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Lead and Arsenic Uptake by Leafy Vegetables Grown on Contaminated Soils: Effects of Mineral and Organic Amendments

机译:在污染土壤上种植的带叶蔬菜对铅和砷的吸收:矿物质和有机物的影响

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To assess strategies for mitigating Pb and As transfer into leafy vegetables from contaminated garden soils, we conducted greenhouse experiments using two field-contaminated soils amended with materials expected to reduce metal phytoavailability. Lettuce and mustard greens grown on these soils were analyzed by ICP-MS, showing that some Pb and As transfer into the vegetables occurred from both soils tested, but plant Pb concentrations were highly variable among treatment replicates. Soil-to-plant transfer was more efficient for As than for Pb. Contamination of the leaves by soil particles probably accounted for most of the vegetable Pb, since plant Pb concentrations were correlated to plant tissue concentrations of the immobile soil elements Al and Fe. This correlation was not observed for vegetable As concentrations, evidence that most of the soil-to-plant transfer for this toxic metal occurred by root uptake and translocation into the above-ground tissues. A follow-up greenhouse experiment with lettuce on one of the two contaminated soils revealed a lower and less variable foliar Pb concentration than observed in the first experiment, with evidence of less soil particle contamination of the crop. This reduced transfer of Pb to the crop appeared to be a physical effect attributable to the greater biomass causing reduced overall exposure of the above-ground tissues to the soil surface. Attempts to reduce soil Pb and As solubility and plant uptake by amendment at practical rates with stabilizing materials, including composts, peat, Ca phosphate, gypsum, and Fe oxide, were generally unsuccessful. Only Fe oxide reduced soluble As in the soil, but this effect did not persist. Phosphate amendment rapidly increased soil As solubility but had no measurable effect on either soil Pb solubility or concentrations of Pb or As in the leafy vegetables. The ineffectiveness of these amendments in reducing Pb transfer into leafy vegetables is attributed in this study to the low initial Pb solubility of the studied soils and the fact that the primary mechanism of Pb transfer is physical contamination.
机译:为了评估缓解从受污染的花园土壤中将铅和砷转移到叶菜类蔬菜中的策略,我们进行了温室实验,使用了两种经田地污染的土壤,并改良了有望降低金属植物利用率的材料。通过ICP-MS分析了在这些土壤上生长的生菜和芥菜,表明两种测试土壤都发生了向蔬菜中的铅和砷转移,但是在处理重复过程中,植物铅的浓度变化很大。从土壤到植物的转移对砷而言比对铅更有效。由于植物Pb的浓度与固定的土壤元素Al和Fe的植物组织浓度相关,因此土壤颗粒对叶片的污染可能是大部分蔬菜Pb的原因。对于蔬菜中的As浓度未观察到这种相关性,这证明该有毒金属从土壤到植物的大部分转移是通过根部吸收和易位到地上组织而发生的。在两个受污染的土壤中的一个上进行的莴苣后续温室试验显示,与第一个实验相比,叶面铅的浓度较低且变化较小,这表明作物的土壤颗粒污染较少。铅向作物中转移的减少似乎是一种物理效应,这归因于生物量的增加,从而导致地上组织暴露于土壤表面的总体暴露减少。尝试通过以稳定的速率(包括堆肥,泥炭,磷酸钙,石膏和氧化铁)稳定化的添加量来降低土壤中Pb和As的溶解度以及通过吸收植物吸收植物的尝试通常是不成功的。仅氧化铁减少了土壤中的可溶性砷,但这种作用并未持续。磷酸盐改良剂迅速增加了土壤As的溶解度,但对土壤Pb的溶解度或叶菜类蔬菜中Pb或As的浓度均没有可测量的影响。在本研究中,这些改良剂不能有效减少铅向叶类蔬菜中的转移,这归因于所研究土壤的初始铅溶解度较低,而且铅转移的主要机理是物理污染这一事实。

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