Impregnation of ZnO onto a Vegetal Activated Carbon from Algerian Olive Waste: A Sustainable Photocatalyst for Degradation of Ethyl Violet Dye

Abdessemed, Ala; Rasalingam, Shivatharsiny; Abdessemed, Sanna; Djebbar, Kamel El Zin; Koodali, Ranjit

doi:https://doi.org/10.1155/2019/4714107

International Journal of Photoenergy

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

Research Article | Open Access

Volume 2019 | Article ID 4714107 | https://doi.org/10.1155/2019/4714107

Impregnation of ZnO onto a Vegetal Activated Carbon from Algerian Olive Waste: A Sustainable Photocatalyst for Degradation of Ethyl Violet Dye

Ala Abdessemed,^1,2Shivatharsiny Rasalingam ,³Sanna Abdessemed,¹Kamel El Zin Djebbar,²and Ranjit Koodali⁴

Academic Editor: Xuxu Wang

Received25 Jul 2018

Revised03 Nov 2018

Accepted21 Nov 2018

Published25 Feb 2019

Abstract

This study is aimed at developing a simple and low-cost method to fabricate ZnO-loaded porous activated carbon (AC-ZnO) prepared from the Algerian olive-waste cakes and utilize it as a photocatalyst for the degradation of Ethyl Violet dye. The synthesized AC-ZnO material was characterized using powder X-ray diffraction, BET surface area measurements, Raman microscopy, thermogravimetric analysis, UV-visible diffuse reflectance spectroscopy, and zeta potential measurements. The degradation efficiency was evaluated with Ethyl Violet (EV) dye in aqueous solution under UV irradiation supplied by a Xenon arc lamp through a Pyrex glass filter (cutoff 280 nm), and the degraded products were identified by using electrospray ionization mass spectroscopy. Additional experiments were carried out under N₂ flow and with isopropyl alcohol to examine the role of superoxide and hydroxyl radicals, respectively. The amount of ^●OH radical formed on irradiated AC-ZnO was tested with terephthalic acid which can act as a chemical trap for the ^●OH radicals. The results from this study indicate that the AC-ZnO is a potential catalyst for the pollutant removal and the ^●OH radicals are the key species for the degradation of EV. Further, this study opens up an opportunity to produce cheaper activated carbon support from olive wastes for environmental remediation applications.

1. Introduction

Semiconductor photocatalysis has become very attractive due to its potential contributions in the field of environmental remediation. In particular, TiO₂ has been widely utilized as a photocatalyst for the removal of aqueous pollutants. Although most of the photocatalytic studies use TiO₂ as an effective photocatalyst, ZnO has also gained attention due to its favorable photocatalytic properties [1–4]. The design and development of highly efficient photocatalytic materials seem to be challenging. Several methods have been utilized to prepare photocatalysts, such as sol-gel, hydrothermal process, precipitation, and impregnation [5–9]. Fabricating materials with favorable physicochemical characteristic features are key for the design of effective photocatalysts. In this regard, porous materials, which have favorable textural properties, such as high surface areas and large pore volumes and pore sizes, have been used as support to disperse semiconductor photocatalysts. Among them, activated carbon has been found to be a promising candidate because of its favorable textural properties [10, 11]. However, commercially available activated carbons are still expensive in many countries, (especially developing ones) due to the need of processing the raw material (charcoal, coal, or carbon) by physical and/or chemical methods. Thus, the high costs hamper their application in several fields [12]. This subsequently leads to a growing interest in the research on the economical production of activated carbons. In recent years, a number of studies have shown that some industrial and agricultural by-products that include waste paper [13], waste tires [14], rice hull [15], corncob [16], apricot stone [17], date stone [18], and coconut husk [19] have the potential for being used as precursors to prepare activated carbons for the removal of dyes from wastewater. In this regard, olive wastes are potential candidates for the preparation of activated carbon, in comparison to the above materials. In particular, the use of lignocellulosic olive-waste cakes has received less consideration for activated carbon production [20, 21].

