International Journal of Polymer Science
Volume 2018 (2018), Article ID 2830286, 11 pages
https://doi.org/10.1155/2018/2830286

Research Article

Adsorption of Anionic Surfactants onto Alumina: Characteristics, Mechanisms, and Application for Heavy Metal Removal

Thi Minh Thu Nguyen,¹ Thi Phuong Thao Do,¹ Thi Sim Hoang,¹ Ngoc Viet Nguyen,² Huy Dong Pham,² Trung Dung Nguyen,³ Thi Ngoc Mai Pham,¹ Thanh Son Le,¹ and Tien Duc Pham¹

¹Faculty of Chemistry, VNU University of Science, Vietnam National University, Hanoi, 19 Le Thanh Tong, Hoan Kiem, Hanoi 10000, Vietnam
²Center of Environmental Engineering and Chemical Safety, Vietnam Institute of Industrial Chemistry, 2 Pham Ngu Lao, Hoan Kiem, Hanoi 10000, Vietnam
³Faculty of Physics and chemical Engineering, Le Quy Don Technical University, 236 Hoang Quoc Viet, Hanoi, Vietnam

Correspondence should be addressed to Thanh Son Le; sonlt@vnu.edu.vn and Tien Duc Pham; tienduchphn@gmail.com

Received 26 April 2018; Revised 22 September 2018; Accepted 10 October 2018; Published 13 December 2018

Academic Editor: De-Yi Wang

Copyright © 2018 Thi Minh Thu Nguyen et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract.

We investigated adsorption of anionic surfactants, sodium dodecyl sulfate (SDS) and sodium tetradecyl sulfate (STS), onto alumina (Al₂O₃) with large size in the present study. The effective conditions for SDS and STS adsorption onto Al₂O₃ were systematically studied. The conditions for SDS and STS adsorption onto γ-Al₂O₃ were optimized and found to be contact time 180 min, pH 4, and 1 mM NaCl. Adsorption of both SDS and STS onto large Al₂O₃ beads increased with an increase of ionic strength, demonstrating that the adsorption is controlled by electrostatic attraction between anionic sulfate groups and positively charged Al₂O₃ surface, as well as hydrophobic interactions between long alkyl chains of surfactant molecules. Nevertheless, the hydrophobic interaction in terms of STS adsorption is much higher than that of SDS adsorption. The obtained SDS and STS adsorption isotherms in different NaCl concentrations onto Al₂O₃ beads were fitted well by two-step adsorption. Adsorption mechanisms were disused in detail on the basis of adsorption isotherm, the change in surface charge, and the change in functional surface groups by Fourier-transform infrared spectroscopy (FTIR). The application of surfactant adsorption onto Al₂O₃ to remove cadmium ion (Cd²⁺) was also studied. The optimum conditions for Cd²⁺ removal using surfactant-modified alumina (SMA) are pH 6, contact time 120 min, and ionic strength 0.1 mM NaCl. Under optimum conditions, the removal efficiency of Cd²⁺ using SMA increased significantly. We demonstrate that SMA is a novel adsorbent for removal of Cd²⁺ from aqueous solution.

1. Introduction

Surfactants are widely used chemicals for cleaning. In the application of environmental remediation, the removal of both inorganic and organic contaminants from polluted soils and aquifer sediments is largely enhanced by using surfactants [1]. In this process, surfactant loss reduces the availability of the surfactants for solubilization because of adsorption to soils and sediments [2]. Soils and sediments can be regarded as the mixture of organic and inorganic materials. Metal oxide or mineral oxide is one of major inorganic components of soils and sediments. In order to consider the removal of inorganic and organic substances, therefore, the information on the adsorption behavior of surfactant onto metal oxide will form a basis of the analysis [3–5].

