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Synthesis of MCM-41/ZIF-67 Composite for Enhanced Adsorptive Removal of Methyl Orange in Aqueous Solution

By Ratna Ediati, Pramita Elfianuar, Eko Santoso, Dety Oktavia Sulistiono and Muhammad Nadjib

Submitted: June 23rd 2018Reviewed: January 24th 2019Published: May 29th 2019

DOI: 10.5772/intechopen.84691

Downloaded: 171


ZIF-67 and MCM-41/ZIF-67 composites were successfully synthesized with water solvent at room temperature. The amounts of MCM-41 added during synthesis were varied at 2.5, 5 and 10 (%w/w) toward the amount of ZIF-67, and the obtained solids were denoted as MC (2.5)/ZIF-67, MC (5)/ZIF-67, and MC (10)/ZIF-67, respectively. The X-ray diffraction (XRD) patterns of ZIF-67 and the composites showed characteristic peaks at 2θ of 7.32, 10.36, 12.69, 14.66, and 16.40°, similar to that of reported ZIF-67. The Fourier transform infra-red (FT-IR) spectra of all solids showed absorption bands at the same wavenumbers as reported for ZIF-67. The results of surface morphology analysis using scanning electron microscope (SEM) have shown that ZIF-67 and the composites have a cube shape, which is characteristic for the ZIF-67 standard. N2 adsorption-desorption data showed that the specific surface area of ZIF-67 and MC (5)/ZIF-67 were 1079.2 and 1011.2 m2/g, respectively, lower than that of MC (10)/ZIF-67 (1250.6 m2/g). However, results of thermal gravimetric analysis (TGA) showed that the thermal stability of MC (10)/ZIF-67 reached 357°C, higher than that of ZIF-67 (325°C). Performance of the composites as adsorbent of methyl orange (MO) in aqueous solution showed that the MC (5)/ZIF-67 had the highest adsorption capacity of 167.635 mg/g, and followed the pseudosecond-order adsorption kinetics and Langmuir isothermal adsorption.


  • ZIF-67
  • composite
  • MCM-41/ZIF-67
  • adsorption
  • methyl orange

1. Introduction

Organic dyes are pollutants that can provide toxic effects on microbial populations and can be toxic or carcinogenic to organisms and mammals [1]. Azo dyes are a group of synthetic organic dyes, which are most widely used in the textile, cosmetics, and food coloring industries, so they are found in industrial waste water. The release of waste water containing dyes, with different chemical compositions and toxicity, into waterways can cause environmental damage [2]. Methyl orange (MO) is one of the cationic dyes, which are widely used in the coloring industry. If the MO concentration in wastewater reaches 500 ppm, it can cause serious health problems, such as tachycardia, vomiting, cyanosis, jaundice, quadriplegia, and tissue necrosis. Therefore, removing MO in wastewater is needed to avoid the negative effects that arise [3, 4, 5].

Several methods have been reported to remove organic dyes in water, such as adsorption with solid materials [6], chemical and biological degradation [7, 8], electrochemical degradation [9], and ozonation [10]. Adsorption, however, is considered as a simple and effective method. The adsorbents used, such as activated carbon, agricultural waste, and chitosan [11], have shown low adsorption capacity and selectivity [12].

Metal organic frameworks (MOF) are a new class of nanoporous crystalline materials consisting of metal ions or clusters that are interconnected with organic ligands and described as materials with microstructure (pore size < 2 nm), adjustable pore size, high surface area (up to 5900 m2/g), and high pore volume (up to 2 cm3/g) [13, 14, 15]. With the advantages, MOF has been considered as a potential material for various applications, including gas storage, separation, adsorption, drug delivery, and catalysts [15]. As an adsorbent, MOF has been widely used to remove toxic metals and organic pollutants from aqueous solutions [16].

