment and for the planning of managing strategies in Cr polluted soils.
本研究旨在探讨两种不同铬污染土壤中铬形态和生物有效性的决定机制,以及这些参数对与生物质量和植物生长相关的土壤功能恢复的影响。该实验在温室条件下进行,使用 36 个 17 公斤的花盆,种植普通矢车菊(Silene vulgaris)21 个月。使用套索估计量的逻辑回归模型表明,土壤有机质(SOM)和 pH 值控制着研究土壤中铬的生物有效性。在使用污泥处理的土壤中,X 射线吸收光谱表明铬主要以 Cr(III)的形式存在,生物质量指标增加,植物能够生长。然而,在受 Cr(VI)污染的土壤中,两种土壤中铬的生物有效性有显著差异。在碱性、有机质含量低的土壤中,有 12%的 Cr(VI)仍留在土壤中,导致土壤质量指标下降,植物生长完全受到抑制。在中性土壤中,Cr(VI)被土壤有机质(SOM)完全还原为 Cr(III),质量指标不受影响,植物生长正常。红外光谱表明,两种土壤中不同的功能基团与铬发生反应。本研究强调了理解铬污染土壤中铬氧化还原和吸附反应机制的重要性,因为这些机制决定了与生物质量指标和植物生长相关的土壤功能的潜在恢复能力。所提出的方法允许在实际浓度下对复杂的土壤样品进行这项研究,这对于风险评估和铬污染土壤管理策略的规划可能是有用的。