Many experimental studies have been reported on the adsorption of surfactant onto colloidal particles of metal oxides [2, 3, 5–9]. However, the adsorption onto small colloidal particles will induce another complicated factor because of aggregation of particles. It is preferable to study an analysis using relatively large beads that can be used to the analysis of transport phenomena and applied for solid-phase extraction technique [10]. In our previously published paper, we successfully analyzed adsorption isotherms of anionic surfactant, sodium dodecyl sulfate (SDS), onto α-Al₂O₃ with low specific area at different NaCl concentrations and pH [11]. The surfactant SDS-modified α-Al₂O₃ (SMA) is also studied to remove ammonium ion from aqueous solution [12]. Also, adsorptive removal of both organic and inorganic pollutants using SMA was carefully examined by Adak et al. [13–18], who demonstrate that SMA is a novel adsorbent. Nevertheless, this group did not study on adsorptive removal of very toxic heavy metal cadmium ion (Cd²⁺) using SMA.

It should be noted that alkyl chain of surfactant is an important factor that strongly influences adsorption behavior and structure of adsorbed layer due to the presence of hydrophobic interactions. To predict the effect of alkyl chain, the concept of hemimicelle is well-known. The concept of hemimicelle was initially proposed by Gaudin and Fuerstenau [19]. The two-step adsorption model [6, 20] proposed the hemimicelles on a linear-linear scale plot [20]. Based on the theoretical concept of the two-step model, a general adsorption isotherm equation was derived. This equation has been successfully applied to various types of surfactant adsorption isotherms and many systems related to surfactants and polymers [11, 12, 20–24]. Although the effect of alkyl chain to surfactant adsorption onto metal oxides was investigated [25, 26], the effective conditions on the adsorption of alkyl sulfate surfactants onto metal oxide have not been studied.

In this paper, we report adsorption of alkyl sulfate surfactants sodium tetradecyl sulfate (STS) and SDS onto the Al₂O₃ with a large size. The effective conditions for adsorption such as contact time, pH, and ionic strength have been experimentally studied. The two-step adsorption model is used to fit adsorption isotherms at different ionic strengths. Adsorption mechanisms are suggested based on the adsorption isotherms, surface charge change, and surface modification by Fourier-transform infrared spectroscopy (FTIR). The application of SDS and STS adsorption for cadmium ion removal is also investigated. To the best of our knowledge, this is the first systematic study of SDS and STS adsorption onto Al₂O₃ large beads modeling an adsorption isotherm by the two-step model and application for the removal of heavy metal using surfactant-modified alumina (SMA).

2. Experimental

2.1. Materials and Chemicals

Ultrapure γ-Al₂O₃ (Riedel-de Haen, Germany), with a diameter of ~50 μm, was used in the present study. The original γ-Al₂O₃ beads were treated according to our previously published paper [27]. The treated γ-Al₂O₃ was used to study adsorption of anionic surfactants.

Anionic surfactants, sodium dodecyl sulfate (SDS) and sodium tetradecyl sulfate (STS) with purity > 95% which were supplied by Sigma-Aldrich, were used without further purification. Figures 1(a) and 1(b) show the chemical structures of SDS and STS. Cationic dye methylene blue (with purity higher than 98.5%) and organic solvent chloroform CHCl₃ (HPLC grade) from Scharlau, Spain, were used to determine the concentration of SDS and STS by spectrophotometric method. Standard solution of cadmium (1000 ppm in 0.5 M HNO₃) was purchased from Merck (Germany).

(a)

(b)

Figure 1: Chemical structures of sodium dodecyl sulfate (SDS) (a) and sodium tetradecyl sulfate (STS) (b).

Other chemicals were purchased from Merck or Scharlau of analytical reagent grade. Ultrapure water system (Labconco, USA) with a resistivity of 18.2 MΩ·cm was used to produce ultrapure water in preparing all aqueous solutions.

2.2. Adsorption Study

Adsorption isotherms were obtained in a 50 mL Erlenmeyer flask with stopper at room temperature, controlled by air conditioner (22 ± 2°C), using a depletion method. For SDS and STS adsorption studies, a 0.1 g of treated γ-Al₂O₃ was mixed with 25 mL of NaCl solutions at different concentrations by a shaker. Then, SDS and STS with concentrations from 10⁻⁵ M to 10⁻² M were prepared and pH was adjusted to the original value. After different contact times, γ-Al₂O₃ was separated from the solutions. The adsorption capacity of SDS onto γ-Al₂O₃ was determined by the difference in the concentration of SDS and STS solutions before and after adsorption by spectrophotometric method using the following equation:

where is the SDS and STS adsorption capacity (mg/g), the initial SDS and STS concentration (mmol/L), the final SDS and STS concentration (mmol/L), the volume of sample (L), the molecular weight of SDS or STS, and the adsorbent mass of Al₂O₃ (g). The adsorption studies were carried out in triplicates.

