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In this research, high strength ceramsite was sintered by zinc contaminated soil and red mud. In addition, the influence of sintering temperature and red mud addition on ceramsite properties and Zn immobilization were investigated, and the Zn immobilization mechanisms were determined. The X-ray diffraction (XRD) analysis, scanning electron microscopy (SEM-EDS), and BCR sequential extraction technique were used to determine the crystal phases, microstructures, and Zn immobilization. Under the optimum synthesis conditions (sintering temperature of 1150 °C and the red mud addition of 5%), the sintered ceramsite exhibited a Zn loss rate of 10.31%, Zn leaching concentration of 0.13 mg/L (performed by rotating vibration device), bulk density of 1052.6 kg/m3, 1 h water absorption of 1.06%, and cylindrical compressive strength of 27.06 MPa, implying that the ceramsite obtained under this conditions not only meets the Chinese National Standards and has no environmental risk. High temperature and the addition of red mud were beneficial to the immobilization of Zn in ceramsite. The main immobilization mechanism of Zn in ceramsite was the formation of ZnFe x Al 2−x O 4 spinel and the encapsulation of glass phase. Thus, Zn can be immobilized effectively by ceramsite prepared from zinc contaminated soil and red mud at high temperature. [ABSTRACT FROM AUTHOR]

With rapid developments in livestock and poultry farming, antibiotics and heavy metals are entering the soil environment as feed additives. However, their relationships with antibiotic resistance genes (ARGs), microorganisms, and environmental factors are unclear. In this study, cadmium (Cd) and sulfadiazine (SD) were selected as representative heavy metal and antibiotic substances, respectively, to investigate the relationships among environmental factors, microorganisms, mobile genetic elements (MGEs), and ARGs. Addition of Cd and SD, both individually and in combination, increased the abundances of total ARGs and MGEs. The abundance of total ARGs increased by 0.89-fold and 1.06-fold in C2 and C8 (only-Cd-added groups), 1.61-fold and 6.53-fold in S10 and S100 (only-SD-added groups), and 7.29-fold, 7.62-fold, 2.32-fold, and 6.80-fold in C2S10, C2S100, C8S10, and C8S100 (groups with Cd and SD in combinations), respectively. Proteobacteria and Bacteroidetes were the most abundant bacterial phyla. MGEs (especially intI1) had the greatest impact on ARGs and played a crucial role in their propagation and expression. Exploring the effects of heavy metals and antibiotics in soil on ARGs is important for comprehensively assessing their ecological and environmental risks to ARGs. [Display omitted] [ABSTRACT FROM AUTHOR]