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International Journal of Computational Engineering Research||Vol, 03||Issue, 6||
www.ijceronline.com ||June||2013|| Page 76
Heavy Metal Biosorption Using Cheap Biomass
1,
S.V.A.R.Sastry, 2,
B.Shyam Shankar, 3,
S.V.S. Kishore
1,
Senior Asst. Professor, Department Of Chemical Engineering, M.V.G.R.College Of Engineering,
Vizianagaram
2,
Final Year Student, Department Of Chemical Engineering, M.V.G.R.College Of Engineering, Vizianagaram
I. INTRODUCTION
In recent years contamination of aquatic bodies by various pollutants has intensified the deterioration
of several ecosystems. Among these heavy metals cause severe damage to the living systems at various levels.
Exposure of the aquatic systems to heavy metal pollutants from various industrial operations like metal ore
refining, electroplating, pigments, mining, battery and accumulator manufacturing has been a serious threat to
the environment. The uptake of both metal and non-metal species by biomass is termed as biosorption. Work on
the metal binding capacity of some type of biomass and agroproducts [1-3] has gained momentum recently. A
number of agricultural waste and by-products like coffee beans, rice husk, cellulose extracted from rice husk
(RH-cellulose), cellulose and lignin extracted from coirpith, tea waste, aspergillus niger, spent-grain, litter of
natural trembling poplar (Populus tremula) forest, nutshells of walnut, hazelnut, pistachio, almond, and apricot
stone [4-10] are studied in literature for their removal capacity Cu(II) ions and other heavy metals from aqueous
solutions.
The use of coconut shell powder as an adsorbent material presents strong potential due to its high
content of lignin, around 35-45% and cellulose around 23-43%. Because of its low cost, powder of coconut
shell- Cocos nucifera is an attractive and inexpensive option for the biosorption removal of dissolved metals.
Various metal binding mechanisms are thought to be involved in the biosorption process including ionexchange,
surface adsorption, chemisorption, complexation, and adsorption complexation. [11-13]. Coconut shell powder
is composed of several constituents, among them lignin acid and cellulose bear various polar functional groups
including carboxylic and phenolic acid groups which are involved in metal binding [11, 14]. Cellulose and
lignin are biopolymers and are considered appropriate for the removal of heavy metals. In the current work,
coconut shell powder as biosorbent for Cu (II) ions from aqueous solutions was studied. The influence of
parameters like pH and particle size is presented. The Scanning Electron Microscope (SEM) analyses are used
for characterising coconut shell powder and experimental data obtained was correlated using adsorption
equilibrium isotherms and kinetic models.
II. METHODS
2.1 Biosorbent material
The powder of coconut shell powder used in the present work was prepared in our laboratory using
mechanical unit operations equipment like jaw crusher, hammer mill, rotap sieve shaker and standard sieves by
the method described by Coconut Board of India.
2.2 Biosorption Experiments
Biosorption experiments were performed batch wise at (27o
C) in Erlenmeyer flasks, stirred in
reciprocal shaker for 4 h. In all sets of experiments, accurately weighed coconut shell powder was thoroughly
mixed in to 250 ml of aqueous metal solution. At regular intervals of time (15 min), a sample of the mixture is
filtered to remove the fine particulates and the filtrate was analyzed by atomic adsorption spectrometer (AAS)
ABSTRACT
The metal taking capacity of several types of biomass, agro products and by-products has
gained attention during recent years. In the present study, one such material i.e., coconut shell powder
was chosen as the biosorbent for the removal of Cu(II) from aqueous solutions. The adsorption capacity
of this sorbent was investigated by batch experiments. High adsorption (>90 %) is achieved in the
present study.
KEYWORDS: Biosorption, Copper, Coconut shell powder
Heavy Metal Biosorption Using...
www.ijceronline.com ||June||2013|| Page 77
for the concentration of metal species. The solution of metal species was prepared dissolving CuSO4.5H2O
(analytical grade supplied by Merck) in deionised water and pH adjustments were made using HCl and NaOH
solution.