The adsorption efficiency of SDS and STS was calculated by

whereis the adsorption efficiency (%) and and are the initial SDS and STS concentrations and the final SDS and STS concentrations (mmol/L), respectively.

For adsorptive removal of heavy metal ion, 0.1 g of adsorbent solution was thoroughly mixed with 25 mL aqueous solution of Cd²⁺ of 10 ppm in 50 mL Erlenmeyer flasks at 22 ± 2°C controlled by an air conditioner. The effects of pH, adsorbent dosage, contact time, and ionic strength on the removal of Cd²⁺ were investigated. All concentrations of Cd²⁺ were quantified by flame atomic absorption spectrometry (F-AAS). The removal (, %) of Cd²⁺ was calculated by

where and are initial concentration and final concentration of Cd²⁺ (ppm), respectively.

2.3. Instrumental Methods

The concentrations of both SDS and STS were determined by extractive spectrophotometric method based on the formation of ion-pair complexes between anionic surfactants and cationic dye, methylene blue in chloroform solvent. Measurements of samples and standard solutions or blanks were carried out simultaneously according to the previously published paper [11]. The absorbances of ion-pair complexes in chloroform phase were measured at a wavelength of 655 nm by an UV-Vis spectrophotometer (UV-1650PC, Shimadzu) with closed quartz cuvette with 1 cm optical path length. The relationships between the UV-Vis absorbance and concentrations of SDS and STS of standard calibration curves in different electrolyte concentrations and pH have a correlation coefficient of at least 0.999.

All concentrations of Cd²⁺ in the solution were determined by using an atomic absorption spectrometer (AA-6800, Shimadzu, Japan). A hollow cathode lamp (HCL) was used to emit a narrow wavelength of 228.8 nm. The slit width was kept as constant of 0.5 nm for all F-AAS measurements. A standard curve of Cd²⁺ by AAS with a correlation coefficient of at least 0.9995 was checked every time before determining unknown samples.

Potentiometric method using a HI 2215 Hanna Instruments pH meter with a glass combination electrode was used to monitor all pH of solutions. Three standard buffers (4.0, 7.0, and 10.0, Hanna) were used to calibrate the electrode before measuring pH of solutions. The change in surface charge of γ-Al₂O₃ beads were evaluated by monitoring pH before and after SDS and STS adsorption. A 1 mM NaCl solution was conducted with the initial pH in the range of 4-10 using 0.1 M solutions of NaOH and HCl. Then, the pH values were measured using the above pH meter. After equilibrium time of adsorption, the final pH values were determined. A graph which was plotted between the initial and final pH against the initial pH was used to evaluate the change in the surface charge [28].

To confirm surface modification of alumina after SDS and STS adsorption, Fourier-transform infrared spectroscopy (FTIR) was carried out using an Affinity-1S (Shimadzu, Japan). The change of functional groups after Cd²⁺ adsorption was also evaluated by FTIR. The FTIR spectra were obtained under at the atmospheric pressure, room temperature controlled by an air conditioner (22 ± 2°C), and a resolution of 4 cm⁻¹.

3. Modeling by General Isotherm Equation

The obtained isotherms of SDS and STS were fitted by a general isotherm equation. The general isotherm equation is as follows [20]:

where is the amount of adsorbed SDS and STS (mg/g), is the maximum adsorption amount (mg/g), and is the number of hemimicelle concentration while (g/mg) and (g/mg)n−1are equilibrium constants for the first step and second step, respectively. denotes the equilibrium concentrations of SDS and STS in solution (mmol/L).

The selected fitting parameters for surfactant adsorption were described in the previously published papers [11].