Algeria is one of the major producers of olive oil in the world [22]. During the manufacturing process of the olive oil, about 20% of oil is obtained; of the remaining percentages, 30% are waste solids and 50% is wastewater [23]. Olive-waste cakes or olive pomace, corresponding to the residue from the oil extraction process, represents a yearly average of tons [24]. The use of this material as a precursor for the preparation of activated carbon not only contributes towards the preparation of a catalyst or adsorbent for aquatic pollutant removal but also results in the effective removal and recycling of solid wastes to value-added products from olive oil production. Although there are several studies that have reported the preparation of activated carbon-supported materials for photocatalytic applications, existing studies are lacking in one or more of the following: (i) a low-cost preparation of activated carbon using Algerian olive-waste cakes, (ii) impregnation of photoactive ZnO on activated carbon, (iii) comprehensive physicochemical characterization of the support and the photoactive material, (iv) utilization of these materials for the removal of aquatic pollutants, especially, dye removal, (v) a thorough analysis of the photocatalytic by-products using electrospray ionization mass spectrometry (ESI-MS) analysis, and (vi) a systematic analysis providing a structure-activity relationship.

The present works explore the use of Algerian olive-waste cakes as potential feedstock for the preparation of activated carbon (AC) as a support for impregnation of ZnO. Further, the degradation of a cationic dye, Ethyl Violet (EV), using this sustainable catalyst prepared by dispersing ZnO on the AC catalyst (AC-ZnO) under (UV) light irradiation is also elaborated herein. Ethyl Violet (EV) is a synthetic cationic dye that belongs to the triphenylmethane (TPM) group which is highly soluble in water [25]. Among the various classes of synthetic dyes used in textile, paper, leather, cosmetic, and food industries, TPM dyes are the largest and most versatile group of dyes that plays a major role [26, 27]. These dyes are recalcitrant molecules as they are resistant to degradation. These dyes have complex aromatic structures, characterized by a chromophoric center comprising of three phenyl groups surrounding a central carbon atom [28, 29]. In particular, these TPM dyes are toxic, carcinogenic or mutagenic, and hazardous to health. Further, it has been reported that TPM can induce tumor growth in some species of fish and induce hepatic tumor formation in rodents. In addition, it causes reproductive abnormalities in rabbits and fish [30].

The study revealed that the newly synthesized material can be used for aquatic pollutant removal. Above all, the method used here for the preparation of AC is cost-effective, and thus, this study will create a path to utilize the Algerian olive waste in a creative and economic manner.

2. Materials and Methods

2.1. Materials

Without further purification, Ethyl Violet (EV) (Basic Violet 4) (Sigma-Aldrich) was employed as a model organic dye and deionized water () was used to prepare the solution mixtures. Hexane (Sigma-Aldrich), sodium hydroxide (Acros), potassium nitrate (Acros), conc. nitric acid (HNO₃) (ACS grade), terephthalic acid (TPA) (Acros, 98%), zinc nitrate hexahydrate (Zn(NO₃)₂.6H₂O) (Sigma-Aldrich), and isopropyl alcohol (Fisher Scientific) were used as received. Optima grade water was used for the ESI-MS studies.

2.2. Synthesis of the AC-ZnO Material

The olive-waste cake obtained from an oil factory located in Béjaia, Algeria, was used as raw material for the production of activated carbon support. First, the olive wastes were washed several times with tap water and then with distilled water to remove impurities; finally, it was purified by hexane to remove residual oil. The solid obtained was dried in open air. The dried olive-waste cakes were then calcined at 400°C for 30 min. in a muffle furnace, and the obtained charcoal was ground and sieved using standard sieves, where the diameter of the particles chosen was between 400 and 250 μm. The particles were then subjected to pyrolysis on a stream of nitrogen (N₂) (50 cm³/min.) at 800°C in a tubular furnace for 1 h.