III. RESULTS AND DISCUSSIONS
3.1 Effect of pH
pH is an important parameter in determining biosorption levels. The effect of pH (in the range 5-9) on
the uptake levels of powder of coconut shell from an aqueous solution is evaluated. The effect of initial pH is
presented in Fig 1. The Cu (II) removal increased from 42 % at pH 5 to 96% at pH 9. There is no significant
increase from pH 7 onwards. Both the surface functional groups present on the coconut shell powder and metal
chemistry in solution relate to the dependence of metal uptake on pH. At low pH, the surface ligants are closely
associated with the hydronium ions (H3O+
) and restricted the approach of metal cations as a result of repulsive
force [20]. Further, the pH dependence on the metal ion uptake by coconut shell powder can be justified by
association-dissociation of certain functional groups like carboxylic and hydroxyl group present on biomass. At
low pH, most of carboxylic group are not dissociated and cannot bind the metal ions, though they take part in
complexation reactions. With these observations, further experiments are performed at pH 7 only.
3.2 Effect of particle size
Influence of the particle size of coconut shell powder used for uptake of Cu (II) was studied. The
results presented in Fig. 2 show a gradual decrease and then increase in removal of Cu(II) with decrease in
particle size. It is important to note that larger particles with spherical surfaces, present higher external mass
transfer. In this case, higher metal adsorption from these particles is attributed to mass transport inside the
sorbent particles [12]. At the same time as the particle size decreases the surface area for adsorption increases
which in turn contribute to high adsorption at fine particle size. Optimum particle size can be obtained if precise
contributions of mass transport and surface diffusion are ascertained. This has been not formed part of this work.
IV. CONCLUSIONS
Coconut shell powder was confirmed as a potential biosorbent in the removal of copper from aqueous
solutions. Investigations showed that pH and particle size influence the uptake of Cu (II). The micrographs
obtained by SEM analyzes before and after the uptake by coconut shell powder do not show any significant
difference indicating the Cu bands and absence of Cl, K bands in EDS after metal uptake indicate that a
possible ion exchange mechanism.
REFERENCES
[1] Volesky, B. (2004). Sorption and Biosorption; BV-Sorbex Inc.: Quebec, Canada.
[2] Wase, J.; Forster, C. (1997). Biosorbent for Metal Ions; Taylor & Francis Ltd.: London, U.K.
[3] Wilde, E. W.; Benemann, J. R. (1993). Bioremoval of heavy metals by the use of microalgae. Biotechnology Advances. 11 (4), 781.
[4] Amarasinghe, B. M. W. P. K.; Williams, R. A. (2007). Tea waste as a low cost adsorbent for the removal of Cu and Pb from
wastewater. Chem. Engg. J. 132 (1-3), 299.
[5] Kaikake, K.; Hoaki, K.; Sunada, H.; Dhakal, R. P.; Baba, Y. (2007). Removal characteristics of metal ions using degreased coffee
beans: Adsorption equilibrium of cadmium(II). Bioresource Technology. 98 (15), 2787.
[6] Kazemipour, M.; Ansari, M.; Tajrobehkar, S.; Majdzadeh, M.; Kermani, H. R. (2008). Removal of lead, cadmium, zinc, and copper
from industrial wastewater by carbon developed from walnut, hazelnut, almond, pistachio shell, and apricot stone. J. Hazard. Mater.
150 (2), 322 .
[7] Lu, S.; Gibb, S. W. (2008). Copper removal from wastewater using spent-grain as biosorbent, Bioresource Tech. 99 (6), 1509.
[8] Mausumi, M.; Noronha, S. B.; Suraishkumar, G. K. (2007). Kinetic modeling for the biosorption of copper by pretreated
Aspergillus niger biomass. Bioresource Tech. 98 (9), 1781.
[9] Dundar, M.; Nuhoglu, C.; Nuhoglu. Y. (2008). Biosorption of Cu(II) ions onto the litter of natural trembling poplar forest. J.
Hazard. Mater. 151 (1), 86.
[10] Nakbanpote, W.; Goodman, B. A.; Thiravetyan, P. (2007). Copper adsorption on rice husk derived materials studied by EPR and
FTIR. Colloids and Surfaces A: Physicochemical and Engineering Aspects. 304 (1-3), 7.