3.1. Results and Discussion

3.2. Adsorption of SDS and STS onto Alumina

3.2.1. Effect of Contact Time

Contact time influences the completeness of adsorption equilibration. The effect of contact time on the adsorption efficiency of SDS and STS onto Al₂O₃ was shown in Figure 2. Figure 2 indicates that the adsorption efficiencies of SDS and STS increased from 0 to 180 min. After 180 min, adsorption changed insignificantly. It suggests that adsorption reaches the equilibrium at 180 min for both SDS and STS. Thus, 180 min is suitable for adsorption of SDS and STS. As can be seen in Figure 2, the adsorption of STS reaches to equilibrium faster than SDS adsorption. The adsorption of SDS and STS in our case is much faster than the adsorption of alkyl sulfate surfactants onto metal oxides [11, 29, 30]. Figure 2 also shows that all error bars showing the replicates are small, indicating that the experiments have very good repeatability.

Figure 2: Effect of contact time on the adsorption efficiency of SDS and STS onto Al₂O₃. Error bars show standard deviations of three replicates.

3.2.2. Effect of pH

Solution pH plays an important role in the adsorption of anionic surfactant onto Al₂O₃ because it can influence the surface charge of Al₂O₃ while the charging behavior of SDS and STS is independent on pH. The effect of initial pH on the SDS and STS adsorption onto Al₂O₃ was investigated in the pH range of 3–10 in 1 mM NaCl (Figure 3).

Figure 3: Effect of pH on the adsorption efficiency of SDS and STS onto Al₂O₃. Error bars show standard deviations of three replicates.

Figure 3 shows that the adsorption of SDS and STS onto Al₂O₃ achieves the maximum at pH 4. The adsorption decreased with increasing solution pH from pH 4 to pH 7 for both SDS and STS due to the decrease of positive charge of Al₂O₃. These trends are similar to the adsorption of SDS onto α-Al₂O₃ with small specific area [11]. The adsorption of SDS onto α-Al₂O₃ induced proton concomitant so that the surface charge of α-Al₂O₃ grew up with an increase SDS adsorption. The change in surface charge upon SDS and STS adsorption will be discussed in Adsorption Mechanisms.

On the one hand, at pH higher than 7, adsorption increased because the charge reversal of Al₂O₃ took place and adsorption here was induced by hydrophobic interaction. The dissolution of γ-Al₂O₃ can take place at pH 3 so that adsorption of both SDS and STS is decreased. At pH 3, the error bars are highest and residual surfactants after adsorption are not stable that is strongly affected by γ-Al₂O₃ dissolution.

3.2.3. Effect of Ionic Strength

Ionic strength affects electrostatic attraction between anionic surfactants and positively charged Al₂O₃ surface. As can be seen in Figure 4, the adsorption efficiencies increase from 0 to 1 mM NaCl then they decrease from 1 to 200 mM. At very low salt concentration, adsorption of both SDS and STS is controlled by both electrostatic and hydrophobic interactions [31, 32]. However, the desorption of surfactant is enhanced with increasing salt concentration [33]. It should be noted that the concentrations of both SDS and STS equal to 10⁻⁵ M, adsorption mainly induced by electrostatic attraction so that adsorption decreases with increasing salt concentration. In order to understand adsorption behavior of sulfate surfactants and effect of alkyl chain, adsorption isotherms were taken and discussed in detail in the next section.

Figure 4: Effect of ionic strength on the adsorption efficiency of SDS and STS onto Al₂O₃. Error bars show standard deviations of three replicates.

3.2.3.1. Adsorption Isotherms of SDS and STS onto Al₂O₃. The effect of ionic strength on SDS and STS adsorption onto alumina surface is well demonstrated in the isotherms. The presented isotherms show two steps at different ionic strengths. The calculated curves by the two-step adsorption model shown as the solid lines in Figures 5 and 6 can reasonably represent experimental data by using the fit parameters (Table 1). From the fitting procedure according to our published paper [11], the values of are chosen about 3 for SDS and 3.2 for STS. Although the values of obtained from this model are much smaller than the measured aggregation number using spectroscopic methods [5, 34], the results from the two-step model are useful to evaluate the effect of ionic strength.

