Characterization of the Adsorption of the Lead (II) by the Nonliving Biomass Spirogyra neglecta (Hasall) Kützing

Abstract

Problem statement: Conventional techniques for removing dissolved heavy metals are only practical and cost-effective when applied to high strength wastes with heavy metal ion concentrations greater than 100 ppm. The possibility of using a nonliving algal biomass to solve this problem was carried in this study. Lead (II) was used in this study because it had been reported to cause several disorders in human. Approach: The nonliving algal biomass was obtained from a filamentous green alga Spirogyra neglecta. The effects of initial concentration and contact time, pH and temperature on the biosorption of lead (II) by the nonliving algal biomass were studied. The equilibrium isotherms and kinetics were obtained from batch adsorption experiments. The surface characteristics of the nonliving algal biomass were examined using scanning electron microscope and Fourier Transformed Infrared. The maximum adsorption capacity of the nonliving algal biomass was also determined. Results: Maximum adsorption capacity of lead (II) was affected by its initial concentration. Adsorption capacity of lead (II) increased with the pH and temperature of lead (II) solution. Langmuir isothermic model fitted the equilibrium data better than the Freundlich isothermic model. The adsorption kinetics followed the pseudo-second-order kinetic model. The nonliving algal biomass exhibited acaves-like, uneven surface texture along with lot of irregular surface. FTIR analysis of the alga biomass revealed the presence of carboyl, amine and carboxyl group which were responsible for adsorption of lead (II). The maximum adsorption capacity (q max ) of lead (II) by the nonliving biomass of Spirogyra neglecta was 132 mg g −1 . Conclusion: The maximum adsorption capacity for lead (II) by the nonliving biomass of Spirogyra neglecta was higher than reported for other biosorbents. Therefore, it had a great potential for removing lead (II) from polluted water. Its use will also need to consider the various factors that affect biosorption process.

<i>Padina pavonica</i> for the Removal of Dye from Polluted Water

“…This result agreed with Murphy et al [37] which reported that metal binding to brown seaweeds showed significant participation of carboxyl group accompanied by interaction of other groups. In fact, the relative importance of these functional groups depend on factors such as the quantity of sites, their accessibility, chemical state and affinity between site and dye [37,38].…”

BIOSORPTION OF TERNARY CADMIUM, NICKEL AND COBALT IONS FROM AQUEOUS SOLUTION ONTO <i>SACCHAROMYCES CEREVISIAE</i> CELLS: BATCH AND COLUMN STUDIES

“…These metals are extremely toxic and harmful even at low concentrations. Thus heavy metal treatment of waste is important in preventing these elements entering our food chains (Hussain et al, 2009). There are several methods for removing heavy metals from wastewater, such as using inverse-phosphor, electrochemical, ion balance, chemical deposition.…”

Equilibrium and kinetic studies of Cu (II), Cd (II), Pb (II) and Fe (II) adsorption from aqueous solution using cocoa (<i>Theobroma cacao</i>) pod husk

“…Further increase in contact time did not increase the percent (%) adsorption capacity of the metal ions as seen in Figure 2. Hussain et al, (2009) reported initial rapid adsorption and attainment of equilibrium at about 50 mins for sorption of Pb (II) using non-living biomass of Spirogyra neglecta. Similar results have also been reported (Okoronkwo et al, 2008;Okoronkwo et al, 2011).…”