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Article

A Novel N-Doped Nanoporous Bio-Graphene Synthesized from Pistacia lentiscus Gum and Its Nanocomposite with WO3 Nanoparticles: Visible-Light-Driven Photocatalytic Activity

by
Maryam Afsharpour
*,
Mehdi Elyasi
and
Hamedreza Javadian
Chemistry & Chemical Engineering Research Center of Iran (CCERCI), Tehran P.O. Box 14335-186, Iran
*
Author to whom correspondence should be addressed.
Molecules 2021, 26(21), 6569; https://doi.org/10.3390/molecules26216569
Submission received: 5 October 2021 / Revised: 23 October 2021 / Accepted: 27 October 2021 / Published: 29 October 2021
(This article belongs to the Special Issue Application of Nanocomposites in Wastewater Treatment)
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Abstract

:
This paper reports the synthesis of a new nitrogen-doped porous bio-graphene (NPBG) with a specific biomorphic structure, using Pistacia lentiscus as a natural carbon source containing nitrogen that also acts as a bio-template. The obtained NPBG demonstrated the unique feature of doped nitrogen with a 3D nanoporous structure. Next, a WO3/N-doped porous bio-graphene nanocomposite (WO3/NPBG-NC) was synthesized, and the products were characterized using XPS, SEM, TEM, FT-IR, EDX, XRD, and Raman analyses. The presence of nitrogen doped in the structure of the bio-graphene (BG) was confirmed to be pyridinic-N and pyrrolic-N with N1 peaks at 398.3 eV and 400.5 eV, respectively. The photocatalytic degradation of the anionic azo dyes and drugs was investigated, and the results indicated that the obtained NPBG with a high surface area (151.98 m2/g), unique electronic properties, and modified surface improved the adsorption and photocatalytic properties in combination with WO3 nanoparticles (WO3-NPs) as an effective visible-light-driven photocatalyst. The synthesized WO3/NPBG-NC with a surface area of 226.92 m2/g displayed lower bandgap and higher electron transfer compared with blank WO3-NPs, leading to an increase in the photocatalytic performance through the enhancement of the separation of charge and a reduction in the recombination rate. At the optimum conditions of 0.015 g of the nanocomposite, a contact time of 15 min, and 100 mg/L of dyes, the removal percentages were 100%, 99.8%, and 98% for methyl red (MR), Congo red (CR), and methyl orange (MO), respectively. In the case of the drugs, 99% and 87% of tetracycline and acetaminophen, respectively, at a concentration of 10 mg/L, were removed after 20 min.

1. Introduction

The environmental impact of industrial wastewaters is a serious concern all around the world [1,2,3,4]. The contaminants circulating in wastewaters are frequently complicated and non-biodegradable, which requires treatment using special removal methods. Different technologies, such as chemical coagulation, adsorption, filtration, reverse osmosis, and catalytic or photocatalytic treatment have been used to remove chemical contaminants [5,6,7,8,9,10,11,12]. In recent years, advanced oxidation processes (AOPs) utilizing catalysts have been applied as efficient methods to eliminate organic pollutants by degrading them into harmless substances via electron-hole generation under light irradiation or in the presence of oxidants [10,11,12,13,14,15,16,17,18,19].
Metal oxides, such as titanium dioxide, zinc oxide, and tungsten oxide, as well as some metal-free compounds, such as g-C3N4 and SiC, are semiconductors with interesting advantages in removing pollutants via AOPs [20,21,22,23,24,25,26]. Among the photocatalysts used in AOPs, the attractive properties of tungsten oxide have been demonstrated by researchers [27,28,29].
Doping and combining metal oxides with other semiconductors can improve photocatalytic activity by increasing the separation of charge and lowering the recombination rate. Graphene is of significant interest in photocatalytic applications because its excellent electronic properties, high conductivity, and high surface area can increase the transfer of electrons and strengthen photocatalytic capabilities [30,31,32].
In this study, a novel N-doped nanoporous bio-graphene (NPBG) synthesized using Pistacia lentiscus as a natural source was used as a substrate to synthesize tungsten oxide nanocomposite as a visible-light-driven semiconductor. Because of its delocalized electrons, which cause the charge transfer, NPBG was chosen to prevent the recombination of produced electrons in the WO3 photocatalyst. To characterize the obtained products, XPS, SEM, TEM, FT-IR, EDX, XRD, and Raman were applied. The synthesized nanocomposite was applied for the photocatalytic degradation of the anionic azo dyes and drugs, and the optimum conditions for maximum removal were obtained.

2. Materials and Methods

2.1. Materials

Pistacia lentiscus was used as a natural carbon source containing nitrogen for the synthesis of the NBG. Tungstic acid and hydrogen peroxide (30%) purchased from Merck (Darmstadt, Germany) were used to synthesis the nanocomposite for the photocatalytic degradation process. The azo dyes, including CR (C.I. Direct Red 28), MO (C.I. Acid Orange 52), and MR (C.I. Acid Red 2), and acetaminophen and tetracycline were selected as model drugs to test the photocatalytic activity of the synthesized nanocomposite.