Figure 5: Adsorption isotherms of SDS onto γ-Al₂O₃ in different NaCl concentrations (pH 4). While the points are experimental data, the solid lines are the results of the 2-step adsorption model.

Figure 6: Adsorption isotherms of STS onto Al₂O₃ in different NaCl concentrations. While the points are experimental data, the solid lines are the results of the 2-step adsorption model.

Table 1: The fit parameters for the SDS and STS adsorption isotherms onto γ-Al₂O₃ at different NaCl concentrations (pH 4). The maximum adsorbed amount , the equilibrium constants and for the first step and second step, respectively, and the aggregation number of hemimicelle of SDS and STS molecules.

(mM)
Surfactant
(mg/g)
(g/mg)
(g/mg)⁻¹

100
SDS
230
4 × 10³
4 × 10⁵
3.0

100
STS
555
3 × 10³
4 × 10⁶
3.2

10
SDS
265
4.5 × 10³
7 × 10⁵
3.0

10
STS
355
5 × 10³
3 × 10⁶
3.3

1
SDS
330
6 × 10³
5 × 10⁵
3.0

1
STS
260
3 × 10³
4 × 10⁶
3.2

Figure 5 shows that at different salt concentrations, the adsorption density of SDS decreases with an increase of salt concentration because the electrostatic attraction between the negatively charged SDS head groups and positively charged γ-Al₂O₃ surface is decreased by increasing salt concentrations. The isotherms of SDS adsorption at lower salt are above others at high salt. For STS adsorption, this trend is appropriated at low STS concentration (Figure 6). However, at high surfactant concentration, the adsorption density of STS increases with increasing salt concentration by screening of repulsive force between negatively charged sulfate ion.

At the high ionic strength (10 and 100 mM NaCl), maximum adsorption of STS is higher than that of SDS (Table 1). Especially, maximum adsorption capacity of STS is 2.4 times greater than that of SDS. It implies that adsorption of alkyl sulfate is strongly controlled by hydrophobic interaction at high ionic strength. The results are in good agreement with previously published papers [11, 32, 35]. The reasons may be due to the significant decrease in critical micelle concentration (CMC) when increasing ionic strength. However, at low ionic strength (1 mM NaCl), adsorption of SDS is higher than that of STS. It suggests that the electrostatic attraction is stronger for SDS adsorption than for STS adsorption at low salt. When increasing salt, electrostatic attraction is reduced and hydrophobic interaction is enhanced. Another thing is that carbon chain length plays an important role in the hydrophobic force so that the adsorption increases with increase carbon chain at high ionic strength. Also, the values of seem to be a parameter to evaluate the effect of carbon chain in which is much higher for STS adsorption than for SDS adsorption. On the one hand, the values of changed insignificantly. We indicate that the adsorption of alkyl sulfate surfactants is induced by both electrostatic and hydrophobic interactions.

3.2.4. Adsorption Mechanisms

Adsorption of alkyl sulfate surfactants onto γ-Al₂O₃ is discussed in detail based on the change in surface charge, the change in functional groups by FTIR, and the adsorption isotherm.

The change in surface charge was evaluated by the difference of initial pH and final pH after SDS and STS adsorption (Figure 7).

Figure 7: The differences of pH (ΔpH) after SDS and STS adsorption as a function of initial pH.

The adsorption amounts of SDS and STS are much higher than those of the proton concomitant. Nevertheless, the proton adsorption is significant so that after SDS and STS adsorption, the differences of pH (ΔpH) are high, especially for low pH. The screening by SDS and STS molecules plays an important role in inducing the proton adsorption. The effect of alkyl chain length is clearly observed in Figure 7 in which ΔpH for STS adsorption is always higher than that for SDS adsorption. These results agreed well with the results of adsorption isotherm of SDS and STS. The influence of pH in proton concomitant is high when surfactant molecules adsorb with head groups toward the γ-Al₂O₃ surface. This trend is similar to the case of SDS adsorption onto α-Al₂O₃ with small surface area. On the other hand, the hydrophobic core is limited so that net charge at the surface site of the bilayer is very low [35]. These findings suggest that the electrostatic interaction is of great important for adsorption of SDS and STS onto γ-Al₂O₃.