[11] Matheickal, J. T.; Yu, Q.; Woodburn, G. M. (1999). Biosorption of cadmium(II) from aqueous solutions by pre-treated biomass of
marine alga DurvillAea potatorum. Water Research. 33 (2), 335.
[12] Pino, G. H.; Souza de Mesquita, L. M.; Torem, M. L.; Pinto, G. A .S. (2006). Biosorption of cadmium by green coconut shell
powder. Minerals Engg. 19 (5), 380.
[13] Pino, G. H.; Souza de Mesquita, L. M.; Torem, M. L.; Pinto, G. A. S. (2006). Biosorption of heavy metals by powder of green
coconut shell. Separation Sci. & Tech. 41 (14), 3141.
[14] Ting, Y. P.; Prince, I. G.; Lawson, F. (1991). Uptake of cadmium and zinc by the alga Chlorella vulgaris: II. Multi-ion situation.
Biotech. & Bioengg. 37 (5), 445.
[15] Veglio, F.; Beolchini, F.(1999). Removal of metals by biosorption: a review. Hydrometallurgy. 1997, 44 (3), 301.
[16] Donmez, G. C.; Aksu, Z.; Ozturk, A.; Kutsal, T. A comparative study on heavy metal biosorption characteristics of some algae.
Process Biochemistry. 34 (9), 885.
Heavy Metal Biosorption Using...
www.ijceronline.com ||June||2013|| Page 78
[17] McKay, G.; Ho, Y. S.; Ng, J. C. Y. (1999). Biosorption of copper from waste waters: A review. Separation and Purification
Methods. 28 (1), 87.
[18] Aksu, Z.; Kutsal, T. (1990). A comparative study for biosorption characteristics of heavy metal ions with C. vulgaris.
Environmental Technology. 11 (10), 979.
[19] Ho, Y. S.; McKay, G. (1990). Pseudo-second order model for sorption processes. Process Biochemistry. 34 (5), 451.
[20] Aksu, Z. (2001). Equilibrium and kinetic modelling of cadmium (II) biosorption by C. vulgaris in a batch system: effect of
temperature. Separation & Purification Tech. 21 (3), 285.

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International Journal of Computational Engineering Research(IJCER)

  • 1. International Journal of Computational Engineering Research||Vol, 03||Issue, 6|| www.ijceronline.com ||June||2013|| Page 76 Heavy Metal Biosorption Using Cheap Biomass 1, S.V.A.R.Sastry, 2, B.Shyam Shankar, 3, S.V.S. Kishore 1, Senior Asst. Professor, Department Of Chemical Engineering, M.V.G.R.College Of Engineering, Vizianagaram 2, Final Year Student, Department Of Chemical Engineering, M.V.G.R.College Of Engineering, Vizianagaram I. INTRODUCTION In recent years contamination of aquatic bodies by various pollutants has intensified the deterioration of several ecosystems. Among these heavy metals cause severe damage to the living systems at various levels. Exposure of the aquatic systems to heavy metal pollutants from various industrial operations like metal ore refining, electroplating, pigments, mining, battery and accumulator manufacturing has been a serious threat to the environment. The uptake of both metal and non-metal species by biomass is termed as biosorption. Work on the metal binding capacity of some type of biomass and agroproducts [1-3] has gained momentum recently. A number of agricultural waste and by-products like coffee beans, rice husk, cellulose extracted from rice husk (RH-cellulose), cellulose and lignin extracted from coirpith, tea waste, aspergillus niger, spent-grain, litter of natural trembling poplar (Populus tremula) forest, nutshells of walnut, hazelnut, pistachio, almond, and apricot stone [4-10] are studied in literature for their removal capacity Cu(II) ions and other heavy metals from aqueous solutions. The use of coconut shell powder as an adsorbent material presents strong potential due to its high content of lignin, around 35-45% and cellulose around 23-43%. Because of its low cost, powder of coconut shell- Cocos nucifera is an attractive and inexpensive option for the biosorption removal of dissolved metals. Various metal binding mechanisms are thought to be involved in the biosorption process including ionexchange, surface adsorption, chemisorption, complexation, and adsorption complexation. [11-13]. Coconut shell powder is composed of several constituents, among them