2.2. Characterization

The XPS analysis was performed using an ESCALAB 250Xi Thermo Scientific System (Waltham, MA, USA) (MgKα = 1253.6 eV). SEM images were obtained using a TESCAN, VEGA3 microscope (Brno, Czech Republic) equipped with an X-ray energy dispersive spectroscope (EDX). The specific surface area and pore size distribution of the samples were evaluated by means of the BELSORP Mini Instrument (Microtrac MRB, York, PA, USA). Fourier-transform infrared (FT-IR) spectra were recorded by Bruker Vector 33 spectrometer (Leipzig, Germany), and Raman spectra of the samples were obtained using Bruker Senterra micro-Raman (Leipzig, Germany) at 785 nm laser wavelength. The XRD (X-ray diffraction) patterns were recorded with Bruker AXS (Leipzig, Germany) using CuKα radiation with λ = 1.54060 Å. The total organic carbon (TOC) was obtained by a TOC analyzer (Multi N/C 3100, Jena, Germany)

2.3. Synthesis of NBG (N-Doped Bio-Graphene) and NPBG (N-Doped Porous Bio-Graphene)

The NBG was synthesized using a natural precursor to obtain the N-doped biomorphic structure. First, Pistacia lentiscus gum was ground to obtain a soft powder. Next, the black powder of NBG with a special morphology of graphenic layers was obtained through the carbonization of the soft powder at 700 °C for 1 h in an N2 atmosphere with a heating rate of 5 °C/min. As surface area is one of the main parameters in catalytic performance, the porosity of the synthesized NBG was increased through KOH activation. For this purpose, 20 g of KOH was dissolved in 100 mL of distilled water. Next, 10 g of synthesized NBG was added to this solution, and the mixture was stirred at 50 °C for 4 h. The obtained product was dried at 80 °C and then treated at 700 °C for 1 h in an N2 atmosphere (5 °C/min).

2.4. Synthesis of WO3/NPBG-NC (WO3/N-Dope Porous Bio-Graphene Nanocomposite)

For the synthesis of WO3/NPBG-NC, oxodiperoxo tungsten complex (WO(O2)2) was used as the tungsten precursor. To prepare the tungsten complex, 10 mmol (2.5 g) of tungstic acid was dissolved in 20 mL of H2O2 (30%) at 40 °C for 48 h. Next, 1 g of synthesized NPBG was added to the solution and stirred at 80 °C for 24 h to stabilize the WO3-NPS on the surface of NPBG. The obtained nanocomposite was filtered, washed several times with distilled water, and finally calcined at 600 °C for 1 h. Since increasing the amount of active site (WO3-NPs) in the composite increases the photocatalytic activity, the maximum amount of WO3-NPs was stabilized on the surface of NPBG using this method.
To compare the bandgap of WO3/NPBG-NC with WO3-NPs, WO3-NPS were synthesized via the same precursor. The peroxo-tungsten solution (WO(O2)2) was treated at 80 °C under ultrasonic conditions to prevent the agglomeration of the particles. The obtained powder was calcined at 600 °C for 1 h.

2.5. Photocatalytic Degradation Method

The photocatalytic activity of the synthesized nanocomposite was evaluated through the degradation of three dyes (CR, MO, and MR) and two drugs (acetaminophen and tetracycline) under visible-light irradiation. The optimal conditions of the photocatalytic system were obtained by investigating the effect of the initial concentration of dyes (100, 200, and 300 mg/L) and the amount of the nanocomposite (0.01, 0.015, and 0.02 g) at room temperature (25 °C). Before irradiation, the adsorption percentage of the analytes was measured in dark conditions. Next, a certain amount of synthesized photocatalyst was dispersed in 10 mL of pollutants solution under stirring (120 rpm) at visible light irradiation. The photocatalytic experiments were carried out in a glass reactor under air bubbling to saturate the solution with oxygen during the reaction. A Xenon lamp (Autotech H7, Guangzhou, China) was used as a visible light source with a light flux of 30 W/cm2. The samples were collected every 10 min from the reaction mixture to determine the concentrations of the pollutants. After centrifugation and filtration of the photocatalyst, the samples were analyzed using a UV-Vis spectrophotometer (Perkin-Elmer Lambda 35) (Seer Green, UK) at 497 nm, 464 nm, 425 nm, 246 nm, and 357 nm to measure the concentrations of CR, MO, MR, acetaminophen, and tetracycline, respectively.
The removal percentage of the pollutant was measured using the following equation:
Removal   % = [ ( C 0 − C t ) C 0 ] ∗ 100 %
where C0 and Ct are the initial and equilibrium concentrations of the pollutants, respectively.
To investigate the degradation mechanism, quenching tests were performed using 2 mM of isopropanol (IPA), 1,4-benzoquinone (BQ), ammonium oxalate (AO) as the hydroxyl radical (•OH), superoxide radical anions (•O2−), and hole (h+) scavenger, respectively.
The reusability of a photocatalyst is considered an important parameter in practical applications. Therefore, it was studied by performing five cycles after centrifuging and washing the photocatalyst with distilled water and drying at 80 °C.