Generally, preparation of activated carbon can be classified under two types, namely, physical activation and chemical activation [31]. In particular, chemical activation uses activation agents that include KOH, ZnCl₂, H₃PO₄, and H₂SO₄. Activation with KOH produces activated carbon with desirable pore size distribution [32, 33]. In addition, activation with KOH provides high specific surface area (~3000 m²/g) materials [34]. Although, there are no general mechanism for chemical activation, the type and amount of activating agent, the process, and the reaction condition that plays an important role in determining the structural properties of the materials. Therefore, according to a literature review, we adopted the most common chemical activation method, activation with KOH, which provides enhanced textural properties to the material, in particular, mesoporosity [35]. In addition, activation with KOH has a long-term history, where the activation of coal, coke, and charcoal has been performed with KOH since 1970s [31, 36, 37]. It was also reported that the activation with KOH will also increase the adsorbing capacity of the activated carbons [38, 39].

The carbonized olive cakes were then impregnated in a solution of KOH (3 N) with a mass ratio of 4 : 1 (i.e., 4 g of KOH per 1 g of pretreated carbon). After 24 h of stirring, the impregnated solid was separated by simple filtration of the solution and the product obtained was dried at 175°C and allowed to cool. After cooling, the activated carbon produced was washed several times with hot distilled water to remove the residual KOH until the pH of the depleted solution stabilized to a neutral value (). The next step was physical activation, where the activated carbon was heated to 900°C for 3 h in a tubular furnace under a nitrogen stream (N₂) (50 cm³/min.). The preparation of the catalyst (AC-ZnO) was done by impregnating the activated carbon with Zn(NO₃)₂.6 H₂O (10% w/w) followed by heating in a tubular furnace at 400°C for 6 h under a stream of nitrogen (50 cm³/min.). 10% loading was selected as optimum loading from the preliminary adsorption studies, and a better removal efficiency was attained with the 10% loading of ZnO. Therefore, in this study, we utilized the 10% (w/w) loading of ZnO on AC as the photocatalyst. Scheme S1 in the supplementary section summarizes the different steps for the preparation of the activated carbon and AC-ZnO.

2.3. Characterization

Powder X-ray diffraction (XRD) patterns were recorded at ambient conditions using the Rigaku Ultima IV instrument with Cu Kα radiation (), operated at an accelerating voltage of 40 kV, and an emission current of 44 mA. The angle ( values) scanned range was between 20 and 80° with a step size of 0.02°, and the scan speed was 1°/min. The crystallite sizes were determined by applying the Debye-Scherrer equation to the peaks at , 34.4°, 36.2°, 47.4°, and 56.5°. The diffraction patterns were analyzed using PDXL software provided by Rigaku. Raman spectra were recorded using a HORIBA Jobin Yvon LabRAM ARAMIS spectrophotometer with an internal He-Ne (532 nm) excitation laser. The unfiltered beam of scattered laser radiation was focused on the sample using a microscope objective (×50) for an acquisition time of 10 s. The radiation was then dispersed by an 1800 line/mm grating onto the CCD detector. Physisorption properties of the catalyst material were investigated by using the Quantachrome Nova 2200e surface area and pore size analyzer. The material was dried overnight at 70°C followed by extensive degassing at 200°C, and the N₂ adsorption-desorption isotherms were obtained at 77 K. Surface areas were calculated using the Brunauer-Emmett-Teller (BET) equation within the relative pressure () range of 0.05-0.30. The pore volume was obtained from the nitrogen amount adsorbed at the highest relative pressure . The pore size distribution was determined by applying the Barrett-Joyner-Halenda (BJH) equation to the desorption isotherm. Fourier transform infrared spectroscopy (FT-IR) was used to provide information regarding the surface properties. The spectra were recorded between 4000 and 350 cm^-1 on a Bruker-ALPHA instrument with 24 scans at a resolution of 4 cm^-1 by placing a small amount of the sample on the diamond crystal. The diffuse reflectance spectra (DRS) were obtained in the wavelength range between 190 and 700 nm using a Carry 100 Bio UV-Vis spectrophotometer equipped with a Harrick DR praying mantis accessory. SEM images were captured on an Oxford instrument. The surface charge of the synthesized materials was recorded by autotitration using a Zetasizer analyzer (Malvern Nano ZS-90) by adjusting the pH of AC-ZnO-electrolyte (KNO₃ in DI water) suspension. Deionized water was used as the diluent. Test samples were prepared with the molarity of 1 mg/mL by dispersing known amounts of the sample in aqueous 0.01 M KNO₃ solution. The pH was controlled by the autoaddition of 0.1 M KOH and/or HNO₃.

