Abstract
Use polyvinyl alcohol-Na-alginate (PVA-SA) to immobilize Lentinus edodes residue for Cd2+ removal. In a single-metal solution, the biosorption of Cd2+ reached equilibrium within 7 h which can be well described by a pseudo-second-order model, with equilibrium biosorption 0.2008 mg/g; 4–7 was the suitable pH value for Cd2+ biosorption by immobilized fungus, a much wider range than that required by mobilized fungus. Unlike the single-metal solution, the Cd2+ biosorption ratio in a two-metal solution increased linearly as the pH values increased. When the concentration of the interferential ion (Cu2+/Pb2+) increased, Cd2+ biosorption decreased significantly (p = 0.01). Isotherm analysis showed that Cd2+ biosorption increased as the initial concentration in a single-metal solution increased. When the initial Cd2+ concentration in the two-metal solution increased, the biosorption increased at first, but when the Cd2+ concentration was over 90 mg/g, a remarkable decrease occurred. Langmuir, Freundlich, Dubinin–Radushkevich and Langmuir–Freundlich isotherm models were fit to the experimental data. The Langmuir model fit the Cd2+ isotherm biosorption best, with correlation coefficients of 0.9981 in Cd2+ single-metal solution and 0.9291 in a Cd2+–Pb2+ solution. The D–R isotherm fit the Cd2+ isotherm biosorption in the Cd2+–Cu2+ solution with a correlation coefficient of 0.9623.