Potentially toxic trace elements, such as zinc, with high levels in water are very serious problems in many places around the world, sometimes in relation to natural sources and in other cases to anthropogenic ones. Adsorption process is among the most effective techniques for removing of many heavy metal ions from different types of water. In this study, an attempt has been made to investigate the efficiency of Calotropis procera roots (CP) in removing of Zn(II) from aqueous solution by using batch mode technique. During the removal process, the effects of solution pH, Zn concentrations and contact time on adsorption efficiency by CP roots were studied. Experimental equilibrium data were analyzed by the Langmuir and Freundlich isotherm models. The results showed that the best fit was achieved with the Langmuir isotherm equation with maximum adsorption capacity of 9.69 mg/g. The biosorption of Zn(II) was a fast process and followed the pseudo-second-order kinetic.
Global developments directed towards making human life increasing comfortable have greatly increased industrialization and urbanization. However, this trend has damaged the environment alarmingly, mainly due to the generation of a large amount of hazardous waste and the pollution of usable surface water. The major pollutants in wastewater are heavy metals such as lead, zinc, copper, cadmium, mercury, chromium and arsenic. These metals accumulate in living tissues/organs and can cause accumulative poisoning and serious health problems such as cancer and brain damage [
There are numerous methods which are currently employed to remove these metals from aqueous environment. Some of these methods are chemical precipitation and sludge separation, chemical oxidation or reduction, ion exchange, reverse osmosis, membrane separation, electrochemical treatment and evaporation. Biosorption as a wastewater bioremediation process has been found to be an economically feasible alternative for metal removal. This method offers the advantages of low operating cost, minimizing secondary pollution and high efficiency in wastes [
The aim of the present work was to study the effect of some environmental parameters such as solution pH, initial Zn(II) concentration and contact time on the ability of Calotropis procera roots to biosorb Zn(II) ions from aqueous solutions.. Calotropis procera (Asclepiadaceae), commonly known as swallow wart, Sodom apple or milk weed, is a glabrous or hairy laticiferous shrub or small tree, found in tropical and subtropical Asia and Africa [
The roots of Calotropis procera studied in this paper were taken from the local shrub roots in Oued Ksiksous in province Bechar (South West of Algeria). These roots were washed with deionized water to remove any dirt. They were dried in an oven at 60˚C for two days. The dried roots were ground and sieved through a sieve of 100 µm and then stored in a container. The sample of roots powder was characterized by using infrared (FT-IR) and scanning electron microscopic (SEM) techniques.
All chemicals used were of analytical grade. Stock standard solution of Zn2+ has been prepared by dissolving the appropriate amount of ZnSO4 in deionized water. This stock solution was then diluted to specified concentrations. The pH of the system was adjusted using reagent grade NaOH and HCl respectively. All plastic sample bottles and glassware were cleaned, then rinsed with deionized water and dried at 60˚C in a temperature controlled oven.
The pH of all solution was measured by a TitraLab Instrument TIM800 Model pH meter. The adsorption experiments have been studied by batch technique using a thermostated shaker bath GFL-1083 Model. An Eppendorf 5702 Model digital centrifuge was used to centrifuge the samples. Zn(II) concentrations of solutions before and after adsorption were measured by using flame atomic absorption spectrophometer (Varian, SpectrAA-100, AAS).
The Fourier transform infrared (FT-IR) absorption spectra was recorded on KBr pressed pellets of the powdered sample in the range 4000 - 400 cm−1, using a Perkine-Elmer FTIR 2000 spectrophotometer.
Nanomorphology was characterized by scanning electron microscopy (SEM) which was carried out using Hitachi S-4800 equipped with energy dispersive spectrometry for chemical analysis (EDS) and operating at 15 kV acceleration voltage.
Adsorption measurements were determined by batch experiments. The effect of contact time on the biosorption capacity of Calotropis procera roots was studied in the range 1 - 360 min at an initial concentration of 100 mg/L. Adsorption kinetics was studied using an initial concentration of 100 mg/L with the adsorbent dosage of 0.1 g/10mL at pH 6.5. Adsorption isotherms were studied at various initial concentrations of Zn(II) ion in the range of 10 - 120 mg/L and the experiments were conducted at different constant temperatures in the range of 25˚C - 60˚C. The amount of Zn(II) adsorbed per unit mass of Calotropis procera roots was calculated by using the mass balance equation given in Equation (1) [
where qe is the maximum adsorption capacity in mg/g, C0 is the initial concentration and Ce is the concentration at equilibrium of Zn(II) solution in mg/L, V is the volume of the Zn(II) solution in mL and m is the mass of CP roots in grams.