lignin acid and cellulose bear various polar functional groups including carboxylic and phenolic acid groups which are involved in metal binding [11, 14]. Cellulose and lignin are biopolymers and are considered appropriate for the removal of heavy metals. In the current work, coconut shell powder as biosorbent for Cu (II) ions from aqueous solutions was studied. The influence of parameters like pH and particle size is presented. The Scanning Electron Microscope (SEM) analyses are used for characterising coconut shell powder and experimental data obtained was correlated using adsorption equilibrium isotherms and kinetic models. II. METHODS 2.1 Biosorbent material The powder of coconut shell powder used in the present work was prepared in our laboratory using mechanical unit operations equipment like jaw crusher, hammer mill, rotap sieve shaker and standard sieves by the method described by Coconut Board of India. 2.2 Biosorption Experiments Biosorption experiments were performed batch wise at (27o C) in Erlenmeyer flasks, stirred in reciprocal shaker for 4 h. In all sets of experiments, accurately weighed coconut shell powder was thoroughly mixed in to 250 ml of aqueous metal solution. At regular intervals of time (15 min), a sample of the mixture is filtered to remove the fine particulates and the filtrate was analyzed by atomic adsorption spectrometer (AAS) ABSTRACT The metal taking capacity of several types of biomass, agro products and by-products has gained attention during recent years. In the present study, one such material i.e., coconut shell powder was chosen as the biosorbent for the removal of Cu(II) from aqueous solutions. The adsorption capacity of this sorbent was investigated by batch experiments. High adsorption (>90 %) is achieved in the present study. KEYWORDS: Biosorption, Copper, Coconut shell powder
  • 2. Heavy Metal Biosorption Using... www.ijceronline.com ||June||2013|| Page 77 for the concentration of metal species. The solution of metal species was prepared dissolving CuSO4.5H2O (analytical grade supplied by Merck) in deionised water and pH adjustments were made using HCl and NaOH solution. III. RESULTS AND DISCUSSIONS 3.1 Effect of pH pH is an important parameter in determining biosorption levels. The effect of pH (in the range 5-9) on the uptake levels of powder of coconut shell from an aqueous solution is evaluated. The effect of initial pH is presented in Fig 1. The Cu (II) removal increased from 42 % at pH 5 to 96% at pH 9. There is no significant increase from pH 7 onwards. Both the surface functional groups present on the coconut shell powder and metal chemistry in solution relate to the dependence of metal uptake on pH. At low pH, the surface ligants are closely associated with the hydronium ions (H3O+ ) and restricted the approach of metal cations as a result of repulsive force [20]. Further, the pH dependence on the metal ion uptake by coconut shell powder can be justified by association-dissociation of certain functional groups like carboxylic and hydroxyl group present on biomass. At low pH, most of carboxylic group are not dissociated and cannot bind the metal ions, though they take part in complexation reactions. With these observations, further experiments are performed at pH 7 only. 3.2 Effect of particle size Influence of the particle size of coconut shell powder used for uptake of Cu (II) was studied. The results presented in Fig. 2 show a gradual decrease and then increase in removal of Cu(II) with decrease in particle size. It is important to note that larger particles with spherical surfaces, present higher external mass transfer. In this case, higher metal adsorption from these particles is attributed to mass transport inside the sorbent particles [12]. At the same time as the particle size decreases the surface area for adsorption increases which in turn contribute to high adsorption at fine particle size. Optimum particle size can be