Decomposition of the Methylene Blue Dye Using Layered Manganese Oxide Materials Synthesized by Solid State Reactions

Becerra, M. E.; Suarez, A. M.; Arias, N. P.; Giraldo, O.

doi:https://doi.org/10.1155/2018/4902376

International Journal of Chemical Engineering

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Abstract Introduction Materials and Methods Results and Discussion Conclusions Data Availability Conflicts of Interest Acknowledgments References Copyright Related Articles

Research Article | Open Access

Volume 2018 | Article ID 4902376 | https://doi.org/10.1155/2018/4902376

Decomposition of the Methylene Blue Dye Using Layered Manganese Oxide Materials Synthesized by Solid State Reactions

M. E. Becerra,^1,2,3,4,5A. M. Suarez,^3,5N. P. Arias,^4,6and O. Giraldo^1,3,4

Academic Editor: Donald L. Feke

Received26 Feb 2018

Accepted24 Jun 2018

Published30 Jul 2018

Abstract

The modulation in the synthesis parameters of layered manganese oxides allowed us to produce materials with different AC conductivities. These conductivities were correlated with the catalytic performance of the materials in the decomposition of methylene blue, as a model of electron transfer reactions. The manganese oxides were prepared by thermal reduction of KMnO₄ at 400°C and 800°C where one sample was heated at 1°C/min and the other was heated at 10°C/min. The materials were characterized by atomic absorption, average oxidation states of manganese, X-ray diffraction, thermogravimetric analysis, and scanning electron microscopy. The results indicate that, by increasing the synthesis temperature, both the lamellar arrangement and the crystal size increased, while the Mn⁴⁺ amount in the material decreased. Furthermore, it was observed that as the conductivity increases for the materials, the catalytic performance also increases. Therefore, a direct correlation between the conductivity and catalytic performance can be established. For example, the layered manganese oxides material synthesized at 400°C, using a heating rate of 10°C/min, showed the highest AC conductivity and had the best performance in the degradation of methylene blue. Finally, we propose a general mechanism for understanding how manganese oxides behave as catalysts that produce oxidizing species from H₂O₂ which degrades methylene blue. Our proposed mechanism takes into consideration the state of aggregation of the catalyst, the availability of Mn⁴⁺, and the electrical conductivity.

1. Introduction

Today’s world requires efficient, clean, and environmentally friendly processes. In this context, manganese oxide base materials are an alternative, since by changing the synthesis parameters it is possible to modulate several characteristics: structure, composition, morphology, and electrical conduction [1–3], among others. These features allow designing materials with applications in the primary and secondary batteries [4], supercapacitors [5], catalytic processes [5–7], and the degradation of dyes [8], among others. A recent critical review [9] accounts for the environmental catalytic applications of the Mn-based oxides and recognizes them as one of the most promising catalysts.

A simple route for obtaining birnessite-type layered manganese oxide is the thermal reduction of KMnO₄ [6]. Birnessite consists of MnO₆ octahedrons where the Mn atoms are present as Mn⁴⁺ and Mn³⁺ ions. The presence of Mn³⁺ ions generates an excess negative charge on the layers, which is offset by cations, commonly Na⁺ or K⁺, and a monolayer of water molecules in the interlayer region [10, 11]. These materials show ionic conduction, due to the movement of the interlaminar cation, and the electronic conduction of (hopping) electrons in the layers [1–3]. The characterization of manganese oxides by AC conductivity is a nondestructive experimental technique, which can provide relevant information on the potential performance of these materials in redox reactions, which can be a useful tool and easy to apply for the design of heterogeneous catalysts for applications that are likely to spread to several redox reactions.

To correlate the conductivity with the catalytic potential of birnessite in electron transfer reactions, its performance in the degradation of methylene blue (chloride 3,7-bis (dimethylamino)phenothiazine-5-inio) was evaluated as a model reaction. The methylene blue (MB) degradation has been studied widely by using Mn-doped g-C₃N₄ [12], ferrimagnetic materials [13], nickel oxide nanoparticles [14], Au/ZnO [15], and titanium oxides [16, 17], among others. In contrast, few studies report the use of manganese oxides (MnOx) for the MB degradation. Some of those report the use of hydrogen peroxide as an oxidizing agent to generate the reactive oxygen species (ROS), responsible for degrading MB up to the mineralization to carbon dioxide, sulfate, and nitrate [18, 19].