3. Results and Discussion

3.1. Characterization

Figure 1 presents the XPS analysis of the synthesized NPBG. The XPS spectra present the photoemission peaks of C1s, O1s, and N1s, indicating the presence of nitrogen atoms doped in the graphene structure, originating from the natural gum. As shown in Figure 1d, the spectrum of N1s is deconvoluted into two peaks at 398.3 eV and 400.5 eV, indicating pyridinic-N and pyrrolic-N species in the structure of NPBG. The spectrum of C1s presents three peaks at 284.5 eV, 285.5 eV, and 287.4 eV, corresponding to C-C, C-O/C-N, and C=O bonds, respectively. As for the spectrum of O1s, it displays O-C, O=C, and O-C=O bonds at 531.3 eV, 532.9 eV, and 533.8 eV, respectively. The XPS results also demonstrate the amount of elements to be 75.87, 21.42, and 2.71 At% for C, O, and N, respectively.
Figure 2 presents the SEM images of synthesized NBG, NPBG, and WO3/NPBG-NC. Figure 2a,b present the SEM images of synthesized NBG that display the packed layers. Figure 2c,d display the morphology of NPBG that indicates the separated layers of graphene. This special morphology of graphenic layers originates in natural Pistacia lentiscus gum. In the SEM images of the WO3/NPBG-NC shown in Figure 2e,f as well as its TEM image (Figure 2g), WO3-NPs can be clearly observed on the surface of the graphenic layers.
Figure 3 presents the EDX spectra of the NPBG and WO3/NPBG-NC and their elemental amounts, confirming the presence of 2.51% of N doped in the synthesized NPBG and 16.09% of tungsten in the nanocomposite. These percentages are close to those obtained bythe XPS analysis (Figure 1).
The values of porosity obtained for the synthesized NBG, NPBG, and WO3/NPBG-NC are reported in Figure 4 and Table 1. The results show that the surface area of the NBG increased from 38.98 m2/g to 151.98 m2/g after the activation process with KOH. This increase can also be observed in the SEM images. As shown in Table 1, the surface area of the WO3/NPBG-NC (226.92 m2/g) is higher than that of the NPBG due to the immobilization of the WO3-NPs on the surface of the NPBG. The values of average pore diameter are 1.77 nm and 6.68 nm, respectively, for the NPBG and WO3/NPBG-NC, indicating the microporous structure of the NPBG and the mesoporous structure of the nanocomposite.
Figure 5 presents the FT-IR spectra of the synthesized NPBG and WO3/NPBG-NC. The absorption peaks at around 1096 cm−1, 1643 cm−1, and 1720 cm−1 indicate the stretching vibrations of the C-O, C=C, and C=O groups, respectively. The weak peak at around 1430 cm−1 represents the C-N stretching vibration, which confirms nitrogen doping in this structure of the sample. The symmetric and asymmetric vibrations of C-H were observed at around 2850 cm−1 and 2928 cm−1. In addition, the wide peak at around 3425 cm−1 corresponds to the O-H and N-H vibrations. In the spectrum of the WO3/NPBG-NC, the new peak that was detected at 842 cm−1 was associated with W=O vibration on the tungsten oxide, which confirmed the successful synthesis of the nanocomposite.
The XRD patterns of the synthesized NPBG and WO3/NPBG-NC are depicted in Figure 6. The XRD pattern of the NPBG displays two diffraction peaks at 2θ = 25.6° and 43.2° that were assigned to the (002) and (100) planes of the carbon phase in the NPBG, respectively. In comparison with the undoped graphene, the major peak is weaker and observed at a higher 2θ (25.6° (doped) vs. 22.3° (undoped)) [33]. The XRD pattern of WO3/NPBG-NC displays the appearance of diffraction peaks at 2θ = 16.6°, 27.5°, 32.3°, 43.1°, 48.8°, 51.0°, 56.7°, 59.0°, and 64.2°, which were assigned to (020), (111), (200), (122), (202), (222), (232), (331), and (351) planes of the orthorhombic WO3.H2O (JCPDS 84-0886).
The Raman spectra of the synthesized NPBG and WO3/NPBG-NC are presented in Figure 7. In both samples, two specific peaks of graphene are displayed at around 1330 cm−1 and 1580 cm−1, which are related to D and G bonds, respectively. In the WO3/NPBG-NC, these peaks display a slight shift to higher frequencies, and the new peaks at around 710 cm−1 and 805 cm−1 confirm the presence of tungsten oxide in the nanocomposite [34].
Figure 8 presents the bandgaps of the WO3/NPBG-NC and tungsten oxide calculated from the UV-Vis drift reflectance spectra using the Tauc plot. The results reveal a decrease in bandgap from 2.85 eV to 2.20 eV, owing to the composition of the tungsten oxide with the NPBG.
The valence band (EVB) and conduction band (ECB) edge potentials can be calculated by the following equations [35]:
EVB = χ − Ee + 0.5Eg
ECB = EVB − Eg
where χ is the electronegativity and Eg is the bandgap energy of the semiconductor. Ee is the energy of free electrons vs. the hydrogen scale (4.5 eV). The values of χ calculated for the WO3-NPs and the WO3/NPBG-NC were 6.59 eV and 6.39 eV, respectively [36]. The EVB and ECB values for the WO3-NPs were 3.51 eV and 0.66 eV, respectively, while, according to these equations, the EVB and ECB for the WO3/NPBG-NC were 2.99 eV and 0.70 eV, respectively.