The sorption capacity at time t, qt (mg/g) was obtained as Equation (2) [
where C0 and Ct (mg/L) are the liquid phase concentrations of Zn(II) at initial and a given time t, V is the solution volume and m the mass of CP roots (g).
Observation under a scanning electron microscope (SEM) in
The FTIR Spectra of Calotropis procera roots, in the range of 400 - 4000 cm−1 was taken to confirm the presence of functional groups that might be responsible for the biosorption process. Peaks appearing in the spectrum (
The displacements of the corresponding bands −OH, −NH and carboxyl groups indicate the involvement of these groups in the biosorption of heavy metals by the roots of Calotropis procera.
The metal distribution between the biomass and the aqueous solution at equilibrium is of importance in determining the maximum biosorption capacity of the biomass for Zn(II) ions. The effect of initial metal concentration on the biosorption capacity was investigated at pH 6.5. In
pH is an important parameter influencing heavy metal adsorption from aqueous solutions. It affects both the surface charge of adsorbent and the degree of ionization of the heavy metal in solution. The pH range of 1.5 - 6.5 was chosen, as the precipitation of Zn(II) is found to occur at pH ≥ 7 [
The biosorption of Zn(II) on CP roots as a function of contact time at pH 6.5 is shown in
Attainment of equilibrium is influenced by several factors including the nature of the adsorbent and the adsorbate, and the interactions between them. The kinetics of the interactions is thus likely to be dependent on different rate processes as the interaction time increases [
On the basis of this result, it can be observed that CP roots can be used to remove this metal ion.
Many models were used to describe the adsorption processes. The most appreciated was Pseudo second-order (Equation (3)) [
where qt (mg/g) is the amount of Zn(II) adsorbed at time t (min), qe (mg/g) is the equilibrium adsorption capacity and K2 (g/(mg・min)) is the pseudo-second-order rate constant of adsorption. The values of K2 and qe calculated from the intercept and slope of equation are 0.28 g/(mg・min) and 4.80 mg/g, respectively.
Several adsorption isotherm models have been employed to interpret the adsorption behaviors of heavy metals on solid adsorbents. In this study, the data collected have been fitted to the Langmuir isotherm [
Freundlich isotherm [
Langmuir equation
Freundlich equation
In these equations, Ce is the concentration of Zn(II) in solution (mg/L) at equilibrium, qe is the amount of the adsorbed metal ions (mg/g) at the solid/liquid interface, qmax is the monolayer capacity of the adsorbent (mg/g), KL is the Langmuir adsorption constant (L/mg), Kf and 1/n are empirical parameters, Kf is the adsorption constant related to the bonding energy and 1/n is associated to the surface heterogeneity.
The sorption isotherms of metal ions on CP roots were fitted by two models, as shown in
Biosorption technology, utilizing natural materials for effectively removing metals from aqueous media, offers an efficient alternative compared to traditional chemical and physical treatments. The goal of this work was to explore the potential use of Calotropis procera roots as a low-cost sorbent for removing Zn(II) ions from
Langmuir | Freundlich | ||||
---|---|---|---|---|---|
qm(mg/g) | KL (L/g) | R2 | n | Kf | R2 |
9.69 | 0.024 | 0.991 | 2.46 | 0.88 | 0.962 |
aqueous solutions by batch design. The adsorption was found to be drastically depending on initial metal ion concentration, contact time and pH solution. The results gained from this study were well described by Langmuir model with monolayer capacity qm = 9.69 mg/g. Calotropis procera roots had a high adsorption capacity when compared with some other adsorbents reported in literature. This adsorption can be a good choice for removal of not only Zn(II) ions but also other heavy metal ions from waste water stream.
BahiaMeroufel,Mohamed AmineZenasni,AndréMerlin,BéatriceGeorge, (2015) Biosorptive Removal of Zinc from Aqueous Solution by Algerian Calotropis procera Roots. Journal of Environmental Protection,06,735-743. doi: 10.4236/jep.2015.67067