The reaction mechanisms proposed for the MB degradation using MnOx and H₂O₂ [19, 20] suggest a reaction between hydrogen peroxide and the surface of MnOx giving the formation of ROS mainly singlet oxygen (¹O₂) and free radicals such as OH^• and O₂^•−. However, we did not find a general mechanism for electron transfer reactions that consider the catalyst aggregation state, the Mn⁴⁺ availability, the reactive oxygen species formation, and electrical conductivity, as relevant features in the catalytic activity of the birnessite materials. In the present study, we propose a general mechanism that considers all the experimental parameters including the conductivity.

2. Materials and Methods

2.1. Preparation of the Samples

The samples for this study were synthesized by thermal reduction of KMnO₄ (Merck, 99%) [6] at a heating rate of 1°C and 10°C/min. The final temperatures were 400°C and 800°C. Once calcinated, the materials were washed with distilled and deionized water (DDW) until the pH of 9.50 was obtained, and finally, the materials were dried at 60°C for 48 hours. The materials obtained are named according to the final synthesis temperature and heating rate as follows: 4R1 and 8R1 for the first set and 4R10 and 8R10 for the second set.

2.2. Characterization

2.2.1. Atomic Absorption Spectroscopy (AA)

The elemental analysis was performed on a Thermo Series S4 atomic absorption spectrophotometer. About 100 mg of the sample powder was taken for analysis and dissolved in 10.0 mL solution of 37% HCl : DDW in a 2 : 1 ratio, and it was then heated to obtain 50% of the initial volume. 1.0 mL of lanthanum chloride at 1.0% was added, and the final volume was adjusted with DDW at 100.0 mL for Mn and K content determination.

2.2.2. Average State of Manganese Oxidation (AOS)

The analysis of each sample was performed in duplicate, following the method reported by Glover et al. [21]. Briefly, to determine the total content of Mn, approximately 40 mg of material was dissolved in 10.0 mL of 37% HCl and 10.0 mL of DDW; then, they were heated until the solution became transparent, and the volume was adjusted to 100.0 mL. 100.0 mL of a saturated solution of Na₂P₂O₇·10H₂O was added to 10.0 mL of the prepared sample, the pH was adjusted to about 7.00 with 37% HCl, and it was titrated by potentiometry with KMnO₄ 0.101 M up to potential jump higher than 100 mV. To determine the available oxygen, approximately 40 mg of the sample was dissolved in 15.0 mL of a 0.10 M (NH₄)Fe(SO₄)₂·6H₂O (FAS) (Merck 98%) solution acidified with H₂SO₄ at 98% and titrated with 0.101 M KMnO₄ until it turned pink. 1.0 mL of FAS was used as a blank under the same conditions described above. The average oxidation state of manganese was calculated like this AOS = (total moles of O/total moles of Mn) × 2.

2.2.3. X-Ray Diffraction (XRD)

The XRD patterns from the powdered samples were obtained at room temperature in a Rigaku MiniFlex II diffractometer equipped with a radiation source of Cu Kα (λ = 1.5406 Å) at 30 kV and 15 mA in the continuous mode. Data were taken from 3 to 70° in 2è with an accuracy of 0.01° in 2è at a scan rate of 0.2°/min and a step size of 0.02° in 2θ. The estimated crystal size was performed using the Debye–Scherrer equation [22]:where is the Cu Ka radiation and and are the full-width at half maximum of the more intense diffraction peak in the sample and silicon standard, respectively.

2.2.4. Thermogravimetric Analysis (TGA)

Thermogravimetric analysis was performed on a TA Instruments, TGA Q500 model, with a sensitivity of 0.1 µg, a resolution of ± 0.1°C, and an accuracy of 0.01%. The measurement was doing over approximately 10 mg of the sample and analyzed under N₂ with a flow of 100.0 mL·min⁻¹, in a temperature range of 25°C to 800°C, at a heating rate of 10°C min⁻¹.

