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In vitro lead bioaccessibility and phosphate leaching as affected by surface application of phosphoric Acid in lead-contaminated soil.

机译:体外铅的生物可及性和磷酸盐浸出受磷酸在铅污染土壤中表面施用的影响。

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摘要

Phosphate treatment of lead-contaminated soil may be a cost-effective remedial alternative for in situ stabilizing soil Pb and reducing Pb toxicology to human. The leaching behaviors of the P added to soil surface and the effect on subsurface Pb bioaccessibility must be addressed for this remedial technology to be acceptable. A smelter-contaminated soil containing an average of 2,670 mg Pb kg(-1), collected from the Jasper County Superfund Site located in Jasper County, Missouri, was surface treated with 10 g P kg(-1) as phosphoric acid (H(3)PO(4)). Following a simulated column leaching and 90-day treatment of field plots, respectively, bioaccessible Pb, P, and pH in soil profile were measured. Surface treatment using H(3)PO(4) effectively stabilized soil Pb and reduced leachable Pb and the bioaccessibility. Phosphate leached into deeper profile significantly lowered bioaccessible Pb in subsurface. Reduction of Pb bioaccessibility increased as a linear function of increasing soil P. Although surface H(3)PO(4) treatment resulted in an enhanced leaching of added P and may increase potential risk of surface and groundwater pollution, the P leaching under field conditions is very limited. Lime addition following the treatment may reduce the leachability of added P and further immobilize soil Pb.
机译:用磷酸盐处理铅污染的土壤可能是一种经济有效的补救措施,可就地稳定土壤铅并降低铅对人的毒理作用。为了使这种修复技术能够被接受,必须解决添加到土壤表面的磷的浸出行为以及对地下铅生物可及性的影响。从密苏里州贾斯珀县贾斯珀县超级基金站点收集的平均含2,670 mg Pb kg(-1)的冶炼厂污染土壤经过10 g P kg(-1)作为磷酸的表面处理(H( 3)PO(4))。在分别对田间样地进行模拟柱浸和90天处理后,测量了土壤剖面中可生物利用的Pb,P和pH。使用H(3)PO(4)的表面处理有效地稳定了土壤Pb,减少了可浸出Pb和生物可及性。磷酸盐浸出更深的轮廓大大降低了地下的生物可及性铅。 Pb生物可及性的降低随着土壤P的增加呈线性函数增加。尽管表面H(3)PO(4)处理导致增加的P浸出并可能增加地表和地下水污染的潜在风险,但在田间条件下P浸出非常有限。处理后添加石灰可能会降低添加的P的浸出性,并进一步固定土壤Pb。

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