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We investigated the biosorption characteristics of thallium (I) ions using dead biomass of Pseudomonas fluorescens strains as biosorbents. The biosorbents were characterized by Fourier transform infrared spectroscopy (FT-IR) and a scanning electron microscope (SEM). The effects of different environmental factors such as initial Tl concentration, initial solution pH, biomass dosage, and contact time were evaluated. The maximum adsorption capacity was found to be 93.76 mg/g at an optimum initial pH of 5.0, a contact time of 60 min, a biomass of 0.5 g/L, and an initial Tl concentration of 50 μg/mL. The biosorption process can be well defined by the Langmuir isotherm (R²= 0.9967). The biosorption kinetics were better described by the pseudo second-order model (R²= 0.9950) than the pseudo first-order one. The analysis of (FT-IR) indicates that the main functional groups responsible for adsorption of Tl (I) were hydroxyl, carboxyl, and amino groups. SEM analysis verifies an obvious surface morphology change of adsorbed biomass. The results presented in this study show that the Pseudomonas fluorescens could be an effective, low-cost, and environmentally friendly biosorbent for removing Tl (I) from aqueous solution.
The karst terrain of Guizhou in southwestern China is ecologically fragile, but has undergone severe heavy metal contamination. To assess such contamination, the spatial distribution of cadmium (Cd) within soils was studied in a lead (Pb)-zinc (Zn) smelting area, coal mining area, Pb-Zn mining area, sewage irrigation area, and an uncontaminated area. Cd concentrations were highest in topsoil, with the highest value of 23.36 mg/kg in the Pb-Zn mining area and lowest value of 0.46 mg/kg in the uncontaminated area. Cd content decreased from 0 to 0.8 m depth, then sharply increased, reflecting Cd precipitation within the contaminated soil profiles. Migration of Cd within the soil was affected by organic content in the Pb-Zn smelting area (R² = 0.99**), coal mining area (r = 0.72*), and Pb-Zn mining area (r = 0.73*). In contrast, Cd accumulated within a clay horizon in the uncontaminated area, where the correlation between Cd and specific surface area was 0.78**; Cd concentrations reached 2.11 mg/kg within this horizon. Reducible, oxidizable, and acid-exchangeable fractions accounted for 60-80% of total Cd in soils having pH values of 5.05-6.86. This indicates that Cd could easily transfer from soil to food or water, leading to human health and environmental risks.
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