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高铁生物固体肥料导致共污染土壤中铅和砷形态和生物可利用性的变化。

High-iron biosolids compost-induced changes in lead and arsenic speciation and bioaccessibility in co-contaminated soils.

机构信息

University of Washington, Seattle, WA, USA.

出版信息

J Environ Qual. 2012 Sep-Oct;41(5):1612-22. doi: 10.2134/jeq2011.0297.

Abstract

The safety of urban farming has been questioned due to the potential for contamination in urban soils. A laboratory incubation, a field trial, and a second laboratory incubation were conducted to test the ability of high-Fe biosolids-based composts to reduce the bioaccessibility of soil Pb and As in situ. Lead and As bioaccessibility were evaluated using an in vitro assay. Changes in Pb, As, and Fe speciation were determined on select samples after the second laboratory incubation using μ-X-ray fluorescence mapping followed by μ-X-ray absorption near-edge structure (XANES). A compost with Fe added to wastewater treatment residuals (Fe WTR compost) added to soils at 100 g kg decreased Pb bioaccessibility in both laboratory incubations. Mixed results were observed for As. Composts tested in the field trial (Fe added as Fe powder or FeCl) did not reduce bioaccessible Pb, and limited reductions were observed in bioaccessible As. These composts had no effect on Pb bioaccessibility during the second laboratory incubation. Bulk XANES showed association of Pb with sulfates and carbonates in the control soil. μ-XANES for three points in the Fe WTR amended soil showed Pb present as Fe-sorbed Pb (88 and 100% of two points) and pyromorphite (12 and 53% of two points). Bulk XANES of the Fe WTR compost showed 97% of total Fe present as Fe. The results of this study indicate that addition of high-Fe biosolids compost is an effective means to reduce Pb accessibility only for certain types of Fe-rich materials.

摘要

由于城市土壤可能受到污染,城市农业的安全性受到了质疑。进行了实验室孵化、田间试验和第二次实验室孵化,以测试基于高铁生物固体的堆肥减少土壤中 Pb 和 As 生物可利用性的能力。使用体外测定法评估 Pb 和 As 的生物可利用性。在第二次实验室孵化后,选择部分样品进行 μ-X 射线荧光图谱分析,随后进行 μ-X 射线吸收近边结构 (XANES) 分析,以确定 Pb、As 和 Fe 形态的变化。将添加到废水处理残余物中的铁(Fe WTR 堆肥)添加到土壤中,用量为 100 g kg,在两次实验室孵化中均降低了 Pb 的生物可利用性。对于 As,观察到混合结果。在田间试验中测试的堆肥(添加的 Fe 为 Fe 粉或 FeCl)并未降低生物可利用的 Pb,并且生物可利用的 As 减少有限。这些堆肥在第二次实验室孵化过程中对 Pb 的生物可利用性没有影响。总体 XANES 显示 Pb 与对照土壤中的硫酸盐和碳酸盐结合。Fe WTR 改良土壤中三个点的 μ-XANES 显示 Pb 以 Fe 吸附的 Pb(两点中的 88%和 100%)和磷氯铅矿(两点中的 12%和 53%)存在。Fe WTR 堆肥的总体 XANES 显示 97%的总 Fe 以 Fe 形式存在。本研究结果表明,仅对于某些类型的富铁材料,添加高铁生物固体堆肥是降低 Pb 可及性的有效手段。

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