2.4. Photocatalysis Experiments

The photocatalysis experiments were performed by the following procedure. 25 mg of the photocatalyst AC-ZnO was dispersed in 50 mL of Ethyl Violet ((EV) with the initial concentration of 20 ppm and the initial pH was recorded as~ 8-9) solution in a quartz cylindrical jacket reactor. It was noted that the pH influences the behavior of Ethyl Violet spectrum; there was a change in the colour when the medium of the dye solution was acidic (). In particular, the colour of the dye turned to yellow at the pH of 1 and green and blue when the pH was at 1.5 and 3, respectively. Further, there was a widening in the band observed with a red shift when the medium was acidic. The characteristic peak for the dye solution was found at of 596 nm, and it was found that the dye is stable when the pH was maintained as basic (pH of ~8-9). Therefore, the pH was maintained as 8-9 throughout the experiment.

Then the suspension was stirred in the dark at 300 rpm for 30 min. to establish the adsorption-desorption equilibrium. Subsequently, UV light was supplied by a Xenon arc lamp (Newport 1000 W) through a Pyrex glass filter (cutoff 280 nm), while the reaction temperature was maintained at by channeling water in between the walls of the reactor throughout the course of the experiment (120 min.). The intensity of the irradiation was estimated to be ~95 mW·cm^-2. 5 mL of the reaction mixture was withdrawn initially at 10 min. intervals followed by 30 min. and 1 h intervals (i.e., 10, 20, 30, 60, and 120 min.). Then the collected samples were centrifuged at 3200 rpm for 15 min., filtered through 0.45 μm Millipore filter membrane, and the filtrate was then analyzed using UV-Vis spectroscopy.

Additional experiments were carried out under N₂ flow (absence of oxygen) and with isopropyl alcohol (IPA) to examine the roles of O₂^●– and ^●OH radicals, respectively. In order to detect the amount of ^●OH radicals formed on the surface of the irradiated catalyst (AC-ZnO), terephthalic acid (TPA) was used as a chemical trap. It is well known that ^●OH radicals rapidly react with TPA to produce highly fluorescent 2-hydroxyterephthalic acid (2-HTPA). In a typical procedure, 25 mg of the photocatalyst was added to 50 mL of ^-4 M TPA solution prepared using ^-3 M NaOH. Then the suspension was irradiated with UV light. 3 mL aliquots was drawn every 20 min. For a duration of 120 min., filtered through a 0.45 μm Millipore filter membrane, the clear solution was analyzed using Flouromax-4 (JY Horiba) fluorimeter. The fluorescence emission intensity of the 2-hydroxyterephthalic acid was recorded at 425 nm, after excitation at 315 nm. The intensity of the peak at 425 nm is proportional to the amount of ^●OH formed.

2.5. Analytical Techniques

The remnant concentration of the dye solution after the photocatalytic reaction was estimated by UV-Vis spectrophotometric method. The absorbance was recorded by following the peak at a wavelength of 596 nm, which corresponds to the absorption maximum of Ethyl Violet (EV). Quantification of the dye concentration at different time intervals was completed by using a calibration plot of EV drawn in the concentration range between 5 and 20 ppm.

A Varian 500-MS Ion Trap Mass Spectrometer was used for the identification of the dye fragments formed during the photocatalytic degradation. Ionization was completed by an electrospray ionization (ESI) source in a positive mode to separate the fragments on the basis of their mass to charge ratio. A 1 : 1 volume ratio of optima grade methanol and dye solution mixture was used to inject into the mass spectrometer. The operating parameters used for MS study are summarized in the supplementary section (Table S1). Finally, the remnant carbon content of the dye solution after degradation was evaluated by using a Shimadzu TOC-VCSH Total Organic Carbon (TOC) analyzer.