3.2. Photocatalytic Study

The photocatalytic activities of the synthesized NBG, NPBG, and WO3/NPBG-NC are displayed in Figure 9. The adsorption of CR on the surface of the synthesized materials was recorded in dark conditions, and the results in Figure 9 (dash lines) display the removal of the dye, even in dark conditions, using all the compounds. Graphene is an effective adsorbent due to its high surface area and unique electronic properties [37,38,39,40]. The electrostatic forces and π–π stacking in the graphene structure could be responsible for enhancing the adsorption capacity [40,41,42,43,44]. In addition, the oxygenated functional groups could be effective at potential adsorption [45]. Furthermore, heteroatom-doped graphene shows an improved adsorption performance due to the surface modification [46,47]. As displayed in Figure 9, the synthesized NBG demonstrated 44.1% dye removal in dark conditions, while the NPBG exhibited a higher removal percentage of dye (60.2%) due to its higher surface area. The WO3/NPBG-NC demonstrated higher adsorption capacity than the NBG support, which was due to the higher surface area and different surface charges of the nanocomposite.
According to other studies [33,48], the difference in the electronegativity of C and N atoms in the structure of NBG causes a positive charge in C atoms. These positively charged C atoms in the structure of NBG can adsorb O2 and produce reactive oxygenated radical species that can decompose the dye, even in dark conditions [48].
In WO3/NPBG-NC, the immobilization of WO3-NPs on the surface of NBG can also change the surface charge, which increases the surface adsorption via the terminal oxygen of WO3-NPs. It causes a change in the value of pHzpc from 8.24 for NPBG to 7.1 for WO3/NPBG-NC.
Figure 9 also displays the photocatalytic performances of synthesized NBG, NPBG, and WO3/NPBG-NC. As can be seen, light irradiation can activate the catalyst and enhance the dye removal via the photocatalytic mechanism [20]. The TOC removal of CR solution was also studied under dark and light irradiation conditions (Figure 10). The WO3/NPBG-NC demonstrated 99.8% decoloration and 96% reduction in carbon content under light irradiation. The TOC removal of the dye solution was near to the decoloration, indicating the complete degradation of the dye under light irradiation. The results of the decoloration and TOC removal in the dark revealed 58.5% and 31% dye removal, respectively. These results confirm a the presence of a degradation mechanism in addition to the adsorption described above.
To justify the observed results after the light irradiation, first, the photocatalytic mechanism of WO3/NPBG-NC was evaluated.
Figure 11 represents the schematic of the proposed photocatalytic mechanisms of the WO3-NPs and the WO3/NPBG-NC. Under visible light irradiation, the electron-hole pairs in the WO3-NPs were generated by the transfer of the generated electrons from the valance bond (VB) to the conduction bond (CB) of the photocatalyst. Next, the excited electrons on the CB were scavenged by NPBG, which that reduced the recombination rate of the electron-hole pairs. The electrons reacted with oxygen to form superoxide radicals, and •OH radical formation took place through reacting holes with H2O. The generation of the oxygenated radicals decomposed the organic pollutants into harmless products.
Tungsten oxide is a visible-light-driven semiconductor that exhibits low photocatalytic activity due to its poor charge separation efficacy. Thus, the composition of WO3-NPs with NPBG can enhance its photocatalytic properties due to its delocalized electrons, which lead to the charge transfer and prevent the recombination of the generated electrons in the photocatalyst [49,50,51]. NPBG can reduce the bandgap by forming a new valence band and enhancing the charge separation efficiency. It acts as an electron scavenger to accept electrons from WO3-NPs, which consequently decreases the electron–hole pair recombination rate. Thus, higher photocatalytic performance is observed with WO3/NPBG-NC (Figure 9).
The active oxygenated radical species involved in this photocatalytic process was identified by the quenching experiments. The results in Figure 12 show the decrease of photodegradation of CR from 99.8% to 42.1%, 73.3%, and 52.3% in the presence of IPA, AO, and BQ as •OH, h+, and •O2− scavenger, respectively, indicating that •OH was the main active radical in the photocatalytic degradation of the dye using WO3/NPBG-NC.
The optimization of photocatalytic reaction conditions for the degradation of CR in visible light is shown in Figure 13 and Figure 14. To investigate the effect of the amount of photocatalyst on the catalytic activity of WO3/NPBG-NC, the degradation of CR was evaluated using different amounts of the nanocomposite (Figure 13). The results demonstrate an increase in dye removal due to increase in the amount of the nanocomposite. Actually, an increase in the photocatalytic active sites occurs, consequently, the oxygenated radicals increase and the degradation process is performed effectively. The optimum amount of the nanocomposite for the maximum removal of the dye was 0.015 g, and a further increase in the amount of the nanocomposite had an effect on the reaction rate (Figure 13).
Figure 14 demonstrates the effect of the dye concentration on the photocatalytic performance of the WO3/NPBG-NC. The results in Figure 14 demonstrate that the degradation of the dye decreased along with any increase in the concentration of the dye. The reduction in dye removal at the concentration of 300 ppm can be attributed to the saturation of the catalyst surface with the dye molecules, which caused a decrease in photocatalytic performance.
To investigate the photocatalytic performance of the WO3/NPBG-NC for the degradation of different organic pollutants, the removal of different dyes and drugs was tested (Figure 15 and Figure 16). As demonstrated in Figure 15, the WO3/NPBG-NC removed 100%, 99.8%, and 98% of the MR, CR, and MO after 15 min, respectively, which indicates the favorable photocatalytic properties of the synthesized nanocomposite for the degradation of the tested azo dyes.
The photodegradation results of the acetaminophen and tetracycline under visible light are displayed in Figure 16. Around 99% and 87% of the tetracycline and acetaminophen, respectively, were removed after 20 min, confirming the suitability of the nanocomposite for the removal of drugs from aqueous media.
The stability and reusability of a catalyst is an important parameter in designing a suitable catalytic degradation process. Figure 17 displays the cycles of using WO3/NPBG-NC for the degradation of CR. As shown in Figure 17, only a slight decrease in the photodegradation of the dye was observed after five cycles, indicating the good reusability of the synthesized nanocomposite in the photocatalytic process.

4. Conclusions

In this study, WO3/NPBG-NC with an excellent photocatalytic activity was synthesized using WO3-NPs and a novel NPBG synthesized from Pistacia lentiscus as a natural source. Tungsten oxide is a visible-light-driven semiconductor that exhibits low photocatalytic performance due to its poor charge separation efficacy. The composition of WO3-NPs with synthesized NPBG enhanced the photocatalytic activity. The bandgap of the WO3-NPs was 2.85 eV, while its value for the WO3/NPBG-NC was 2.20 eV. As compared with blank WO3, a significant increase in photocatalytic activity was observed using WO3/NPBG-NC for the degradation of MR, CR, MO, tetracycline, and acetaminophen, with removal percentage values of 100%, 99.8%, 98%, 99%, and 87%, respectively. The enhancement was due to the fact that the combination of WO3 with NPBG improved the photocatalytic property by decreasing the electron–hole recombination rate. The results of the reusability studies revealed that after using WO3/NPBG-NC in five cycles, the change in the removal percentage of the dye was negligible, confirming that it can be used as a reusable nanocomposite for the successful degradation of dyes and drugs from aqueous media.

