ISTO UMR 7327-CNRS, Université d'Orléans Campus Géosciences, 1A, rue de la Férollerie, 45071, Orléans cedex 2, France,
Environ Sci Pollut Res Int. 2014 Sep;21(17):10307-19. doi: 10.1007/s11356-014-2938-0. Epub 2014 May 9.
The remediation of copper-contaminated soils by aided phytostabilisation in 16 field plots at a wood preservation site was investigated. The mobility and bioavailability of four potentially toxic trace elements (PTTE), i.e., Cu, Zn, Cr, and As, were investigated in these soils 4 years after the incorporation of compost (OM, 5 % w/w) and dolomite limestone (DL, 0.2 % w/w), singly and in combination (OMDL), and the transplantation of mycorrhizal poplar and willows. Topsoil samples were collected in all field plots and potted in the laboratory. Total PTTE concentrations were determined in soil pore water (SPW) collected by Rhizon soil moisture samplers. Soil exposure intensity was assessed by Chelex100-DGT (diffusive gradient in thin films) probes. The PTTE phytoavailability was characterized by growing dwarf beans on potted soils and analyzing their foliar PTTE concentrations. OM and DL, singly and in combination (OMDL), were effective to decrease foliar Cu, Cr, Zn, and As concentrations of beans, the lowest values being numerically for the OM plants. The soil treatments did not reduce the Cu and Zn mineral masses of the bean primary leaves, but those of Cr and As decreased for the OM and DL plants. The Cu concentration in SPW was increased in the OM soil and remained unchanged in the DL and OMDL soils. The available Cu measured by DGT used to assess the soil exposure intensity correlated with the foliar Cu concentration. The Zn concentrations in SPW were reduced in the DL soil. All amendments increased As in the SPW. Based on DGT data, Cu availability was reduced in both OM and OMDL soils, while DL was the most effective to decrease soil Zn availability.
在木材防腐剂场的 16 个野外试验区中,通过辅助植物稳定化来修复铜污染土壤。在掺入堆肥(OM,5%w/w)和白云石石灰石(DL,0.2%w/w)、单独和组合(OMDL)以及移植菌根杨树和柳树后 4 年,研究了这些土壤中四种潜在有毒痕量元素(PTTE),即 Cu、Zn、Cr 和 As 的迁移性和生物可利用性。从所有野外试验区采集表层土壤样本并在实验室盆栽。通过 Rhizon 土壤水分采样器收集土壤孔隙水(SPW)并测定总 PTTE 浓度。通过 Chelex100-DGT(薄膜扩散梯度)探针评估土壤暴露强度。通过在盆栽土壤上种植矮豆并分析其叶片 PTTE 浓度来表征 PTTE 的植物可利用性。OM 和 DL 单独和组合(OMDL)都能有效降低豆类叶片的 Cu、Cr、Zn 和 As 浓度,OM 植物的数值最低。土壤处理并未降低豆类初生叶的 Cu 和 Zn 矿质质量,但 OM 和 DL 植物的 Cr 和 As 矿质质量降低。OM 土壤中 SPW 中的 Cu 浓度增加,而 DL 和 OMDL 土壤中的 Cu 浓度保持不变。用于评估土壤暴露强度的 DGT 测量的有效 Cu 与叶片 Cu 浓度相关。DL 土壤中 SPW 中的 Zn 浓度降低。所有添加剂均增加了 SPW 中的 As。基于 DGT 数据,OM 和 OMDL 土壤中的 Cu 可用性降低,而 DL 是降低土壤 Zn 可用性最有效的方法。