Zeolitic imidazolate frameworks (ZIF) are parts of MOF, composed of tetrahedral metal ions such as Zn2+ or Co2+, which are bridged by imidazolate ligands [17, 18]. ZIF-67 (Co(Hmim)2), with a sodalite (SOD) topology [18], has been evaluated for its performance as an adsorbent in an aqueous environment and shows a high adsorption capacity against several pollutants including azo dyes [12, 19]. In the adsorption process, the pore size of adsorbent is very influential. MOF with pore size of less than 2 nm (microporous) may cause diffusion problems toward large molecules. Mesoporous silica such as MCM-41, MCM-48, and SBA-15 have been reported as supports in MOF synthesis, as an effort to increase pore size of MOF and to reduce diffusion problems when used as adsorbents. Furthermore, mesoporous silica also has high thermal stability, surface area, and porosity [20, 21].

Based on the description above, in this study, removal of MO in aqueous solution was carried out using ZIF-67 and MCM-41/ZIF-67 composites. ZIF-67 and the composites were synthesized following the method reported by Gross et al. with a slight modification [22]. The experiments were carried out at room temperature with CoCl2·6H2O as a metal source and 2-methylimidazole as a ligand in aqueous solution. A certain amount of MCM-41 was added directly into the reaction mixture.

2. Experimental

2.1 Materials

Materials used in this study were cobalt chlorida hexahydrate (CoCl2.6H2O, Sigma Aldrich, 99%), 2-methylimidazole (C4H6N2, Sigma Aldrich, 99%), deionized water, triethylamine (TEA), methanol (MeOH, Merck 99.8%), and methyl orange (Sigma Aldrich, 85%). Mesoporous silica (MCM-41) was synthesized using a procedure reported by Badamali et al. [23].

2.2 Synthesis of ZIF-67 and composite MCM-41/ZIF-67

ZIF-67 and MCM-41/ZIF-67 composites were synthesized with a molar ratio of metal:ligand of 1:11.6. The synthesis of ZIF-67 was begun by dissolving 6.09 g of 2-methylimidazole (MeIM) in 13.5 mL deionized water. Triethylamine (TEA) added was 0.5 mL and the amount of MCM-41 added was varied at 2.5, 5 and 10 w/w% toward the amount of the obtained ZIF-67. Then, CoCl2·6H2O solution was made by dissolving 1.52 g of CoCl2·6H2O in 10 mL deionized water. CoCl2·6H2O solution was mixed with 2-methylimidazole solution in a vial bottle and stirred for 20 min. Furthermore, the reaction mixture was centrifuged at 3000 rpm for 30 min. The obtained solids were washed with deionized water, followed by washing with methanol. Finally, the solids were dried in an oven at a temperature of 120°C for 16 hours.

2.3 Characterization ZIF-67 and MCM-41/ZIF-67 composites

The crystallinity of ZIF-67 and MCM-41/ZIF-67 composites were determined by XRD with CuKα radiation (λ = 1.5406 Å), with 40 kV accelerated voltage, and a current of 30 mA. The 2θ angle was recorded from 3 until 50°. Analysis of the existence of functional groups on ZIF-67 and MCM-41/ZIF-67 composites was carried out by FTIR spectrophotometer at wavenumbers of 4000–400 cm−1. Analysis by scanning electron microscope (SEM) has been done to determine the surface morphology of synthesized material. TEM images were obtained using a JEOL JEM1400 transmission electron microscope at an accelerating voltage of 200 kV. Measurement of surface area and pore size distribution of the materials were carried out using surface area analyzer based on adsorption-desorption isotherm using nitrogen gas, and the samples were degassed at 150°C for 5 hours (3 × 10−3 Torr) before being analyzed. Thermogravimetric analysis (TGA) has been used to determine the thermal stability, and the samples were heated from temperature of 35–700°C with an air gas flow.

2.4 Adsorption experiment

Methyl orange (MO) adsorption test on the effect of contact time was carried out using 10 mg of adsorbent in 100 mg/L of MO solution. The mixture was stirred at 300 rpm for 5 until 40 min. In addition, the adsorption test was also carried out on the effect of the initial concentration and concentration of MO was varied from 50 to 330 mg/L. After adsorption process, the solution was centrifuged at a rate of 3500 rpm for 10 min to separate the adsorbent from the solution. Concentration of MO was measured using a UV-Vis spectrophotometer at the maximum wavelength. Adsorption capacities of adsorbent and %removal of MO were calculated using the formula:


where Co and Ce are initial and equilibrium concentrations of MO in mg/L, W is the mass of adsorbent in g, and V is the volume of solution in mL.