3. Results and Discussion

3.1. Powder XRD

Powder XRD patterns of the AC-ZnO prepared are shown in Figure 1. Well-defined peaks at the two theta degrees of 31.7°, 34.4°, 36.2°, 47.4°, 56.5°, 62.9°, and 67.9° corresponding to the diffraction planes of (100), (002), (101), (102), (110), (103), and (112), respectively, confirm the Wurtzite hexagonal structure of ZnO particles (JCPDS file 36-1451) [40–42].

Broad peaks at around 23° and 43° indicate the presence of the carbon support due to the (002) and (101) planes, respectively. These two peaks resemble with the XRD peaks obtained for the pure activated carbon support as illustrated in Figure S1 in the supplementary section. The crystallite size and the lattice constants of ZnO are calculated to be 209 Å and , and , respectively, consistent with previous reports [43, 44].

3.2. Raman Spectra

The Raman study further confirms the presence of ZnO on the carbon support. The Raman spectra of AC-ZnO (Figure 2) exhibit a sharp peak at 437 cm^-1 corresponding to the ZnO structure attributed to the high-frequency E2 vibration mode of the Wurtzite phase [45, 46].

3.3. N₂ Sorption Analysis

The nitrogen isotherm of the AC-ZnO material prepared is depicted in Figure 3(a). According to the IUPAC classification, the isotherm possesses a combination of type I and type II, indicating the presence of both micropores and mesopores in the material [47]. Figure 3(b) illustrates the pore size distribution of the AC-ZnO material. The catalyst exhibits hierarchical set pores with one set of pores predominantly centered near the 13 Å region and a broad set of pores in the 50 to 125 Å region. The total pore volume was calculated to be 0.12 cm³/g. The specific surface area of the material was found to 392 m²/g. It is interesting to note that the pore volume obtained was found to be lower than that of pure activated carbon (AC) 0.22 cm³/g. This may be due to the formation of the ZnO nanoparticles encapsulated within the pores.

(a)

(b)

3.4. UV-Visible Diffuse Reflectance Spectroscopy (DRS)

The band gap of the AC-ZnO was determined from the Tauc plot (Figure 4(a)), which is a transformation of the absorption spectra through the Kubelka-Munk function vs. the energy plot (Figure 4(b)). The catalyst synthesized exhibits a significant absorption below 400 nm, which is attributed to electron transitions from the valence band to the conduction band of ZnO [48]. The band gap energy was calculated to be 3.75 eV by extrapolating the steep portion of the plot in Figure 4(b) to the -axis. The measured optical band gap value is close to the band gap of intrinsic ZnO powder and is in good agreement with the literature reports [49–52].

(a)

(b)

3.5. Zeta Potential Measurements

The change in zeta potential () as a function of pH is illustrated in Figure 5. The isoelectric point (IEP) of AC-ZnO was found to be at a pH of around 6.8. These results suggest that the surface of the AC-ZnO material is negatively charged at pH values of above 6.8, whereas the surface possesses a positive charge below the pH of 6.8.

3.6. Thermogravimetric Analysis (TGA)

Thermal stability of the synthesized catalyst, AC-ZnO, was studied by using TGA analysis. The catalyst was found to be stable, and around 2% of weight loss was recorded up to the temperature of 450°C (Figure 6), and it can be clearly seen that the impregnation decreases the carbon content and thus causes the decrease in the weight loss.

In addition, the total weight loss of this ZnO-loaded catalyst was found to be less than that of pure activated carbon (AC) as illustrated in Figure S2 (3.2%). This low weight loss further indicates the stability of the catalyst against temperature.

3.7. Scanning Electron Microscopic Analysis (SEM)

SEM studies confirm the loading of ZnO on the activated carbon support, and Figure 7 illustrates the SEM image of the ZnO-loaded materials. It can be seen that the activated sample is in an irregular pattern with fine pores. In addition, ZnO particulates are deposited on the surface and in the pores of the activated carbon. A closer observation indicates the flake-like ZnO structure on the surface of activated carbon.

