Removal of lead (II) ions from synthetic and real effluents using immobilized Pinus sylvestris sawdust: Adsorption on a fixed-bed column
Introduction
The removal of toxic heavy metal contaminants from aqueous waste streams is currently one of the most important environmental issues being researched. Although this issue has been studied for many years, effective treatment options are still limited. Chemical precipitation, ion exchange, reverse osmosis and solvent extraction are the methods most commonly used for removing heavy metals ions from dilute aqueous streams [1]. Studies carried out to look for new and innovative treatment technologies have focused attention on the metal binding qualities of various types of biomass [2], [3]. It was shown that some microorganisms and biomass are able to adsorb toxic and heavy metals from dilute aqueous solutions. The factors affecting the metal binding qualities of these biomaterials or their affinity for a metal dissolved in aqueous media include: (i) the chemical nature of the metal ions (e.g. size, valence, electron orbital structure, stability of the chemical forms in nature) and that of the biomass (e.g. charge density and structure of the polymer chain, functional groups), (ii) medium conditions (e.g., pH, temperature, ionic strength, presence of competing organic or inorganic metal chelators). Biosorptive processes are generally rapid and theoretically suitable for extracting metal ions from large volumes of water [4].
Results obtained in previous studies carried out on a batch reactor showed that the removal of lead and cadmium through their binding onto Pinus sylvestris sawdust is possible. The latter biomaterial contains various organic compounds such as lignin (with polyphenolic groups), cellulose (with numerous hydroxyl functions) and hemicelluloses (with carboxylic and hydroxyl groups). These functional groups may be useful for binding ions of heavy metals [5]. Although various types of reactors, e.g. batch, continuously stirred tank reactors and fluidized-bed columns can be used, adsorption on packed-bed columns presents numerous advantages. It is simple to operate, gives high yields and can be easily scaled up from a laboratory process.
The purpose of this study was to investigate the influences of bed depth, linear flow rate and concentrations of feed metal ions on the performance of lead (II) adsorption onto P. sylvestris sawdust immobilized in a packed-bed column. This work was firstly carried out on a mini-column and the results were then checked on a pilot scale unit.
Section snippets
Methods
In this work, studies were starting from the mass balance of the packed-bed reactor. The variation of this balance during the reaction can be illustrated by Fig. 1, where u is the linear flow rate, which is the average rate of the liquid flow when the column is empty. The equation of mass balance material is: input flow = output flow + flow inside pores volume + matter adsorbed onto sawdust. For this system, the balance can be expressed according to the following equationwhere Qv is
Mini-column scale
The results of lead (II) adsorption onto P. sylvestris sawdust are presented in the form of breakthrough curves where the concentration ratio Ct/C0 is plotted versus time. Several parameters were studied.
Conclusion
Adsorption of lead (II) ions through sawdust in a packed bed column is an economically feasible technique for removing metal ions from a solution. The process allows treatment of a given volume of effluent by using a minimal mass of adsorbent which concentrates maximal content of metal.
The adsorption breakthrough curves obtained at different flow rates indicate that an increase in flow rate decreases the volume treated until the breakthrough point and therefore decreases the service time of the
Acknowledgements
The authors would like to thank the Agence Nationale pour la Valorisation de la Recherche (ANVAR) for their financial support. We are also sincerely grateful to Dr. Monin (Génie Analytique/Cnam Laboratory) for conducting the absorption atomic analysis. Our thanks also go to G. Le Buzit (Laboratoire des Sciences Nucléaires/Cnam Laboratory) for the design of the mini-column laboratory.
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