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EVALUATING THE CONTRIBUTION OF SOIL PROPERTIES TO MODIFYING LEAD PHYTOAVAILABILITY AND PHYTOTOXICITY

机译:评估土壤性质对改善铅的植物有效性和植物毒性的贡献

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Soil properties affect Pb bioavailability to human and ecological receptors and should be considered during ecological risk assessment of contaminated soil. We used path analysis (PA) to determine the relative contribution of soil properties (pH, organic C [OC], amorphous Fe and Al oxides [FEAL], and cation-exchange capacity [CEC]) in modifying Pb bioavailability. The response of biological endpoints (bioaccumulation and dry matter growth [DMG]) of lettuce (Lactuca sativa) grown on 21 Pb-spiked (2,000 mg/kg) soils were determined. Lettuce tissue Pb ranged from 3.22 to 233 mg/kg, and relative DMG ranged from 2.5 to 88.5% of their respective controls. Simple correlation showed strong relationships between CEC and OC (p < 0.01) and weaker relationships between pH and FEAL (p < 0.05) and Pb bioaccumulation. Results of PA suggest that soil pH increased the negative surface charge of organic matter and clay, thereby increasing CEC and decreasing Pb bioaccumulation. Also, the direct effect of OC on tissue Pb can be attributed to formation of surface Pb complexes by organic matter functional group ligands. Increased OC and/or CEC reduced Pb solubility and bioavailability in the 21 soils in the present study. The relative importance of soil properties likely will vary between studies employing different soils. Soil properties should be considered during the ecological risk assessment of metal in contaminated soils. Path analysis is useful for ecological studies involving soils with a wide range of physicochemical properties and can assist in site risk assessment of metals and remediation decisions on contaminated sites.
机译:土壤特性会影响人体和生态受体对铅的生物利用度,因此在评估受污染土壤的生态风险时应考虑到这一点。我们使用路径分析(PA)来确定土壤性质(pH,有机碳[OC],无定形铁和铝氧化物[FEAL]以及阳离子交换容量[CEC])在改变铅生物利用度方面的相对贡献。确定了在21种掺铅(2,000 mg / kg)的土壤上生长的莴苣(Lactuca sativa)的生物学终点(生物积累和干物质生长[DMG])的响应。生菜组织中Pb的范围为3.22至233 mg / kg,相对DMG的范围为相应控件的2.5至88.5%。简单的相关性表明,CEC和OC之间的关系很强(p <0.01),而pH和FEAL之间的关系却很弱(p <0.05)和Pb生物积累。 PA的结果表明,土壤pH值增加了有机物和粘土的负表面电荷,从而增加了CEC并降低了Pb的生物积累。而且,OC对组织Pb的直接作用可归因于有机物官能团配体形成的表面Pb配合物。在本研究中,增加的OC和/或CEC降低了21种土壤中Pb的溶解度和生物利用度。在使用不同土壤的研究之间,土壤性质的相对重要性可能会有所不同。在对污染土壤中的金属进行生态风险评估时,应考虑土壤特性。路径分析对于涉及具有多种理化性质的土壤的生态研究非常有用,并且可以协助对金属进行现场风险评估并在受污染的现场进行补救决策。

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