3.8. Fourier Transform Infrared Spectroscopic Analysis (FT-IR)

FT-IR studies of AC-ZnO (Figure S3) indicated that the band at around 3470 cm⁻¹ is due to the O-H stretching vibration mode of hydroxyl functional groups [39]. The stretching at a wave number of 2920 cm^-1 is due to the C-H stretching, while the band visible near 2360 cm⁻¹ corresponds to the C–O stretching vibration of the carbon monoxide or carbon dioxide derivatives. The stretching vibration band at around 1700 cm⁻¹ is assigned to the carbonyl C=O group, and the band at 1600 cm^-1 is attributed to the character of C=C. The peak at around 1500 cm^-1 is assigned to aromatic skeletal vibration. The bands between 900 and 1300 cm^-1 can be attributed to the C-OH groups. The peaks appearing between 450 and 630 cm^-1 are assigned to the Zn-oxygen (Zn–O) stretching mode [53, 54].

3.9. Photocatalytic Degradation of Ethyl Violet (EV)

The suspension made with 25 mg of the catalyst, AC-ZnO, and 50 mL of 20 ppm dye solution was first stirred for 30 min. in the dark, to attain an adsorption-desorption equilibrium. It was found that the adsorption-desorption equilibrium is attained within 30 min. The amount of Ethyl Violet adsorbed after 120 min. was calculated to be mg/g. Then the reactor was illuminated. Similar experiments were done without the catalyst for comparison purposes. Only discolouration was observed with the dye solution when the photolysis was performed without the catalyst, whereas the degradation occurred (the degradation profile is illustrated in Figure S4) when the catalyst was used. Figure 8 illustrates the relative concentration () of the remnant dye solution against irradiation time.

It can be seen that a reasonable adsorption was attained in the dark and the concentration reached zero (complete degradation) after 60 min. of irradiation in the presence of a catalyst with the rate constant of ^-1. The solution without a catalyst reached an equilibrium after 120 min. of irradiation, and the rate constant of the direct photolysis was found to 0.0058 min^-1. These observations clearly indicate the effectiveness of the photocatalyst.

In a reported work, Chen studied the degradation of Ethyl Violet (EV) dye using a ZnO nanoparticle (0.5 g/L) under UV illumination (365 nm). The initial concentration of the dye chosen for their study was 50 mg/L, and it was found that 99.9% of EV was removed after 5 h irradiation [1]. In another study, Chen with his coworkers examined the degradation of EV dye using TiO₂ suspension under visible light irradiation.

Photocatalytic degradation of EV dye mediated by TiO₂ under anaerobic condition was reported by Lee and Chen, where they mainly focused on the degraded products and the cleavage mechanism.

In another study, Wang et al. used a TiO₂ catalyst doped with an upconversion luminescence agent for the degradation of EV (initial concentration of 10 mg/L), and they found that the degradation rate of Ethyl Violet in the presence of a doped rutile TiO₂ photocatalyst reached 87.08% under 4 h of visible light irradiation, and it was observed that the rate of degradation was found to be higher than that of the undoped TiO₂ material (35.42%) [55]. In comparison to all these reported works, it can be clearly stated that our material is more effective, since it can completely degrade the dye in 60 min. of irradiation.

Band gap excitation of AC-ZnO results in the promotion of electrons from the valence band to the conduction band edge. These electrons can readily react with oxygen molecules to produce reactive oxygen species (ROS), such as O₂^●¯, ^●OOH, and ^●OH [56]. These ROS then attack the dye molecule and destroy its auxochromic groups leading to destruction of the ring structure. Equation (1) describes the photocatalytic degradation process involving EV.

Although discolouration was observed during the photocatalysis process, it is not an indication of the complete removal of the dye from the aqueous solution. However, a shift in the prominent absorption band at of 596 nm indicates the cleavage of the auxochromic group of the EV dye molecule [57, 58]. The decrease in the organic contents during the degradation process was further confirmed by TOC studies. Figure 9 represents the total organic contents after photocatalytic degradation of EV in comparison to the TOC of original dye solution used in this study. It can be seen that the total organic carbon content present in the EV solution decreases during the degradation and a 63% decrease in concentration of EV dye was attained after 120 min. of degradation. These results indicate that although the remnant solution became colourless after degradation, there are some organic residues existing in the resultant solution, which may be the by-products formed during degradation.