3. Result and discussion

3.1 Characterization of materials

The effect of the addition of MCM-41 on characteristic of the obtained MCM-41/ZIF-67 composites has been determined from the results of characterization using XRD, FTIR, SEM-EDX, nitrogen adsorption-desorption, and TGA. The XRD patterns of ZIF-67 and MCM-41/ZIF-67 composites are shown in Figure 1. As can be seen, the characteristic peaks appear at 2θ of 7.32, 10.36, 12.69, 14.66, and 16.40°, respectively, which are in accordance with the results of previous studies [22]. Likewise, the XRD patterns of the MCM-41/ZIF-67 composites have shown the same pattern as pure ZIF-67. The addition of MCM-41 during the ZIF-67 synthesis, however, has resulted in a reduction in crystallinity of the obtained composites, which may be attributed to amorphous properties of mesoporous silica [24].

Figure 1.

XRD pattern of ZIF-67 and MCM-41/ZIF-67 composites.

FT-IR analysis has been carried out to identify the functional groups of the obtained materials, and the results are shown in Figure 2. Each sample exhibit the presence of a sharp absorption band at a wavenumber of 423 cm−1, due to the Co▬N stretching vibration, indicating a bond between Co and N of the 2-methylimidazole ligand [25]. An absorption band at 693 cm−1 may be attributed to the bending vibration of the ring 2-metilimidazole [26]. Absorption peaks at wavenumbers of 755 and 1577 cm−1 may be resulted from out-of-plane vibrations and stretching vibrations of C〓N in 2-methylimidazole ligands. The occurrence of C▬N bending vibration has been identified from the appearance of a peak at wavenumber of 992 cm−1, while stretching vibration from C▬N is identified at wavenumber 1141 cm−1. Absorption bands at wavenumbers 2926 and 3134 cm−1 appear due to stretching vibration of C▬H sp3 aromatic ring on 2-methylimidazole and stretching vibration of C▬H sp2 on aliphatic hydrocarbon chains [25]. The characteristic peak of MCM-41 that appears at wavenumber of 1050 cm−1, as a result of Si▬O▬Si asymmetric vibration, is seen in the MC(5)/ZIF-67 composite spectrum and appears more pronounced in the MC(10)/ZIF-67 composite. This observation has indicated the existence of MCM-41 in the composite.

Figure 2.

FT-IR spectra of ZIF-67 and the composites.

Surface morphology of ZIF-67, as is shown in Figure 3(a), has a cubic shape, similar to that reported by Qian et al. [18]. Likewise, the MC(10)/ZIF-67 composite also has a uniform surface morphology, as is shown in Figure 3(b). The results of SEM showed that the presence of mesoporous silica resulted in the increase in particle size, while the cube shape and more uniform surface morphology remained unchanged. The SEM images may indicate that the growth of ZIF-67 has taken place inside the pores as well as on the surface of mesoporous silica. The phenomenon is reinforced by TEM image of the MC(10)/ZIF-67 composite, in which the characteristic hexagonal pore shape of MCM-41 is not seen any more in Figure 3(c).

Figure 3.

SEM image of (a) ZIF-67 (b) MC (10)/ZIF-67 (c) and TEM image of MC (10)/ZIF-67.

Nitrogen adsorption-desorption isotherms and pore size distributions of ZIF-8, and the composites are presented in Figure 4(a) and (b), respectively, and the results of BET surface area and pore size are summarized in Table 1.

Figure 4.

(a) N2 adsorption-desorption isotherm and (b) pore distribution of ZIF-67 and the composites.

MaterialsSBETa (m2/g)Vmesob (cm3/g)Vmicroc (cm3/g)Dd (nm)

Table 1.