Author Contributions

Conceptualization, M.A.; methodology, M.A. and M.E.; investigation, M.A., M.E. and H.J.; writing—original draft preparation, M.A.; writing—review and editing, M.A. and H.J.; supervision, M.A. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data are contained within the article.

Acknowledgments

The support for this work by the Chemistry & Chemical Engineering Research Center of Iran is gratefully acknowledged.

Conflicts of Interest

The authors declare no conflict of interest.

Sample Availability

Samples of the compounds 1–3 are available from the authors.

References

  1. Ranade, V.V.; Bhandari, V.M. Industrial Wastewater Treatment, Recycling and Reuse; Butterworth-Heinemann: Oxford, UK, 2014. [Google Scholar]
  2. Yaseen, D.A.; Scholz, M. Textile dye wastewater characteristics and constituents of synthetic effluents: A critical review. Int. J. Environ. Sci. Technol. 2019, 16, 1193–1226. [Google Scholar] [CrossRef] [Green Version]
  3. Pattnaik, P.; Dangayach, G.S.; Bhardwaj, A.K. A review on the sustainability of textile industries wastewater with and without treatment methodologies. Rev. Environ. Health 2018, 33, 163–203. [Google Scholar] [CrossRef] [PubMed]
  4. Muralikrishna, I.V.; Manickam, V. Industrial Wastewater Treatment Technologies, Recycling, and Reuse. In Environmental Management; Elsevier: London, UK, 2017; pp. 295–336. [Google Scholar]
  5. Teh, C.Y.; Budiman, P.M.; Shak, K.P.Y.; Wu, T.Y. Recent Advancement of Coagulation–Flocculation and Its Application in Wastewater Treatment. Ind. Eng. Chem. Res. 2016, 55, 4363–4389. [Google Scholar] [CrossRef]
  6. Verma, S.; Daverey, A.; Sharma, A. Slow sand filtration for water and wastewater treatment—A review. Environ. Technol. Rev. 2017, 6, 47–58. [Google Scholar] [CrossRef]
  7. Hube, S.; Eskafi, M.; Hrafnkelsdóttir, K.F.; Bjarnadóttir, B.; Bjarnadóttir, M.A.; Axelsdóttir, S.; Wu, B. Direct membrane filtration for wastewater treatment and resource recovery: A review. Sci. Total Environ. 2020, 710, 136375. [Google Scholar] [CrossRef]
  8. Vourch, M.; Balannec, B.; Chaufer, B.; Dorange, G. Treatment of dairy industry wastewater by reverse osmosis for water reuse. Desalination 2008, 219, 190–202. [Google Scholar] [CrossRef]
  9. Cai, Z.; Sun, Y.; Liu, W.; Pan, F.; Sun, P.; Fu, J. An overview of nanomaterials applied for removing dyes from wastewater. Environ. Sci. Pollut. Res. 2017, 24, 15882–15904. [Google Scholar] [CrossRef]
  10. Rueda-Marquez, J.J.; Levchuk, I.; Ibanez, P.F.; Sillanpa, M. A critical review on application of photocatalysis for toxicity reduction of real wastewaters. J. Clean. Prod. 2020, 258, 120694. [Google Scholar] [CrossRef]
  11. Nidheesh, P.V.; Zhou, M.; Oturan, M. An overview on the removal of synthetic dyes from water by electrochemical advanced oxidation processes. Chemosphere 2018, 197, 210–227. [Google Scholar] [CrossRef]
  12. Hermosilla, D.; Merayo, N.; Gascó, A.; Blanco, Á. The application of advanced oxidation technologies to the treatment of effluents from pulp and paper industry: A review. Environ. Sci. Pollut. Res. 2015, 22, 168–191. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  13. Ahmed, E.A.E.; El-Sayed, B.A.; Mohamed, W.A.A.; Fahmy, A.; Helal, A. Recycling of supported nanocomposites for hazardous industrial wastewater treatment via Solar photocatalytic process. Egypt. J. Petrol. 2021, 30, 29–35. [Google Scholar] [CrossRef]
  14. Mohan, H.; Ramasamy, M.; Ramalingam, V.; Natesan, K.; Duraisamy, M.; Venkatachalam, J.; Shin, T.; Seralathan, K. Enhanced visible light-driven photocatalysis of iron-oxide/titania composite: Norfloxacin degradation mechanism and toxicity study. J. Hazard. Mater. 2021, 412, 125330. [Google Scholar] [CrossRef] [PubMed]
  15. Rodwihok, C.; Charoensr, K.; Wongratanaphisan, D.; Choi, W.M.; Hur, S.H.; Park, H.J.; Chung, J.S. Improved photocatalytic activity of surface charge functionalized ZnO nanoparticles using aniline. J. Mater. Sci. Technol. 2021, 76, 1–10. [Google Scholar] [CrossRef]
  16. Khazaee, Z.; Mahjoub, A.R.; Khavar, A.H.C. One-pot synthesis of CuBi bimetallic alloy nanosheets-supported functionalized multiwalled carbon nanotubes as efficient photocatalyst for oxidation of fluoroquinolones. Appl. Catal. B Environ. 2021, 297, 120480. [Google Scholar] [CrossRef]
  17. Tanase, M.A.; Marinescu, M.; Oancea, P.; Raducan, A.; Mihaescu, C.I.; Alexandrescu, E.; Nistor, C.L.; Jinga, L.; Ditu, L.M.; Petcu, C.; et al. Antibacterial and Photocatalytic Properties of ZnO Nanoparticles Obtained from Chemical versus Saponaria officinalis Extract-Mediated Synthesis. Molecules 2021, 26, 2072. [Google Scholar] [CrossRef] [PubMed]