The surfactant adsorption mechanism is suggested by comparing the FTIR spectrum of unmodified γ-Al₂O₃ (Figure 8) and the γ-Al₂O₃ beads after adsorption (Figures 9 and 10). Figure 8 shows that the peaks appearing at 3564.45 cm⁻¹ is assigned for –OH stretching vibration. The absorption band at 1645.28 cm⁻¹ is due to the water molecule in the sample [36]. The broaden peak between 893.04 cm⁻¹ and 522.71 cm⁻¹ confirms the bending vibration of Al-O in γ-Al₂O₃. On the other hand, Figure 9 shows that the relative intensity of asymmetrical and symmetrical stretching of –CH₂– present at 2922 and 2856 cm⁻¹ decreases dramatically in the spectra of γ-Al₂O₃ after SDS adsorption compared to SDS powder. On the other hand, Figure 10 still shows the strong peaks of stretching of –CH₂– present at 2926 and 2860 cm⁻¹ after STS adsorption onto γ-Al₂O₃. These indicate that hydrophobic interaction takes place on the surface of γ-Al₂O₃. In addition, the hydrophobic interaction in case of STS adsorption is stronger than that of SDS adsorption. In addition, the peaks of at about 1254 cm⁻¹ and 1218 cm⁻¹ occur very strongly in the spectrum of SDS and STS and while these bands do not appear in the spectra of γ-Al₂O₃ after SDS and STS adsorption (Figures 9 and 10). This suggests that SDS and STS have sulfate head groups toward the surface of γ-Al₂O₃ by electrostatic attraction. Admicelles with the bilayer containing both the first layer head-on toward γ-Al₂O₃ and second layer head-out toward solution were formed [11]. Also, admicelles are enhanced in the case of STS than SDS. The results are also in good agreement with adsorption isotherm shown in the above section. The results of FTIR spectra of γ-Al₂O₃ after SDS and STS adsorption combined with the adsorption isotherm suggest that SDS and STS molecules mainly adsorb on the surface of γ-Al₂O₃ by both electrostatic attraction as well as probably by hydrophobic interaction. The hydrophobic interaction in the case of STS is much stronger than that of SDS, demonstrating that the effect of hydrocarbon alkyl chain length is of great importance for alkyl sulfate surfactant adsorption.

Figure 8: The FTIR spectra in the wavenumber range of 400–4000 cm⁻¹ of unmodified γ-Al₂O₃.

Figure 9: FTIR spectrum of γ-Al₂O₃ after SDS adsorption in the wavenumber range of 400–4000 cm⁻¹.

Figure 10: FTIR spectrum of γ-Al₂O₃ after STS adsorption in the wavenumber range of 400–4000 cm⁻¹.

3.3. Adsorptive Removal of Cadmium Using Surfactant-Modified Alumina (SMA)

3.3.1. Influence of pH

The pH of the solution is one of the most important factors that strongly affect the removal of Cd²⁺. The pH can affect the charging behavior of adsorbents and the species of Cd²⁺ in aqueous solution. In order to evaluate the role of surfactant modification, we compare three adsorbents. γ-Al₂O₃ denotes without surfactant while γ-Al₂O₃ materials after STS preadsorption and SDS preadsorption are called with STS modification and with SDS modification, respectively. The effect of initial pH on removal of Cd²⁺ using three adsorbents in the range of pH 3–7 in 1 mM NaCl is indicated in Figure 11.

Figure 11: Influence of pH on removal of Cd²⁺ using different Al₂O₃ adsorbents (without surfactant, with STS modification, and with SDS modification) at 1 mM NaCl. Error bars show standard deviations of three replicates.