Summary of the textural properties of the synthesized material at different addition of MCM-41.

BET surface area.

Mesopore volume calculated using BJH method.

Micropore volume calculated using t-plot method.

Average pore diameter.

As shown in Figure 4(a), type I isotherm adsorption curves of ZIF-67 and the composites have indicated that adsorption occurred in micropores of the samples that have high surface area. At a relatively higher pressure (P/P0 = 0.85–1), the amount of gas absorbed increased and a narrow vertical hysteresis loop was observed on all samples, which may be due to the presence of interparticle mesoporous. Based on the BET equation, the highest surface area was observed for MC(10)/ZIF-67 (1250.6 m2/g). The high surface area may result from the formation of ZIF-8 particles inside the MCM-41 mesopores so as to produce new micropores with high surface area [27]. The pore distribution curves of ZIF-67 and the composites based on the BJH method are shown in Figure 4b, in which microporous and mesoporous distributions have been observed (Table 1). It can be concluded that the addition of mesoporous silica into the ZIF-8 synthesis results in the increase in the pore volume and pore diameter of the obtained composites (Figure 4b).

Figure 5.

Thermogravimetric profiles of ZIF-7 and MC(10)/ZIF-67 composite.

The results of TGA, as is shown in Figure 5, confirmed two-stage process of decomposition of ZIF-67 and MC(10)/ZIF-67 composite.

Figure 6.

Effect of contact time on MO adsorption.

At a temperature range of 35–325°C, a mass decrease of 7.68% was observed, as a result of the loss of guest molecules of solvent or ligands that occupied the pores or surface of the samples [18]. Furthermore, a sharp decrease of 60.05% mass was observed in the temperature range of 325–429°C, which considered as decomposition of 2-methylimidazole ligand and damage of ZIF-67 structure. In addition, it can be seen in Figure 5 that the thermal stability of the MC(10)/ZIF-67 was slightly higher than that of ZIF-67. The observation was in accordance with the result reported by Bhatt et al. [28]. Also, higher remaining mass of the composite as compared to the ZIF-67 was due to presence of SiO2 from the MCM-41 added.

3.2 Adsorption kinetic studies

Kinetic study of MO adsorption was carried out using 20 mL of MO solution with a concentration of 100 mg/L. The contact times were varied in the range of 5–40 min, while the weight of adsorbent was 10 mg. The effect of contact time on MO adsorption for ZIF-67, MC(5)/ZIF-67, and MC(10)/ZIF-67 materials is illustrated in Figure 6. It can be seen that adsorption capacities increased with the increase in contact time to reach a maximum value after 25 min, after which a more stable adsorption capacity was observed until 50 min. The results indicated that the empty space of pores and the surface of adsorbent have been completely filled with adsorbate [29].

The kinetics data were analyzed using pseudofirst-order and pseudosecond-order kinetic models using Eqs. (3) and (4).


Based on the calculation of adsorption kinetics with Eqs. (3) and (4), graph plots were performed on each of the adsorption kinetics models and the obtained graphs are shown in Figure 7. MO adsorption kinetics model of ZIF-67, MC(5)/ZIF-67, and MC(10)/ZIF-67 adsorbents were determined by comparing the R2 values of each graph of the adsorption kinetics as shown in Table 2. It can be seen that correlation coefficient of the pseudosecond-order plot is higher than the pseudofirst-order plot. The results indicated that the mechanism of adsorption in all materials observed was as a result of chemisorption [30].

Figure 7.

Plots of (a) pseudofirst-order kinetics and (b) pseudosecond-order kinetics for the adsorption of MO.

AdsorbentQe(exp)Pseudofirst orderPseudosecond order

Table 2.

Kinetic parameters and correlation coefficients for the pseudofirst-order and pseudosecond-order equations.

Adsorption of MO at different initial concentrations was carried out at the optimum contact time obtained of 25 min with MO concentration in the range of 50–330 mg/L. As is shown in Figure 8, the adsorption capacity increased with the increase in initial concentration of MO and the equilibrium of adsorption capacity was observed at an initial concentration of 285.20 mg/L. By further increasing the initial MO concentrations, a stable equilibrium adsorption capacity was obtained.

