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Sustainable Soil Washing: Shredded Card Filtration of Potentially Toxic Elements after Leaching from Soil Using Organic Acid Solutions

机译:可持续的土壤洗涤:使用有机酸溶液从土壤中浸出后对潜在的有毒元素进行切丝过滤

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摘要

Shredded card (SC) was assessed for use as a sorbent of potentially toxic elements (PTE) carried from contaminated soil in various leachates (oxalic acid, formic acid, CaCl2, water). We further assessed SC for retention of PTE, using acidified water (pH 3.4). Vertical columns and a peristaltic pump were used to leach PTE from soils (O and A/B horizons) before passing through SC. Sorption onto SC was studied by comparing leachates, and by monitoring total PTE contents on SC before and after leaching. SC buffers against acidic soil conditions that promote metals solubility; considerable increases in solution pH (+4.49) were observed. Greatest differences in solution PTE content after leaching with/without SC occurred for Pb. In oxalic acid, As, Cd, Pb showed a high level of sorption (25, 15, and 58x more of the respective PTE in leachates without SC). In formic acid, Pb sorption was highly efficient (219x more Pb in leachate without SC). In water, only Pb showed high sorption (191x more Pb in leachate without SC). In desorption experiments, release of PTE from SC varied according to the source of PTE (organic/mineral soil), and type of solvent used. Arsenic was the PTE most readily leached in desorption experiments. Low As sorption from water was followed by fast release (70% As released from SC). A high rate of Cd sorption from organic acid solutions was followed by strong retention (~12% Cd desorption). SC also retained Pb after sorption from water, with subsequent losses of ≤8.5% of total bound Pb. The proposed use of this material is for the filtration of PTE from extract solution following soil washing. Low-molecular-mass organic acids offer a less destructive, biodegradable alternative to strong inorganic acids for soil washing.
机译:切碎的卡片(SC)被评估为用作各种沥滤液(草酸,甲酸,CaCl2,水)中污染土壤携带的潜在有毒元素(PTE)的吸附剂。我们使用酸化水(pH 3.4)进一步评估了SC对PTE的保留。在通过SC之前,使用垂直柱和蠕动泵从土壤(O和A / B层)中浸出PTE。通过比较浸出液,并通过监测浸出前后SC上总PTE含量,研究了对SC的吸附。 SC缓冲液可抵抗酸性土壤条件,从而提高金属的溶解度;观察到溶液pH值显着增加(+4.49)。 Pb浸出后,溶液中PTE含量的最大差异。在草酸中,As,Cd,Pb表现出较高的吸附水平(不含SC的渗滤液中的PTE分别多25、15和58x)。在甲酸中,Pb的吸附效率很高(不含SC的渗滤液中的Pb含量高219倍)。在水中,只有Pb表现出高吸附性(不含SC的渗滤液中Pb含量高191倍)。在解吸实验中,SC中PTE的释放随PTE的来源(有机/矿物土壤)和所用溶剂的类型而异。在解吸实验中,砷是最容易浸出的PTE。从水中的低砷吸附随后快速释放(70%的砷从SC释放)。 Cd从有机酸溶液中的吸附速率很高,但保留力强(Cd解吸量约为12%)。从水中吸收后,SC还保留了Pb,其后续损失≤总结合Pb的8.5%。该材料的建议用途是在土壤洗涤后用于从提取液中过滤PTE。低分子质量有机酸为土壤洗涤提供了破坏性强,可生物降解的强无机酸替代品。

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