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Lability, solubility and speciation of Cd, Pb and Zn in alluvial soils of the River Trent catchment UKf

机译:特伦特河集水区UKf冲积土壤中Cd,Pb和Zn的不稳定性,溶解度和形态

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Alluvial soils can store a wide range of metal contaminants originating from point and diffuse sources. The biological health of these soils is important as they act as an interface between terrestrial and aquatic environments, therefore playing an important role in maintaining the quality of surface waters. The aim of this work was to examine the lability, solubility and bioavailability of Pb, Zn and Cd in the top (0-15 cm) and sub soil (35-50 cm) of metal contaminated alluvial soils from the Trent catchment, U.K. Samples (n = 46) were collected from within 10 m of the river bank. Sources of contamination include historical mining, industry, sewage treatment works and energy production. Enrichment factors based on total metal concentrations showed that contamination in soils declined with distance from the mining areas before rising again as a result of general urbanisation and identified point sources (e.g. river dredging activities). Pore waters were extracted and isotopic dilution and single extraction assays were undertaken on the soils to assess the lability and solubility of the metals. Multi-element isotopic dilution assays were used to determine the labile pool or £-value of these metals in the soil. E-value concentrations were found to range between 0.5 and 14 mg kg~(-1), 11-350 mg kg~(-1) and 25-594 mg kg~(-1) for Cd, Pb and Zn, respectively. Comparison of the E-value assay with the EU standard extraction assay for trace element availability (0.05 M EDTA) showed that EDTA extractions generally over-estimated the f-value for Zn and Pb, with the difference being greater as contamination levels increased. Bioavailability of the metals was assessed by speciating the pore waters [M_(soi)] using WHAM 7 to obtain estimates of free ion activities (M~(2+)). Values of (M~(2+)) were compared to published 'median critical limits' for soils that estimate levels of protection for 95% of biological species. For each of the three metals, (M~(2+)) was found to exceed these critical limits at some sites. Solubility of the metals are reported using K_d values expressed using both the total and E-value as the solid phase. Finally we examine the use of different metal pools (total, E-value, EDTA-extractable) and different measures of Fe oxide pools (total, free total, free amorphous), in predicting [M_(soi)] concentrations and (M~(2+)) using WHAM 7 in assemblage modelling mode. Overall best simultaneous model predictions for the three metals were obtained using the f-values. Larger over-estimates of [M_(so)|] and (M~(2+)) were produced using the EDTA and total metal pools whereas a better fitting in the prediction was obtained when models used either the total or the free total FeO_x pools.
机译:冲积土壤可以储存来自点源和扩散源的各种金属污染物。这些土壤的生物健康非常重要,因为它们充当了陆地和水生环境之间的界面,因此在维持地表水质量方面发挥着重要作用。这项工作的目的是检查英国特伦特河集水区被金属污染的冲积土壤的顶部(0-15厘米)和亚土壤(35-50厘米)中铅,锌和镉的不稳定性,溶解度和生物利用度。 (n = 46)来自河岸10 m以内。污染源包括历史采矿,工业,污水处理厂和能源生产。基于总金属浓度的富集因子表明,土壤污染随距矿区的距离而减少,然后由于普遍的城市化和确定的点源(例如河道疏activities活动)而再次增加。提取孔隙水,并在土壤上进行同位素稀释和单次提取测定,以评估金属的不稳定性和溶解性。用多元素同位素稀释法测定土壤中这些金属的不稳定库或pool值。发现Cd,Pb和Zn的E值浓度分别在0.5和14 mg kg〜(-1),11-350 mg kg〜(-1)和25-594 mg kg〜(-1)之间。 E值分析与欧盟标准提取方法中痕量元素的可利用性(0.05 M EDTA)的比较表明,EDTA提取通常高估了Zn和Pb的f值,随着污染水平的提高,差异更大。通过使用WHAM 7指定孔隙水[M_(soi)]来评估金属的生物利用度,以获得自由离子活性(M〜(2+))的估计值。将(M〜(2+))的值与已发布的土壤“中位临界极限”进行比较,以评估对95%的生物物种的保护水平。对于这三种金属中的每一种,在某些位置发现(M〜(2+))都超过了这些临界限值。使用K_d值报告金属的溶解度,K_d值使用总和E值作为固相表示。最后,我们研究了在预测[M_(soi)]浓度和(M〜)时使用不同的金属熔池(总量,E值,EDTA可萃取物)和不同的Fe氧化物熔池量度(总量,游离总量,游离无定形)。 (2+))在装配建模模式下使用WHAM 7。使用f值获得了三种金属的总体最佳同时模型预测。使用EDTA和总金属池产生了更大的[M_(so)|]和(M〜(2+))高估,而当模型使用总FeO_x或自由总FeO_x时,则可以更好地拟合预测。池。

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