  18. Bao, X.; Li, H.; Wang, Z.; Tong, F.; Liu, M.; Zheng, Z.; Wang, P.; Cheng, H.; Liu, Y.; Dai, Y.; et al. TiO2/Ti3C2 as an efficient photocatalyst for selective oxidation of benzyl alcohol to benzaldehyde. Appl. Catal. B Environ. 2021, 286, 119885. [Google Scholar] [CrossRef]
  19. Zhang, M.; Du, H.; Ji, J.; Li, F.; Lin, Y.C.; Qin, C.H.; Zhang, Z.; Shen, Y. Highly Efficient Ag3PO4/g-C3N4 Z-Scheme Photocatalyst for Its Enhanced Photocatalytic Performance in Degradation of Rhodamine B and Phenol. Molecules 2021, 26, 2062. [Google Scholar] [CrossRef]
  20. Darvishi-Farash, S.; Afsharpour, M.; Heidarian, J. Novel siligraphene/g-C3N4 composites with enhanced visible light photocatalytic degradations of dyes and drugs. Environ. Sci. Pollut. Res. 2021, 28, 5938–5952. [Google Scholar] [CrossRef] [PubMed]
  21. Kumar, K.S.; Vellaichamy, B.; Paulmony, T. Visible light active metal-free photocatalysis: N-doped graphene covalently grafted with g-C3N4 for highly robust degradation of methyl orange. Solid State Sci. 2019, 94, 99–105. [Google Scholar] [CrossRef]
  22. Wen, M.; Wang, J.; Tong, R.; Liu, D.; Huang, H.; Yu, Y.; Zhou, Z.; Chu, P.K.; Yu, X. A Low-Cost Metal-Free Photocatalyst Based on Black Phosphorus. Adv. Sci. 2019, 6, 1801321. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  23. Asadzadeh-Khaneghah, S.; Habibi-Yangjeh, A. g-C3N4/carbon dot-based nanocomposites serve as efficacious photocatalysts for environmental purification and energy generation: A review. J. Clean. Prod. 2020, 276, 124319. [Google Scholar] [CrossRef]
  24. Rosso, C.; Filippini, G.; Criado, A.; Melchionna, M.; Fornasiero, P.; Prato, M. Metal-Free Photocatalysis: Two-Dimensional Nanomaterial Connection toward Advanced Organic Synthesis. ACS Nano 2021, 15, 3621–3630. [Google Scholar] [CrossRef]
  25. Chen, L.; Huang, H.; Zheng, Y.; Sun, W.; Zhao, Y.; Francis, P.S.; Wanga, X. Noble-metal-free Ni3N/g-C3N4 photocatalysts with enhanced hydrogen production under visible light irradiation. Dalton Trans. 2018, 47, 12188–12196. [Google Scholar] [CrossRef] [PubMed]
  26. Jiang, L.; Yuan, X.; Zeng, G.; Wu, Z.; Liang, J.; Chen, X.; Leng, L.; Wang, H.; Wang, H. Metal-free efficient photocatalyst for stable visible-light photocatalytic degradation of refractory pollutant. Appl. Catal. B Environ. 2018, 221, 715–725. [Google Scholar] [CrossRef]
  27. Dutta, V.; Sharma, S.; Raizada, P.; Thakur, V.K.; Parvaz Khan, A.A.; Saini, V.; Asiri, A.M.; Singh, P. An overview on WO3 based photocatalyst for environmental remediation. J. Environ. Chem. Eng. 2021, 9, 105018. [Google Scholar] [CrossRef]
  28. Nguyen, T.T.; Nam, S.N.; Son, J.; Oh, J. Tungsten Trioxide (WO3)-assisted Photocatalytic Degradation of Amoxicillin by Simulated Solar Irradiation. Sci. Rep. 2019, 9, 9349. [Google Scholar] [CrossRef] [PubMed]
  29. Liu, X.; Zhai, H.; Wang, P.; Zhang, Q.; Wang, Z.; Liu, Y.; Dai, Y.; Huang, B.; Qin, X.; Zhang, X. Synthesis of a WO3 photocatalyst with high photocatalytic activity and stability using synergetic internal Fe3+ doping and superficial Pt loading for ethylene degradation under visible-light irradiation. Catal. Sci. Technol. 2019, 9, 652–658. [Google Scholar] [CrossRef]
  30. Salama, T.M.; Morsy, M.; Abou Shahba, R.M.; Mohamed, S.H.; Mohamed, M.M. Synthesis of Graphene Oxide Interspersed in Hexagonal WO3 Nanorods for High-Efficiency Visible-Light Driven Photocatalysis and NH3 Gas Sensing. Front. Chem. 2019, 7, 722. [Google Scholar] [CrossRef]
  31. Albero, J.; Mateo, D.; García, H. Graphene-Based Materials as Efficient Photocatalysts for Water Splitting. Molecules 2019, 24, 906. [Google Scholar] [CrossRef] [Green Version]
  32. Li, X.; Yu, X.; Wageh, S.; Al-Ghamdi, A.A.; Xie, J. Graphene in Photocatalysis: A Review. Small 2016, 28, 6640–6696. [Google Scholar] [CrossRef]
  33. Afsharpour, M.; Gomi, L.S.; Elyasi, M. Novel metal-free N-doped bio-graphenes and their MoO3 bifunctional catalysts for ultra-deep oxidative desulfurization of heavy fuel. Sep. Purif. Technol. 2021, 274, 119014. [Google Scholar] [CrossRef]
  34. Santato, C.; Odziemkowski, M.; Ulmann, M.; Augustynsk, J. Crystallographically Oriented Mesoporous WO3 Films: Synthesis, Characterization, and Applications. J. Am. Chem. Soc. 2001, 123, 10639–10649. [Google Scholar] [CrossRef]
  35. Chang, F.; Zheng, J.; Wang, X.; Xu, Q.; Deng, B.; Hu, X.; Liu, X. Heterojuncted non-metal binary composites silicon carbide/g-C3N4 with enhanced photocatalytic performance. Mater. Sci. Semicond. Process. 2018, 75, 183–192. [Google Scholar] [CrossRef]
  36. Pearson, R.G. Absolute electronegativity and hardness: Application to inorganic chemistry. Inorg. Chem. 1988, 27, 734–740. [Google Scholar] [CrossRef]