2.2.5. Scanning Electron Microscopy (SEM)

The micrographs of the materials were taken on a QUANTA 250 FEI microscope with a tungsten electron source, with a resolution of 3.0 nm at 30 kV. The samples were deposited on a carbon tape and analyzed in the high vacuum mode with a power voltage range between 10.00 kV and 15.00 kV and magnifications of 10000x.

2.2.6. AC Conductivity at Room Temperature

The AC conductivity of the powder materials was measured at 21°C and 50% relative humidity in accordance with the methodology proposed by Arias et al. [1] in a SOLARTRON 1260 equipment with a SOLARTRON 1296 dielectric interface and a 1296-4A test cell equipped with two bronze electrodes in a parallel arrangement in two-point configuration. The distance between the working and the reference electrodes was 1.57 mm. To prevent border effects and eddy currents, the working electrode, with an effective diameter of 20 mm, has a guard ring. The acquisition of impedance data was performed using the Z-plot software version 3.3, in a frequency range of 10 MHz to 0.1 Hz with a voltage amplitude of 100 mV rms. The analyses were performed in duplicate. For treating the data, a Z-view software version 3.3 (Scribner Association) was used.

The real-AC conductivity was found from the impedance data usingwhere is the thickness of the sample (cm), is the effective electrode area (cm²), is the real component of the impedance, is the imaginary part of the complex impedance, is the geometric factor of the sample, and is the conductance.

2.3. Catalytic Test: Degradation of Methylene Blue

The degradation of methylene blue at room temperature was performed by the method reported by Zhang et al. [19], which is described briefly: 150.0 mL of methylene blue at 30 ppm and 30.0 mg of the MnOx material were stirred for 20 minutes, and then 6.8 mL of H₂O₂ at 30% were added. The concentration of methylene blue was monitored at baseline and in the following reaction times: 15, 30, 60, and 120 minutes. For the tests, two aliquots of 1.0 mL were taken and centrifuged for 4 minutes at 5000 rpm. The concentration of methylene blue was measured by UV-Vis spectroscopy at λ = 665 nm.

To determine the effect of the superoxide anion in the degradation of the dye [19], the same reaction was carried out in the presence of 100 mM of gallic acid.

3. Results and Discussion

3.1. X-Ray Diffraction (XRD)

The diffraction patterns from the set of synthesized materials heated at 1°C/min heating rate (Figure 1(a)) show the characteristic diffraction peak of birnessite-type layered manganese oxide [6, 23] around 12.30° (7.19 Å). There were no crystallographic phase changes of the layer structure as it was determined from XRD patterns. However, in the range of 30° to 70° (Figure 1(b)), the characteristic peaks of certain lamellar stacking faults appear in the samples that have been heated to 400°C. Thus, the presence of diffraction peaks at 36.50°, 37.26°, 41.98°, 65.56°, and 66.90° in the 4R1 material has been reported for a turbostratic stacking fault in manganese oxides [24]. In 8R1, the peaks located at 36.02° (2.49 Å), 38.24° (2.35 Å), 40.88° (2.20 Å), 44.28° (2.04 Å), 53.08° (1.72 Å), and 65.30° (1.42 Å) were characteristic of hexagonal-type birnessite [24, 25], and weak peaks at 35.18° (2.55 Å), 37.42° (2.40 Å), 40.06° (2.25 Å), 43.70° (2.07 Å), 51.04° (1.79 Å), 52.44° (1.74 Å), and 64.06° (1.45 Å) were typical of orthogonal-type birnessite [25]. These changes indicate that the structural order increases as the temperature increases. The XRD patterns for the synthesized materials at 10°C/min heating rate are shown in Figure 1(c). There was no evidence of significant changes in the lamellar arrangement (Figure 1(d)), compared with the materials synthesized at 1°C/min (Figure 1(b)).

(a)

(b)

(c)

(d)

These figures show that materials that were heated at the same temperature have similar structure independent of the rate at which they heated. In contrast, the estimated crystal size was affected by both the synthesis temperature (Table 1) and the heating rate. At higher temperatures and lower heating rate, larger crystal size was obtained.

