Mineral Composition and Elemental Oxide Changes in Heat-Affected Soils and the Implications on Heavy Metal Immobilization by Sewage Sludge

This paper investigated how increased soil temperatures affect soil mineralogy and major and trace element oxide concentrations and the implications of these effects on the mobility of potentially toxic elements (PTEs) in heat-affected soils amended with sewage sludge. The aim was to determine the efficiency of sewage sludge as an immobilizer of PTEs in heat-affected PTE-contaminated soils. Soil samples were heated to 150 °C, 300 °C, 500 °C, and 750 °C and later amended with stabilized sewage sludge at different rates. The concentrations of arsenic (As), chromium (Cr), cobalt (Co), copper (Cu), lead (Pb), nickel (Ni), and zinc (Zn) in the different geochemical fractions of the soils were determined before heating, after heating, and after sewage sludge application. Increased soil temperatures affected the mineral assemblage and the concentrations of some major and trace element oxides and the degree of weathering of the soils. These changes were, however, insignificant. The segregation of PTEs into the different soil geochemical fractions before and after heating varied. High soil temperatures resulted in an increase in PTE concentrations in the non-residual fractions of the soil (F1, F2, and F3) with a consequent increase in their mobility. The application of sewage sludge to heated and unheated soils reduced PTE concentrations in the F1 and F2 fractions of both soils, whereas it increased PTE concentrations in the F3 and F4 fractions by up to 30% for As and Cu, 20% for Cd, 25% for Co, 60% for Cr and Ni, 50% for Pb, and 55% for Zn. Significant immobilization of the PTEs was observed in the heat-affected soils that received higher amount of sewage sludge. Fire events could increase the mobility of PTEs in soils, but sewage sludge could still effectively immobilize these PTEs, although it needs to be applied at higher application rates.