Biosorption of lead, cadmium, copper and arsenic ions was studied using algal biomass. Mixture of green (Chlorophyta) and blue-green (Cyanophyta) algae were used in this study as biosorbent of heavy metals.
A series of experiments were carried out in a batch reactor to obtain equilibrium isotherms data for biosorption of single, binary, ternary and quaternary metals solutions. The biosorption of these metals is based on ion exchange mechanism accompanied by the release of light metals such as calcium, magnesium, potassium and sodium. Experimental parameters included pH, initial metal concentrations and temperature were studied. The optimum pH values were 3 for Pb2+, 4 for Cu2+, 5 for As3+ and Cd2+, respectively. Fourier Transformation Infrared Spectroscopy analysis was used to find the effects of functional groups of algae in biosorption process. The results showed that Pb2+ made a greater change in the functional groups of algal biomass due to the high affinity to this metal.
An ion exchange model was found suitable for describing the biosorption process. The affinity constant (K) sequence calculated for single system was KPb>KAs>KCu>KCd; these values reduced in binary, ternary and quaternary system. The experimental data showed that the biosorption of the four metals well fitted the pseudo-second order kinetics model.
A fluidized bed reactor was adopted for the continuous removal of metals. The minimum fluidization velocities of beds were found equal to 2.27 and 3.64 mm/s for particles of 0.4-0.6 and 0.6-1 mm diameters, respectively. A series of experiments were carried out on the fluidized bed reactor to obtain the breakthrough curves data for biosorption of single, binary, ternary and quaternary metals ions.
The experimental breakthrough data of four metal ions were fitted well the theoretical model. Pb2+ showed the largest breakthrough time compared with other metals demonstrating high affinity, while Cd2+ had the shortest breakthrough time. Different operating conditions were used, static bed height (correspondent to 50,100 and 150 g of algal biomass), superficial velocity (1.1Umf and 1.5 Umf) and particle diameter (0.4-0.6 and 0.6-1 mm). The variation of liquid superficial velocity from 1.1Umf to 1.5Umf resulted decreasing in biosorption capacity. The variation of particles diameter causes a small variation in biosorption capacity. The biosorption capacity order for the four systems was: Pb2+>As3+>Cu2+>Cd2+.