3.2. Chemical Composition, Average Oxidation State, Thermal Stability, and Structural Formulas Determination

As it can be seen in Table 1, the content of K⁺ does not vary significantly in the analyzed samples, whereas the Mn⁴⁺ content varies with both the temperature and the heating rate.

In the materials calcined at 800°C, a lower content of Mn⁴⁺ is observed in comparison with those that were calcined at 400°C. The material 4R10 showed the highest content of Mn⁴⁺. The AOS for Mn is greater for 4R1 and 4R10 than for 8R1 and 8R10. These values were also higher than the average oxidation state values reported for birnessite-type materials obtained by low-temperature oxidation-reduction methods [1, 26]. The thermal reduction of KMnO₄ generated materials with higher content of Mn⁴⁺ at lower temperatures [2, 27]. The content of Mn⁴⁺ has been reported as a critical surface species in similar materials [18, 19, 28–30] due to the fact that it initiates the decomposition reactions of NOx, SOx [30], and dyes on the surface. Thermal stability studies through TGA showed that the mass losses in the two sets of synthesized materials (Figures 2(a) and 2(b)) up to 150°C were associated with physisorbed water, between 150°C and 250°C with structural water. Finally, for temperatures above 250°C, the mass losses were associated with a structural change involving the release of oxygen, as it has been reported in previous studies [6]. In general, the thermal stability of the material increases with the synthesis temperature, and no significant differences were observed concerning the heating rate.

(a)

(b)

With the information obtained by the atomic absorption analysis, the average oxidation, and thermal gravimetric analysis, the different structural formulas were calculated (Table 1) using a modification of the equation reported by Gaillot et al. [23, 31] in accordance with the following equation:where is the average oxidation state of Mn, is the K/Mn ratio, and is the water content calculated from the mass loss of up to 250°C under a nitrogen atmosphere.

3.3. Morphological Analysis by Scanning Electron Microscopy (SEM)

The morphology of the materials (Figure 3) shows particle aggregates of different sizes, with a sponge morphology. The larger particles in 8R1 and 8R10 materials take the form of a mesh with different spacings between crystals.

(a)

(b)

(c)

(d)

These results showed a relationship between aggregate size and both temperature synthesis and heating rate, as it has been reported for ceramic materials like perovskites [32]. The morphological changes were consistent with the increase in the crystal size as it was estimated by the XRD (Table 1).

3.4. AC Conductivity at Room Temperature

The comparative study of the conductivity of synthesized materials (Figure 4) showed that those obtained at 10°C/min had conductivities up to 1 order of magnitude higher than materials obtained at 1°C/min. In materials synthesized at 1°C and 10°C/min, the real component of the complex conductivity in the low-frequency region (0.1 Hz to 10³ Hz) decreases as the synthesis temperature increases. Above 1000 Hz, the conductivity depends more on the frequency, according to the “Universal Johnscher’s Law” [33], while at low frequencies, it is less dependent, which suggests DC conductivity. This phenomenon is similar to the one reported for birnessite synthesized by thermal reduction routes [2] and soft chemistry routes [1, 3]. For frequencies up to 1 × 10⁵ Hz, in both sets of materials, σ′ increases at lower temperature synthesis, and at higher frequencies, the conductivity become similar, having values in the range of semiconductors [34–36]. The increase in conductivity with the frequency indicates a joint movement of charge carriers and changes in the conduction mechanisms [1, 2], mainly dominated by short-range conduction.

The conductivity as a function of the preparation temperature (Figure 4) showed that, at 400°C, the materials were more conductive, thereby suggesting that the lamellar arrangement and the average oxidation state of manganese affect the conduction mechanisms as it was reported by Arias et al. [1, 2]. On the contrary, the presence of Mn⁴⁺, understood as the amount of surface Mn⁴⁺ per nm of the crystal size (Table 1) as well as the stacking faults found by XRD (Figure 1), favors the electron “hopping” mechanism [1, 37] and therefore the electrical conduction. Moreover, the high heating rate used in the synthesis of these materials favors the generation of structural defects and microcracks [38] that modified the electrical conduction pathways. Also, both the variation in the lamellar ordering [24] and the birnessite crystal size alter this conduction routes. Consistent with the above, it was found that the conduction process was more favorable in 4R10. This material had the largest lamellar disorder, Mn⁴⁺ content, and the smallest crystal size.