As can be seen in Figure 11, the removal of Cd²⁺ using three adsorbents (without surfactant, with STS modification, and with SDS modification) increases with increasing pH from pH 3 to 6. The removal of Cd²⁺ with surfactant modification is always higher than in the case without surfactant, demonstrating that surfactant-modified γ-Al₂O₃ is a better adsorbent compared with γ-Al₂O₃ without surfactant. At the optimum pH, the removal of Cd²⁺ increases from 62.7% (without surfactant) to about 94.6% (with SDS modification). In addition, the differences between STS modification and SDS modification are insignificant. Since SDS is a more common chemical compared with STS, SDS-modified γ-Al₂O₃ (SMA) is chosen for further study in the removal of Cd²⁺ from aqueous solution. The optimum pH for the removal of Cd²⁺ by SMA is pH 6.

3.3.2. Influence of Contact Time

Figure 12 shows that the removal of Cd²⁺ using SMA is rapidly increased. The removal increases with increasing contact time from 5 min to 120 min. After 120 min, the removal of Cd²⁺ changes very little. It indicates that the adsorption of Cd²⁺ using SMA reaches equilibrium at 120 min. Thus, 120 min is chosen for removal of Cd²⁺ using SMA.

Figure 12: Influence of contact time on removal of Cd²⁺ using surfactant-modified γ-Al₂O₃ (SMA) (Ci (Cd²⁺) = 10 ppm, pH 6, 1 mM NaCl). Error bars show standard deviations of three replicates.

3.3.3. Influence of Ionic Strength

Ionic strength affects the electrostatic attraction between Cd²⁺ onto SMA and the SDS remaining on the γ-Al₂O₃ surface. Figure 13 shows that the removal efficiency decreases with increasing NaCl concentration, except for salt free (0 mM NaCl). Without salt, the electrostatic interaction is smaller than that with salt. Nevertheless, an increase of NaCl concentration induced the presence of Cl⁻ ion. When increasing salt, the concentration of Cl⁻ is high so that the removal is decreased. This result can be also explained by desorption of SDS at high salt concentration [33]. An increase of NaCl concentration decreases the attraction of DS⁻ with Cd²⁺ so that error bars of replicated experiments seem to be larger at high salt concentration.

Figure 13: Influence of NaCl concentration on removal of Cd²⁺ using surfactant-modified γ-Al₂O₃ (SMA) (Ci (Cd²⁺) = 10 ppm, pH 6, contact time 120 min). Error bars show standard deviations of three replicates.

3.3.4. Surface Modification of SMA after Cadmium Adsorption

Adsorption of Cd²⁺ onto SMA induced the charge of functional groups of SMA. Figure 14 shows the FTIR of SMA after Cd²⁺ adsorption. The FTIR spectra of SDS-modified γ-Al₂O₃ after adsorption of Cd²⁺ (Figure 14) indicates that the specific peaks assigned for the vibration of CH₂– in the wavenumber range of 2500 cm⁻¹-3500 cm⁻¹ still occurred but the intensity is much smaller compared with that of SMA [37]. It implies that after adsorption of cationic Cd²⁺, the small number of SDS admicelles SDS remained γ-Al₂O₃. In other words, the adsorption of Cd²⁺ induced the less negatively SMA surface.

Figure 14: The FTIR spectra in the wavenumber range of 400–4000 cm⁻¹ for SDS-modified γ-Al₂O₃ after adsorption of cadmium.

3.3.5. Comparison of the Effectiveness of SMA and Other Adsorbents

Many researchers investigated the removal of Cd²⁺ using different kinds of adsorbents. Nevertheless, adsorptive removal of Cd²⁺ using surfactant-modified alumina (SMA) has not been studied. Furthermore, the SMA which is used in the present study, achieved the highest removal efficiency compared to adsorbents (Table 2). Also, the adsorption capacity of Cd²⁺ on SMA is quite high when comparing with other adsorbents. This demonstrates that SMA is a novel adsorbent for the removal of Cd²⁺ from aqueous solutions.

Table 2: Adsorption capacity and removal efficiency of Cd²⁺ using surfactant-modified alumina (SMA) and other absorbents.

