首页> 外文会议>International Plant Nutrition Colloquium; 2005; Beijing >Effects of phosphate amendments on the bioavailability of lead, cadmium and zinc in metal-contaminated soil
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Effects of phosphate amendments on the bioavailability of lead, cadmium and zinc in metal-contaminated soil

机译:磷酸盐改良剂对金属污染土壤中铅,镉和锌生物利用度的影响

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Phosphate compounds of metis (e.g., pyromorphite M_5 (PO_4)_3-(X), where M= Pb, Cd and Zn; X= OH, F, or Cl) are comparatively insoluble and their formation in contaminated soils may be a cost-effective way to reduce contaminant bioavailability in soils To assess the efficiency of P-induced metals immobilization in soils, four chemical materials, natural hydroxyapatite (HA), mineral phosphate rock (PR), triple-superphosphate (TSP) and diammonium phosphate (DAP) were evaluated using pot experiments to determine their ability to reduce cadmium (Cd), lead (Pb), and zinc (Zn) bioavailabihty in an artificially metal-contaminated soil with three addition levels: control (CK), T1 (Cd/Pb/Zn:0.6/100/66 mg kg~(-1)) and T2 (Cd/Pb/Zn:1.5/300/200 mg kg~(-1)). Phosphate compounds were applied at 2500 mg P kg~(-1) soil for each metals addition level with five treatments: CK (control), TSP, DAP, PR and HA, respectively. The immobilization and bioavailability of Cd, Pb, and Zn were determined by plant (Brassica campestris L) uptake, scanning electron microscope (SEM), transmission electron microscope (TEM) and sequential extraction. The results showed that HA was superior to all other materials for reducing Pb, Zn and Cd uptake in shoot with reduction of 34.6-53.3% for Pb, 31.2-47.3% for Zn and 39.1-42.4% for Cd, respectively, as compared with the control treatment. The mechanisms of Pb immobilization in the soil by P-decreased Pb translocation from the plant root to shoot were identified with SEM-EDS and TEM-EDS micrographs, whereas SEM and TEM analysis identified no phosphate mineral Cd or Zn. Triple super phosphate was generally less effective for reducing Cd, Pb and Zn in plant tissues. Sequential extraction results indicated that the addition of phosphate amendments convert soil Pb, Zn and Cd from non-residual fractions to residual fraction substantially. In general, the effect of different phosphates on plant uptake of Pb, Zn and Cd followed the order: HA > PR > DAP > TSP. The results suggested that HA and PR amendments could significantly reduce the bioavailability and increase the geochemical stability of soil Pb, Zn and Cd, so there is a potential to use them for in-situ remediation in metal-contaminated soils.
机译:陨石的磷酸盐化合物(例如,焦晶石M_5(PO_4)_3-(X),其中M = Pb,Cd和Zn; X = OH,F或Cl)相对不溶,并且在受污染的土壤中形成磷盐可能会导致成本上升。减少土壤中污染物生物利用度的有效方法为了评估P诱导的金属在土壤中的固定效率,四种化学材料,天然羟基磷灰石(HA),矿物磷酸盐岩(PR),三重过磷酸盐(TSP)和磷酸二铵(DAP)通过盆栽试验评估了其在三种添加水平下的人工金属污染土壤中降低镉(Cd),铅(Pb)和锌(Zn)生物利用度的能力:对照(CK),T1(Cd / Pb / Zn:0.6 / 100/66 mg kg·(-1))和T2(Cd / Pb / Zn:1.5 / 300/200 mg kg·(-1))。对于每种金属添加水平,分别在2500 mg P kg〜(-1)的土壤上施用磷酸盐化合物,并分别进行五种处理:对照(​​对照),TSP,DAP,PR和HA。 Cd,Pb和Zn的固定化和生物利用度通过植物(Brassica campestris L)的吸收,扫描电子显微镜(SEM),透射电子显微镜(TEM)和顺序萃取来确定。结果表明,相比于其他材料,HA降低了芽中铅,锌和镉的吸收,与铅相比分别降低了34.6-53.3%,锌31.2-47.3%和39.1-42.4%。对照治疗。通过SEM-EDS和TEM-EDS显微照片确定了P减少了Pb从植物根部到芽的​​易位性,从而将Pb固定在土壤中的机制,而SEM和TEM分析未发现磷矿物质Cd或Zn。三重过磷酸钙通常在减少植物组织中的Cd,Pb和Zn方面效果较差。连续萃取结果表明,添加磷酸盐改良剂可将土壤中的Pb,Zn和Cd从非残留组分基本上转化为残留组分。通常,不同磷酸盐对植物吸收Pb,Zn和Cd的影响顺序为:HA> PR> DAP> TSP。结果表明,HA和PR改良剂可显着降低土壤中Pb,Zn和Cd的生物利用度并提高其地球化学稳定性,因此有可能将其用于金属污染土壤的原位修复。

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