3.5. Catalytic Degradation of Methylene Blue

With the aim to correlate the conductivity results with the catalytic performance, the catalytic degradation of methylene blue (MB) was used as the reaction model. Therefore, the synthesized materials were tested in the MB degradation reaction using hydrogen peroxide as an oxidizing agent. The 4R10 material exhibits the best performance in this reaction as it can be seen in Figure 5(a). This result was consistent with its highest conductivity (Figure 4), the content of Mn⁴⁺, and the smallest crystal size (Table 1) among all materials studied as it was discussed above. The literature reports that the materials with smaller crystal size exhibit better catalytic performance [38–41], which can be correlated with the increased surface area, necessary for reactions that occur mainly on the surface of the material [28, 39] like in those of MB degradation.

(a)

(b)

(c)

To study the maximal degradation of MB achieved by the 4R10 material, the reaction was monitored up to 1000 min. Between 120 and 300 min, the degradation percentage of MB was 10% higher than that obtained at 60 min (Figure 5(b)). At 600 min, a 63.0% of degradation was reached. After 600 minutes, no significant increase was observed in the disappearance of MB. When only H₂O₂ was used in the MB degradation, the percentage of the demise of MB was 9.3% at 120 min of reaction and 6.4% using only 4R10 (inset in Figure 5(b)), while the MB degradation with 4R10 in the presence of H₂O₂ was 50%. These observations suggest that MB degradation occurs through the formation of reactive oxygen species (ROS) from H₂O₂ over MnOx such as O₂^•− and OH^• [19, 42, 43]. The formation of the OH^• radical finally promotes the degradation of the organic dye until its complete mineralization and protonation of the peroxide HO₂⁻ anion which regenerates the H₂O₂, and it is shown as

To elucidate if radical participate in this reaction, an additional experiment was done. It consisted of the addition of gallic acid, a scavenger specific for the radical [44]. Figure 5(c) shows a reduction to 16.1% in the percentage of degradation of MB at 120 minutes of reaction. These results confirm the participation of these radicals in the mechanism of MB degradation.

3.6. Proposed Mechanism Involving Electron Transfer

Oxidative degradation of organic compounds, especially methylene blue, has been reported as a surface reaction that generates reactive oxygen species [45, 46]. The oxidation of methylene blue through Fenton-type reactions involves the generation of free radicals from an oxidizing substance and from a material that can potentially provide electrons [45, 47]. In this case, hydrogen peroxide is decomposed by the manganese oxide to generate highly reactive oxygen species [18, 19, 45, 48].

The reaction between the birnessite and the hydrogen peroxide involves the adsorption of hydrogen peroxide over the material surface. The hydrogen peroxide should be adsorbed by an acid-Lewis site, with the Mn⁴⁺ being fundamental versus the Mn³⁺ because of its most acidic characteristic. Finally, an electronic transfer from the hydrogen peroxide to the manganese (4+) led to the oxidation of the hydrogen peroxide to form a reactive oxygen species [19].

