Department of Soil and Water Sciences, Faculty of Agriculture, University of Kafrelsheikh, 33 516, Kafr El-Sheikh, Egypt.
School of Architecture and Civil Engineering, Institute of Foundation Engineering, Water- and Waste-Management, Soil- and Groundwater-Management, University of Wuppertal, Pauluskirchstraße 7, 42285, Wuppertal, Germany.
Environ Geochem Health. 2017 Dec;39(6):1365-1379. doi: 10.1007/s10653-017-9927-4. Epub 2017 Mar 3.
The objective of this research was to investigate the effects of biosolids on the competitive sorption and lability of the sorbed Cd, Cu, Ni, Pb, and Zn in fluvial and calcareous soils. Competitive sorption isotherms were developed, and the lability of these metals was estimated by DTPA extraction following their sorption. Sorption of all metals was higher in the fluvial than in the calcareous soil. Sorption of Cu and Pb was stronger than that of Cd, Ni, and Zn in all soils. Biosolids application (2.5%) reduced the sorption of all metals especially Cu and Pb (28-43%) in both soils (especially the calcareous soil) at the lower added metal concentrations (50 and 100 mg L). However, it increased the sorption of all metals especially Pb and Cu in both soils (especially the calcareous soil; 15.5-fold for Cu) at the higher added concentrations (250 and 300 mg L). Nickel showed the highest lability followed by Cd, Zn, and Pb in both soils. Biosolids increased the lability of the sorbed Ni in the fluvial soils at all added concentrations and the lability of Cd, Pb, and Zn at 50 mg L, but decreased the lability of Cd, Pb, and Zn at 250 and 300 mg L in both soils. We conclude that at low loading rate (e.g., 50 mg L) biosolids treatment might increase the lability and environmental risk of Cd, Cu, Pb, and Zn. However, at high loading rate (e.g., 300 mg L) biosolids may be used as an immobilizing agent for Cd, Cu, Pb, Zn and mobilizing agent for Ni.
本研究旨在探讨生物固体对河流和钙质土壤中吸附态 Cd、Cu、Ni、Pb 和 Zn 的竞争吸附和生物有效性的影响。通过吸附后用 DTPA 提取来建立竞争吸附等温线,并估计这些金属的生物有效性。所有金属在河流土壤中的吸附量均高于钙质土壤。在所有土壤中,Cu 和 Pb 的吸附均强于 Cd、Ni 和 Zn。在较低的添加金属浓度(50 和 100 mg/L)下,生物固体(2.5%)的应用降低了所有金属,尤其是 Cu 和 Pb 在两种土壤(尤其是钙质土壤)中的吸附(降低幅度为 28-43%)。然而,在较高的添加浓度(250 和 300 mg/L)下,它增加了所有金属,尤其是 Pb 和 Cu 在两种土壤中的吸附(尤其是钙质土壤;Cu 增加 15.5 倍)。在两种土壤中,Ni 的生物有效性最高,其次是 Cd、Zn 和 Pb。生物固体增加了河流土壤中吸附态 Ni 在所有添加浓度下的生物有效性以及 Cd、Pb 和 Zn 在 50 mg/L 下的生物有效性,但降低了两种土壤中 Cd、Pb 和 Zn 在 250 和 300 mg/L 下的生物有效性。我们得出结论,在低负荷率(例如 50 mg/L)下,生物固体处理可能会增加 Cd、Cu、Pb 和 Zn 的生物有效性和环境风险。然而,在高负荷率(例如 300 mg/L)下,生物固体可被用作 Cd、Cu、Pb 和 Zn 的固定剂以及 Ni 的活化剂。