3.10. Photocatalysis in the Presence of Scavenging Agents

In order to understand the role of ROS and identify the most prominent ROS species, photocatalytic experiments were carried out in the presence of scavenging agents. The impact of the different scavenging agents on the dye removal efficiencies was investigated with the catalyst prepared. To investigate the role of oxygen (O₂), N₂ flow was used to degasify the suspension throughout the study and isopropyl alcohol (IPA) was used as the ^●OH trapping agent in the degradation process of EV dye to provide more insight about the role of ^●OH radical. The obtained results for the two scavenging agents are represented in Figure 10(a), and the values obtained for the apparent rate constant, (min^-1), are 0.014 and 0.010.

(a)

(b)

From the results, we can conclude that the rate of the reaction is very low, when these scavenging agents are used. Thus, the presence of dissolved oxygen plays an important role in degrading the dye molecules by providing the reactive oxygen species, such as superoxide radicals and hydroxyl radicals. Also, the results showed that the degradations obey pseudo-first-order kinetics with the values of 0.986 (under N₂ flow) and 0.997 (with IPA) and the apparent rate constant () was calculated from the plot of vs. time (Figure 10(b)).

3.11. Photoluminescence (PL) Spectroscopic Studies

It is known that hydroxyl radicals play an important role in the degradation of organic pollutants. To shed more light on this, ^●OH trapping experiments were carried out. These radicals can react with terephthalic acid (TPA) and form fluorescent 2-hydroxyterephthalic acid (2-HTPA), and the formation of 2-HTPA is proportional to the amount of ^●OH formed. Figure 11 illustrates a plot of fluorescence intensity for 2-HTPA at different times for the catalyst used in this study.

It can be seen from Figure 11 that the maximum photoluminescence (PL) intensity of (a.u.) was recorded after 40 min. of irradiation. This means that the generation of the ^•OH radicals by this system reaches its maximum at 40 min., and then the rate of formation started to decrease. This phenomenon is reflected in the rate of degradation of EV, where a fast degradation is attained until 40 min. of time and the rate of degradation is found to be slow after 40 min. (Figure 10(a)) of the degradation time. It is noteworthy to mention that 2-HTPA which is formed during the process can be further degraded by •OH. Since the trapping agent can itself be degraded, the formation of •OH radical seems to decrease after 40 min.

3.12. ESI-MS Analysis

The intermediates formed during the degradation of EV dye was evaluated from the ESI-MS analysis, and the structures of molecular fragments detected by mass spectrometry are summarized in Schemes 1–3. The mass spectrum of pure EV dye solution shows two major peaks at and 428 under our experimental conditions. The disappearance of the parent peak () was achieved after 120 min. of degradation. In addition, a decrease in the intensity (counts) of this major peak with time and formation of several other peaks at lower values further validate the degradation of the EV dye molecule in the presence of the catalyst, AC-ZnO, (Figure S5). On the basis of these results, a general mechanism of photocatalytic degradation of EV dye is proposed. The mechanism consists of several steps that include (i) N-de-ethylation, (ii) destruction of the conjugated structure, and (iii) oxidative degradation. The primary cleavage of the EV dye results in the formation of peaks with , 400, and 372, which are mainly due to the addition of ^●OH radical and the subsequent removal of water and acetaldehyde molecules, respectively, as indicated in Scheme 1.

The cleavage of the ring structure from the original molecule () leads to the secondary degraded products with the values of 325, 297, 269, and 241. This may be due to the addition of ^●OH radicals and the removal of water and acetaldehyde molecules as illustrated in Scheme 2. Further cleavage of these degraded molecules results in the formation of secondary products with values of 341, 313, and 285. The small fragmented products, i.e., tertiary products, detected in this study at values of 95 and 74 are phenol and diethylamine, respectively, as illustrated in Scheme 3.