  37. Guo, Y.; Deng, J.; Zhu, J.; Zhou, X.; Bai, R. Removal of mercury(ii) and methylene blue from a wastewater environment with magnetic graphene oxide: Adsorption kinetics, isotherms and mechanism. RSC Adv. 2016, 6, 82523–82536. [Google Scholar] [CrossRef]
  38. Ghasemabadi, S.M.; Baghdadi, M.; Safari, E.; Ghazban, F. Investigation of continuous adsorption of Pb(II), As(III), Cd(II), and Cr(VI) using a mixture of magnetic graphite oxide and sand as a medium in a fixed-bed column. J. Environ. Chem. Eng. 2018, 6, 4840–4849. [Google Scholar] [CrossRef]
  39. Sham, A.Y.W.; Notley, S.M. Adsorption of organic dyes from aqueous solutions using surfactant exfoliated graphene. J. Environ. Chem. Eng. 2018, 6, 495–504. [Google Scholar] [CrossRef] [Green Version]
  40. Rouhi, M.; Lakouraj, M.M.; Tashakkorian, H.; Hasantabar, V. Novel carbon based bioactive nanocomposites of aniline/indole copolymer for removal of cationic dyes from aqueous solution: Kinetics and isotherms. New J. Chem. 2019, 43, 2400–2410. [Google Scholar] [CrossRef]
  41. Yang, S.T.; Chen, S.; Chang, Y.; Cao, A.; Liu, Y.; Wang, H. Removal of methylene blue from aqueous solution by graphene oxide. J. Colloid Interface Sci. 2011, 359, 24–29. [Google Scholar] [CrossRef]
  42. Björk, J.; Hanke, F.; Palma, C.A.; Samori, P.; Cecchini, M.; Persson, M. Adsorption of Aromatic and Anti-Aromatic Systems on Graphene through π−π Stacking. J. Phys. Chem. Lett. 2010, 1, 3407–3412. [Google Scholar] [CrossRef]
  43. Sriram, G.; Uthappa, U.T.; Kigga, M.; Jung, H.Y.; Altalhi, T.; Brahmkhatri, V.; Kurkuri, M.D. Xerogel activated diatoms as an effective hybrid adsorbent for the efficient removal of malachite green. New J. Chem. 2019, 43, 3810–3820. [Google Scholar] [CrossRef]
  44. Peng, R.; Chen, X.; Ghosh, R. Preparation of graphene oxide-cotton fiber composite adsorbent and its application for the purification of polyphenols from pomegranate peel extract. Sep. Purif. Technol. 2017, 174, 561–569. [Google Scholar] [CrossRef]
  45. Thiruppathi, A.R.; Sidhureddy, B.; Keeler, W.; Chen, A. Facile one-pot synthesis of fluorinated graphene oxide for electrochemical sensing of heavy metal ions. Electrochem. Commun. 2017, 76, 42–46. [Google Scholar] [CrossRef]
  46. Sidhureddy, B.; Thiruppathi, A.R.; Chen, A. From graphite to interconnected reduced graphene oxide: One-pot synthesis and supercapacitor application. Chem. Commun. 2017, 53, 7828–7831. [Google Scholar] [CrossRef]
  47. Mao, B.; Sidhureddy, B.; Thiruppathi, A.R.; Wood, P.C.; Chen, A. Efficient Dye Removal and Separation Based on Graphene Oxide Nanomaterials. New J. Chem. 2020, 44, 4519–4528. [Google Scholar] [CrossRef]
  48. Gomi, L.S.; Afsharpour, M.; Ghasemzadeh, M.; Lianos, P. Bio-inspired N, S-doped siligraphenes as novel metal-free catalysts for removal of dyes in the dark. J. Mol. Liq. 2019, 295, 111657. [Google Scholar] [CrossRef]
  49. Zeng, Q.; Li, J.; Li, L.; Bai, J.; Xia, L.; Zhou, B. Synthesis of WO3/BiVO4 photoanode using a reaction of bismuth nitrate with peroxovanadate on WO3 film for efficient photoelectrocatalytic water splitting and organic pollutant degradation. Appl. Catal. B Environ. 2017, 217, 21–29. [Google Scholar] [CrossRef]
  50. Williams, K.; Nelson, C.; Yan, X.; Li, L.; Zhu, X. Hot electron injection from graphene quantum dots to TiO2. ACS Nano 2013, 7, 1388–1394. [Google Scholar] [CrossRef] [PubMed]
  51. Tu, Y.; Utsunomiya, T.; Kokufu, S.; Soga, M.; Ichii, T.; Sugimura, H. Immobilization of reduced graphene oxide on hydrogen-terminated silicon substrate as a transparent conductive protector. Langmuir 2017, 33, 10765–10771. [Google Scholar] [CrossRef]
Molecules 26 06569 g001 550
Figure 1. XPS analysis of NPBG: (a) XPS survey, (b) C1s, (c) O1s, and (d) N1s.
Figure 1. XPS analysis of NPBG: (a) XPS survey, (b) C1s, (c) O1s, and (d) N1s.
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Figure 2. SEM images of (a,b) NBG, (c,d) NPBG, (e,f) WO3/NPBG-NC; (g) TEM image of WO3/NPBG-NC.
Figure 2. SEM images of (a,b) NBG, (c,d) NPBG, (e,f) WO3/NPBG-NC; (g) TEM image of WO3/NPBG-NC.
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Figure 3. EDX spectra of (a) NPBG and (b) WO3/NPBG-NC.
Figure 3. EDX spectra of (a) NPBG and (b) WO3/NPBG-NC.
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Figure 4. N2 adsorption/desorption and pore size distribution of (a) NBG, (b) NPBG, and (c) WO3/NPBG-NC.
Figure 4. N2 adsorption/desorption and pore size distribution of (a) NBG, (b) NPBG, and (c) WO3/NPBG-NC.
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Figure 5. FT-IR spectra of (a) NPBG and (b) WO3/NPBG-NC.
Figure 5. FT-IR spectra of (a) NPBG and (b) WO3/NPBG-NC.
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Figure 6. XRD patterns of (a) NPBG and (b) WO3/NPBG-NC.
Figure 6. XRD patterns of (a) NPBG and (b) WO3/NPBG-NC.
