Copper, zinc, cadmium and lead biosorption by Gymnogongrus torulosus. Thermodynamics and kinetics studies
Introduction
The increasing concentration of heavy metals in waters is mainly due to effluent discharges from industries. Pollution of natural waters by metal ions has become a major issue all over the world because metal concentrations in waters often exceed the admissible values. Consequently, industries are required to diminish the contents of heavy metals in their effluents to acceptable levels.
The increasing waste products are forcing scientist to study new and alternative technologies to remove trace metals from polluted waters [1] and one of the main goals regarding heavy metals removal from waste waters consists in the reduction of these pollutants at very low levels [2]
Biosorption, known as the sorption of heavy metals onto biological materials, is becoming a potential alternative for toxic metals removal from waters [3], [4] and is a cost effective technology that uses readily available biomass from nature [5]. Among many biosorbents, marine seaweeds are excellent biosorbents for metals [6]. In recent years, the metal biosorption potential of various red, green and brown seaweeds were investigated by many researchers [7], [8], [9], [10], [11], [12], [13], and references therein.
Seaweeds have a high bonding affinity with heavy metals [1], [14], [15], [16], [17], [18], [19], [20]. Since their cell walls have different functional groups (such as carboxyl, hydroxyl, phosphate or amine) that can bind to metal ions [21], they are much more efficient than active carbon and natural zeolites and, depending on the pH, these groups are either protonated or deprotonated [22], [23].
Many works describing metals biosorption have been published [8], [24], [25], [26], [27], [28], [29], [30]. The advantages of using dried aquatic algae for metal removal derive from its high efficiency as biosorbents, easy handling, no nutrient requirements, low costs, and their availability.
Gymnogongrus torulosus (Rhodophyta) is a seaweed with great commercial interest in Argentina because it produces carrageenan, a polysaccharide commonly used in hydrocolloid industries. This seaweed predominates along the coastal and continental shelf areas of temperate and cold-water regions. Thus, the present study was focused on heavy metal removal from aqueous solution by G. torulosus under different experimental conditions in order to optimize the efficiency of the adsorption process. Equilibrium isotherm and kinetic models were carried out for a better understanding of the adsorption process.
Section snippets
Biosorbent material
G. torulosus were collected in Cabo Corrientes at Mar del Plata City, Buenos Aires Province, Argentina. The seaweed was washed thoroughly with deionized water, then dried overnight at 60 °C and finally stored in desiccators before being used. Afterwards, the dried seaweed was blended in a homogenizer into finer particles. A stainless steel standard sieve was used to obtain fine particles (0.5–2 mm) of seaweed, which were subsequently used for biosorption experiments.
The specific surface area was
Biosorption kinetics
Equilibrium analysis is fundamental in order to evaluate the affinity or capacity of a sorbent. However, it is important to assess how sorption rates vary with aqueous free metal concentrations, and how rates are affected by sorption capacity or by the sorbent character in terms of kinetics [34]. Fig. 1 shows the four metal uptakes by G. torulosus versus time at pH 5.5 and room temperature. The initial metal concentrations were 0.99; 0.83, 0.360 and 0.350 mM of Zn(II), Cu(II), Cd(II) and Pb(II),
Conclusions
Experimental evidence suggests that the biomass of G. torulosus could be used as an efficient biosorbent for the removal of Zn(II), Cu(II), Pb(II) and Cd(II) ions. The initial pH significantly influenced metal uptake. Biosorption kinetics follows a pseudo-second-order model. Experimental data were analyzed using Langmuir, Freundlich, Dubinin–Radushkevich and Temkin isotherm models and it was found that the Langmuir model presented a better fit. SEM–EDS confirmed the presence of Zn(II), Cu(II),
Acknowledgements
The authors acknowledge Universidad de Buenos Aires, for financial support through Project UBACyT X043, Secretaria de Ciencia y Técnica, Agencia Nacional de Promoción Científica y Tecnológica, SECyT- ANPCyT- FONCyT through PICT 32678 and Consejo Nacional de Investigaciones Científicas y Técnicas de la República Argentina (CONICET). Authors are also grateful to Dr. Marina Ciancia and Dr. José Estevez for providing the seaweed used for this research.
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