4. Conclusions

A sustainable and versatile photocatalyst, AC-ZnO, was prepared by a facile method using Algerian olive-waste cakes as raw material for activated carbon. Impregnation method was utilized to load ZnO on the activated carbon support. Degradation of the Ethyl Violet (EV) dye was evaluated with the prepared catalyst AC-ZnO, and the kinetic study suggests that the rate of the degradation obeys pseudo-first-order kinetics. The intermediate products formed during the photocatalytic degradation of EV were identified by using ESI-MS analysis, and a degradation mechanism was proposed. The total organic contents (TOC) were found to decrease after 120 min. of degradation. Further, the scavenging experiments indicate that dissolved oxygen is important to achieve faster and effective degradation, since this dissolved oxygen leads to the formation of reactive oxygen species, such as superoxide and hydroxyl radicals. Overall, this study exemplifies the usage of the Algerian olive waste for the preparation of activated carbon and, thus, provides opportunity to reduce these wastes, as well as reduce the cost for importing activated carbon to countries like Algeria. Further, modifying this activated carbon material using active oxide materials, such as TiO₂ and ZnO, will open up the opportunity to introduce cheaper catalysts to the market for environmental remediation applications.

Data Availability

The data sets obtained during the research and the analysis are already available in the article and the supplementary document. However, if there are any information/data that are needed, these may be obtained from the corresponding author on a reasonable request.

Conflicts of Interest

The authors declare that there is no conflict of interest regarding the publication of this paper.

Acknowledgments

Authors would like to acknowledge the National Science Foundation (CHE-1337707) for the financial support in purchasing the SEM instrument and Dr. Aravind Baride, who assisted with the SEM analysis.

Supplementary Materials

Supplementary 1. Scheme S1: different steps involved in the preparation of the catalyst, AC-ZnO. Table S1: optimal instrumental conditions for ESI-MS studies. Figure S1: powder X-ray diffraction patterns of blank activated carbon (AC). Figure S2: TGA of blank activated carbon (AC). Figure S3: FT-IR spectrum of AC-ZnO. Figure S4: absorption spectra of EV dye (after filtration) at various time intervals during UV light irradiation for 120 min. using AC-ZnO. Figure S5: mass spectrum (MS) of the by-products generated during the degradation of Ethyl Violet by the system (AC-ZnO/UV) at different times.

Supplementary 2. Graphical Abstract: the first two pictures of the graphical abstract explain how the oil waste was collected from the site and the activated charcoal preparation process. Then the scheme illustrates the ZnO-loaded activated carbon; the next photograph taken during the degradation process indicates the irradiation source and the photoreactor setup. The final photograph illustrates the dye solution withdrawn in different time intervals. Disappearance of the colour indicates the degradation of the dye material.

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Copyright © 2019 Ala Abdessemed 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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International Journal of Photoenergy

Impregnation of ZnO onto a Vegetal Activated Carbon from Algerian Olive Waste: A Sustainable Photocatalyst for Degradation of Ethyl Violet Dye

Abstract

1. Introduction

2. Materials and Methods

2.1. Materials

2.2. Synthesis of the AC-ZnO Material

2.3. Characterization

2.4. Photocatalysis Experiments

2.5. Analytical Techniques

3. Results and Discussion

3.1. Powder XRD

3.2. Raman Spectra

3.3. N2 Sorption Analysis

3.4. UV-Visible Diffuse Reflectance Spectroscopy (DRS)

3.5. Zeta Potential Measurements

3.6. Thermogravimetric Analysis (TGA)

3.7. Scanning Electron Microscopic Analysis (SEM)

3.8. Fourier Transform Infrared Spectroscopic Analysis (FT-IR)

3.9. Photocatalytic Degradation of Ethyl Violet (EV)

3.10. Photocatalysis in the Presence of Scavenging Agents

3.11. Photoluminescence (PL) Spectroscopic Studies

3.12. ESI-MS Analysis

4. Conclusions

Data Availability

Conflicts of Interest

Acknowledgments

Supplementary Materials

References

Copyright

3.3. N₂ Sorption Analysis