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Figure 7. Raman spectra of (a) NPBG and (b) WO3/NPBG-NC.
Figure 7. Raman spectra of (a) NPBG and (b) WO3/NPBG-NC.
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Figure 8. Bandgaps of (a) WO3-NPs and (b) WO3/NPBG-NC, according to the Tauc plot.
Figure 8. Bandgaps of (a) WO3-NPs and (b) WO3/NPBG-NC, according to the Tauc plot.
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Figure 9. Degradation of 100 mg/L of CR solution using 0.015 g of (a,a1) NBG, (b,b1) NPBG, and (c,c1) WO3/NPBG-NC in the dark condition (- - -) and visible light (—).
Figure 9. Degradation of 100 mg/L of CR solution using 0.015 g of (a,a1) NBG, (b,b1) NPBG, and (c,c1) WO3/NPBG-NC in the dark condition (- - -) and visible light (—).
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Figure 10. TOC removal efficiency under dark and light irradiation conditions for degradation of 100 mg/L of CR solution using 0.015 g of the photocatalyst.
Figure 10. TOC removal efficiency under dark and light irradiation conditions for degradation of 100 mg/L of CR solution using 0.015 g of the photocatalyst.
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Figure 11. Schematic of photocatalytic mechanism of pollutant degradation by WO3/NPBG-NC.
Figure 11. Schematic of photocatalytic mechanism of pollutant degradation by WO3/NPBG-NC.
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Figure 12. Control experiments of the photocatalytic removal of 100 mg/L of CR solution with the addition of different radical quenchers using 0.015 g of WO3/NPBG-NC.
Figure 12. Control experiments of the photocatalytic removal of 100 mg/L of CR solution with the addition of different radical quenchers using 0.015 g of WO3/NPBG-NC.
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Figure 13. Effect of different amounts of WO3/NPBG-NC on the removal of 100 mg/L of CR solution under visible light.
Figure 13. Effect of different amounts of WO3/NPBG-NC on the removal of 100 mg/L of CR solution under visible light.
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Figure 14. Effect of different concentrations of CR on the photocatalytic activity of 0.015 g of WO3/NPBG-NC under visible light.
Figure 14. Effect of different concentrations of CR on the photocatalytic activity of 0.015 g of WO3/NPBG-NC under visible light.
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Figure 15. Comparison of the photocatalytic activity of 0.015 g of WO3/NPBG-NC for the removal of 100 mg/L of different anionic azo dyes under visible light.
Figure 15. Comparison of the photocatalytic activity of 0.015 g of WO3/NPBG-NC for the removal of 100 mg/L of different anionic azo dyes under visible light.
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Figure 16. Degradation of 10 mg/L of acetaminophen and tetracycline solutions using 0.015 g of WO3/NPBG-NC under visible light.
Figure 16. Degradation of 10 mg/L of acetaminophen and tetracycline solutions using 0.015 g of WO3/NPBG-NC under visible light.
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Figure 17. Photocatalytic activity of 0.015 g of WO3/NPBG-NC in degradation of 100 mg/L of CR solution after 15 min under visible light for five cycles.
Figure 17. Photocatalytic activity of 0.015 g of WO3/NPBG-NC in degradation of 100 mg/L of CR solution after 15 min under visible light for five cycles.
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Table
Table 1. Textural characterization of the synthesized samples.
Table 1. Textural characterization of the synthesized samples.
SampleSBET (m2/g)Total Pore Volume (cm3/g)Average Pore Diameter (nm)
NBG38.980.0272.65
NPBG151.980.0671.77
WO3/NPBG-NC226.920.0956.68
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Afsharpour, M.; Elyasi, M.; Javadian, H. A Novel N-Doped Nanoporous Bio-Graphene Synthesized from Pistacia lentiscus Gum and Its Nanocomposite with WO3 Nanoparticles: Visible-Light-Driven Photocatalytic Activity. Molecules 2021, 26, 6569. https://doi.org/10.3390/molecules26216569

AMA Style

Afsharpour M, Elyasi M, Javadian H. A Novel N-Doped Nanoporous Bio-Graphene Synthesized from Pistacia lentiscus Gum and Its Nanocomposite with WO3 Nanoparticles: Visible-Light-Driven Photocatalytic Activity. Molecules. 2021; 26(21):6569. https://doi.org/10.3390/molecules26216569

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Afsharpour, Maryam, Mehdi Elyasi, and Hamedreza Javadian. 2021. "A Novel N-Doped Nanoporous Bio-Graphene Synthesized from Pistacia lentiscus Gum and Its Nanocomposite with WO3 Nanoparticles: Visible-Light-Driven Photocatalytic Activity" Molecules 26, no. 21: 6569. https://doi.org/10.3390/molecules26216569

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