obtained if precise contributions of mass transport and surface diffusion are ascertained. This has been not formed part of this work. IV. CONCLUSIONS Coconut shell powder was confirmed as a potential biosorbent in the removal of copper from aqueous solutions. Investigations showed that pH and particle size influence the uptake of Cu (II). The micrographs obtained by SEM analyzes before and after the uptake by coconut shell powder do not show any significant difference indicating the Cu bands and absence of Cl, K bands in EDS after metal uptake indicate that a possible ion exchange mechanism. REFERENCES [1] Volesky, B. (2004). Sorption and Biosorption; BV-Sorbex Inc.: Quebec, Canada. [2] Wase, J.; Forster, C. (1997). Biosorbent for Metal Ions; Taylor & Francis Ltd.: London, U.K. [3] Wilde, E. W.; Benemann, J. R. (1993). Bioremoval of heavy metals by the use of microalgae. Biotechnology Advances. 11 (4), 781. [4] Amarasinghe, B. M. W. P. K.; Williams, R. A. (2007). Tea waste as a low cost adsorbent for the removal of Cu and Pb from wastewater. Chem. Engg. J. 132 (1-3), 299. [5] Kaikake, K.; Hoaki, K.; Sunada, H.; Dhakal, R. P.; Baba, Y. (2007). Removal characteristics of metal ions using degreased coffee beans: Adsorption equilibrium of cadmium(II). Bioresource Technology. 98 (15), 2787. [6] Kazemipour, M.; Ansari, M.; Tajrobehkar, S.; Majdzadeh, M.; Kermani, H. R. (2008). Removal of lead, cadmium, zinc, and copper from industrial wastewater by carbon developed from walnut, hazelnut, almond, pistachio shell, and apricot stone. J. Hazard. Mater. 150 (2), 322 . [7] Lu, S.; Gibb, S. W. (2008). Copper removal from wastewater using spent-grain as biosorbent, Bioresource Tech. 99 (6), 1509. [8] Mausumi, M.; Noronha, S. B.; Suraishkumar, G. K. (2007). Kinetic modeling for the biosorption of copper by pretreated Aspergillus niger biomass. Bioresource Tech. 98 (9), 1781. [9] Dundar, M.; Nuhoglu, C.; Nuhoglu. Y. (2008). Biosorption of Cu(II) ions onto the litter of natural trembling poplar forest. J. Hazard. Mater. 151 (1), 86. [10] Nakbanpote, W.; Goodman, B. A.; Thiravetyan, P. (2007). Copper adsorption on rice husk derived materials studied by EPR and FTIR. Colloids and Surfaces A: Physicochemical and Engineering Aspects. 304 (1-3), 7. [11] Matheickal, J. T.; Yu, Q.; Woodburn, G. M. (1999). Biosorption of cadmium(II) from aqueous solutions by pre-treated biomass of marine alga DurvillAea potatorum. Water Research. 33 (2), 335. [12] Pino, G. H.; Souza de Mesquita, L. M.; Torem, M. L.; Pinto, G. A .S. (2006). Biosorption of cadmium by green coconut shell powder. Minerals Engg. 19 (5), 380. [13] Pino, G. H.; Souza de Mesquita, L. M.; Torem, M. L.; Pinto, G. A. S. (2006). Biosorption of heavy metals by powder of green coconut shell. Separation Sci. & Tech. 41 (14), 3141. [14] Ting, Y. P.; Prince, I. G.; Lawson, F. (1991). Uptake of cadmium and zinc by the alga Chlorella vulgaris: II. Multi-ion situation. Biotech. & Bioengg. 37 (5), 445. [15] Veglio, F.; Beolchini, F.(1999). Removal of metals by biosorption: a review. Hydrometallurgy. 1997, 44 (3), 301. [16] Donmez, G. C.; Aksu, Z.; Ozturk, A.; Kutsal, T. A comparative study on heavy metal biosorption characteristics of some algae. Process Biochemistry. 34 (9), 885.
  • 3. Heavy Metal Biosorption Using... www.ijceronline.com ||June||2013|| Page 78 [17] McKay, G.; Ho, Y. S.; Ng, J. C. Y. (1999). Biosorption of copper from waste waters: A review. Separation and Purification Methods. 28 (1), 87. [18] Aksu, Z.; Kutsal, T. (1990). A comparative study for biosorption characteristics of heavy metal ions with C. vulgaris. Environmental Technology. 11 (10), 979. [19] Ho, Y. S.; McKay, G. (1990). Pseudo-second order model for sorption processes. Process Biochemistry. 34 (5), 451. [20] Aksu, Z. (2001). Equilibrium and kinetic modelling of cadmium (II) biosorption by C. vulgaris in a batch system: effect of temperature. Separation & Purification Tech. 21 (3), 285.