Figure 8.

Effect of initial concentrations of MO.

The MC(5)/ZIF-67 showed highest Qe value of 167.64 mg/g, compared to other adsorbents. The results of adsorption studies have been in accordance with the results of N2 adsorption-desorption analysis, in which the higher the pore size of the adsorbent, the higher is the adsorption capacity. The largest pore size of MC(5)/ZIF-67, as a result of adding 5%w/w mesoporous silica during the ZIF-67 synthesis, has improved its performance in MO adsorption [26]. The large pore size of the MC(5)/ZIF-67 allowed MO molecules to easily diffuse in to the pores and interacted electrostatically with cobalt ions from ZIF-67.

3.3 Isotherm adsorption

The study of adsorption isotherms was based on Langmuir and Freundlich isotherms models as calculated in Eqs. (5) and (6):


Plots of adsorption isotherm obtained from the calculation are presented in Figure 9. The calculated correlation coefficient for each adsorbent used approaches with the value of 1 in the Langmuir model (Table 3). These results indicated that the adsorption process occurred in accordance with the Langmuir adsorption isotherm model, which led to the assumption that adsorption occurred on a specific homogeneous surface of the adsorbent, which had the same energy for monolayer adsorption [31].

Figure 9.

Plots of (a) Langmuir and (b) Freundlich models of MO adsorption.

Qm (mg/g)KL (L/mg)R2KF (mg/g)nR2

Table 3.

Langmuir and Freundlich isotherm parameters for the adsorption of MO.

As an anionic dye, MO contains SO3 group in its molecular structure. The adsorption of MO by ZIF-67 and MCM-41/ZIF-67 composites can occur as a result of the electrostatic interaction between the SO3 group and the positive charge of cobalt ion from ZIF-67 [12]. In addition, the imidazole rings of ZIF-67 may interact with the benzene rings from MO molecules through π-π stacking [16, 19]. The molecular interaction of MO with ZIF-67 is illustrated in Figure 10.

Figure 10.

Mechanism of MO adsorption to ZIF-67.

4. Conclusions

ZIF-67 and MCM-41/ZIF-67 composites have been successfully synthesized at room temperature in aqueous solution with addition of TEA as a deprotonating agent. The results of characterization using XRD indicated that both ZIF-67 and composites exhibited the same diffractogram patterns, with characteristic peaks at 2θ of 7.32, 10.36, 12.69, 14.66, and 16.40°, similar to that of reported ZIF-67. In addition, the absorption bands of FTIR spectra of all composites appeared at the same wavenumber as observed for synthesized and the reported ZIF-67. SEM images showed similar cube shapes of surface morphology between ZIF-67 and MC(10)/ZIF-67 composites. The results of analysis by adsorption-desorption N2 showed that the highest surface area of 1250.6 m2/g was observed for MC(10)/ZIF-67. The highest adsorption capacity toward MO in aqueous solution of 167.6 mg/g was achieved by MC(5)/ZIF-67 adsorbent, and followed a pseudosecond-order adsorption kinetics and Langmuir adsorption isotherm.


We gratefully acknowledge funding from Institut Teknologi Sepuluh Nopember (ITS) Surabaya, through Laboratory Research Grant 2018, and Material Chemistry and Energy Laboratory, Department of Chemistry-ITS, for facilities supporting this work.

© 2019 The Author(s). Licensee IntechOpen. This chapter is distributed under the terms of the Creative Commons Attribution 3.0 License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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Ratna Ediati, Pramita Elfianuar, Eko Santoso, Dety Oktavia Sulistiono and Muhammad Nadjib (May 29th 2019). Synthesis of MCM-41/ZIF-67 Composite for Enhanced Adsorptive Removal of Methyl Orange in Aqueous Solution, Mesoporous Materials - Properties and Applications, Manjunath Krishnappa, IntechOpen, DOI: 10.5772/intechopen.84691. Available from:

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