According to the results obtained in this study and considering the availability of Mn⁴⁺ in the surface of the material, Figure 6(a) shows the reaction mechanism for the formation of ROS from H₂O₂ and the layered material, mainly considering the presence of the Mn⁴⁺/Mn³⁺ [19] system. The described mechanism suggests acid-base reactions on the surface of the layered material, which has active sites of Mn⁴⁺. Initially, an acid-base reaction occurs between one of the oxygen molecules of H₂O₂ and Mn⁴⁺, followed by an electrostatic attraction between the hydrogen molecules of H₂O₂ and the layered material, which is well known to have a negative charge [1, 10]. Once this interaction is established, a homolytic rupture is suggested in the bond formed by Mn⁴⁺ and the oxygen of the peroxide, with the consequent reduction from Mn⁴⁺ to Mn³⁺ with the formation of the superoxide radical O₂^•−. The original active site would be regenerated by the transfer of an electron from Mn³⁺, which has remained after the reaction, to an adjacent Mn⁴⁺ ion through the oxobridge, as illustrated in Figure 6(6). The electron transfer process from Mn³⁺ to Mn⁴⁺ via an oxobridge (electronic hopping) is well known in perovskite-type manganese oxides [49]. The described process should be facilitated in those materials, which have a higher electronic conductivity, thus helping to regenerate the active sites efficiently and thus increasing the catalytic activity of the material. It is suggested that this mechanism is most likely in materials with high oxidation state, that is, the highest content of Mn⁴⁺.

(a)

(b)

(c)

(d)

Figure 6

Proposed mechanism for the formation of the superoxide and hydroxyl radicals in MB degradation. (a) Hydrogen peroxide adsorption at an Mn⁴⁺ active site (oxygen vacant) with a posterior electron transfer to the Mn⁴⁺ active site and formation of a superoxide radical and an Mn³⁺ inactive site. There is an electron transfer process from an Mn³⁺ ion to an adjacent Mn⁴⁺ ion via an oxobridge (electronic hopping) to finally regenerate the Mn⁴⁺ active site. (b) A similar step as in (a) but in this case without regeneration of the active side. (c) Oxidation of Mn³⁺ with O₂ at the oxygen vacant site to restore the Mn⁴⁺ active site and superoxide radical. (d) Formation of hydroxyl radical (OH^•) and regeneration of hydrogen peroxide.

Another possible scenario would be given when the active sites of Mn⁴⁺ are adjacent only to Mn³⁺ ions. As shown in Figure 6(b), the reaction mechanism would be like that described above, except that the active sites that have been reduced to Mn³⁺ would no longer be so easily regenerated. For this purpose, it is proposed that an oxygen molecule can oxidize Mn³⁺ to Mn⁴⁺ and generate a superoxide radical, as it is illustrated in Figure 6(c). Finally, Figure 6(d) shows the reactions for the formation of hydroxyl radical from superoxide radical and the regeneration of hydrogen peroxide.

The proposed mechanism is consistent with experimental data and explains the trends found between conductivity, the average oxidation state of Mn, and catalytic activity of the studied materials. Unlike mechanisms reported in the literature, this mechanism not only collects experimental observations but also considers explicitly the surface sites on which the reaction may be occurring, indicating the state of aggregation of the catalyst and the heterogeneous nature of the process.

4. Conclusions

We obtained birnessites whose conductivity differed significantly as a result of variations in the synthesis temperature and heating rate. A direct relationship between catalyst conductivity and MB degradation performance was observed. The 4R10 material which had a smaller crystal size, higher content of Mn⁴⁺, and higher conductivity showed the largest percentage of MB degradation. A general mechanism was proposed for understanding how manganese oxides behave as catalysts that produce oxidizing species from H₂O₂ that degrade methylene blue. Our proposed mechanism takes into consideration the following experimental observations: the availability of Mn⁴⁺, the electrical conductivity, and the heterogeneous nature of the process. This relationship can be useful and easy to apply for the design of heterogeneous catalysts for applications that are likely to spread beyond the studied reaction.

Data Availability

The data used to support the findings of this study are available from the corresponding author upon request.

Conflicts of Interest

The authors declare that there are no conflicts of interest regarding the publication of this paper.

Acknowledgments

The work at the Universidad Nacional de Colombia, Manizales Campus, was supported by Facultad de Ciencias Exactas y Naturales. The authors also acknowledge Laboratorio de Química (Atomic Absorption Analysis), Laboratorio de Magnetismo y Materiales Avanzados (Thermal and Calorimetric Analysis), and Laboratorio de Microscopia Electronica de Barrido (SEM) at the Universidad de Caldas. A. M. Suarez also acknowledges Facultad de Ciencias Exactas y Naturales, Universidad Nacional de Colombia-Manizales, for a research internship.

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Copyright © 2018 M. E. Becerra 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.

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