Adsorbent
Adsorption capacity (mg/g)
Removal efficiency (%)
References

Kaolinite clay
15.60
87.50
[38]

Multi-carboxyl-functionalized silica gel
40.48
89.44
[39]

Activated sludge
18.0
74.5
[40]

Waste sludge
15.73
90.0
[41]

Zeolite-based geopolymer
20.58
92.28
[42]

Activated alumina
35.06
93.50
[43]

SMA
24.40
94.60
This study

4. Conclusions

We have studied the adsorption of alkyl sulfate surfactants, sodium dodecyl sulfate (SDS) and sodium tetradecyl sulfate (STS), onto large γ-Al₂O₃ beads and application for removal of heavy metal ion (Cd²⁺) using surfactant-modified γ-Al₂O₃ (SMA). The effective adsorption conditions of SDS and STS adsorption onto γ-Al₂O₃ were found as contact time 180 min, pH 4, and 1 mM NaCl. Adsorption isotherms of both SDS and STS onto γ-Al₂O₃ were fitted well by the two-step adsorption model. The adsorption of alkyl sulfate surfactants onto γ-Al₂O₃ was induced by electrostatic and hydrophobic interactions. However, the hydrophobic interaction is much stronger for STS adsorption than for SDS adsorption. For SDS adsorption, the electrostatic attraction is more important than hydrophobic interaction. The adsorption mechanisms were confirmed by analyzing adsorption isotherm, the change in surface charge, and surface modification by FTIR. Adsorptive removal of Cd²⁺ from aqueous solution using SMA was investigated. The optimum conditions for Cd²⁺ removal using SMA were found to be pH 6, contact time 120 min, and ionic strength 0.1 mM NaCl. The removal of Cd²⁺ increased from 62.7% (without surfactant) to about 94.6% after modification with SDS. We demonstrate that SMA is a novel adsorbent compared with other adsorbents for removal of Cd²⁺ from aqueous solution.

Data Availability

(1) The data is all carried out mainly at our laboratories at the Faculty of Chemistry, VNU University of Science, Vietnam National University, Hanoi, 19 Le Thanh Tong, Hoan Kiem, Hanoi 10000, Vietnam, partly at the Center of Environmental Engineering and Chemical Safety, Vietnam Institute of Industrial Chemistry, 2 Pham Ngu Lao, Hoan Kiem, Hanoi 10000, Vietnam, and Faculty of Physics and Chemical Engineering, Le Quy Don Technical University, 236 Hoang Quoc Viet, Hanoi, Vietnam. (2) The data in the article can be accessed at the Faculty of Chemistry, VNU University of Science, Vietnam National University, Hanoi, 19 Le Thanh Tong, Hoan Kiem, Hanoi 10,000, Vietnam; Center of Environmental Engineering and Chemical Safety, Vietnam Institute of Industrial Chemistry, 2 Pham Ngu Lao, Hoan Kiem, Hanoi 10,000, Vietnam; and Faculty of Physics and Chemical Engineering, Le Quy Don Technical University, 236 Hoang Quoc Viet, Hanoi, Vietnam.

Conflicts of Interest

The authors declare that they have no competing interests.

Supplementary Materials

S1: Fourier-transform infrared spectroscopy (FTIR) of unmodified alumina shows that the peaks appearing at 3664.45 cm⁻¹ is assigned for –OH stretching vibration. The absorption band at 1645.28 cm⁻¹ is due to the water molecule in the sample [1]. The broaden peak between 893.04 cm⁻¹ and 522.71 cm⁻¹ confirms the bending vibration of Al-O in γ-Al₂O₃. S2: Fourier-transform infrared spectroscopy (FTIR) of SDS-modified γ-Al2O3 after adsorption of cadmium indicates that the specific peaks assigned for the vibration of CH2– in the wavenumber range of 2500 cm⁻¹-3500 cm⁻¹ still occurred but the intensity is much smaller compared with that of SMA [2]. It implies that after adsorption of cationic Cd2⁺, the small number of SDS admicelles SDS remained γ-Al₂O₃. In other words, the adsorption of Cd2⁺ induced the less negatively SMA surface. (Supplementary Materials)

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