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Yousef, A.;  Thiehmed, Z.;  Shakoor, R.A.;  Altahtamouni, T. WS2-Based Nanomaterials Employed for Photocatalytic Water Treatment. Encyclopedia. Available online: https://encyclopedia.pub/entry/31850 (accessed on 19 April 2024).
Yousef A,  Thiehmed Z,  Shakoor RA,  Altahtamouni T. WS2-Based Nanomaterials Employed for Photocatalytic Water Treatment. Encyclopedia. Available at: https://encyclopedia.pub/entry/31850. Accessed April 19, 2024.
Yousef, Aseel, Zeineb Thiehmed, Rana Abdul Shakoor, Talal Altahtamouni. "WS2-Based Nanomaterials Employed for Photocatalytic Water Treatment" Encyclopedia, https://encyclopedia.pub/entry/31850 (accessed April 19, 2024).
Yousef, A.,  Thiehmed, Z.,  Shakoor, R.A., & Altahtamouni, T. (2022, October 28). WS2-Based Nanomaterials Employed for Photocatalytic Water Treatment. In Encyclopedia. https://encyclopedia.pub/entry/31850
Yousef, Aseel, et al. "WS2-Based Nanomaterials Employed for Photocatalytic Water Treatment." Encyclopedia. Web. 28 October, 2022.
WS2-Based Nanomaterials Employed for Photocatalytic Water Treatment
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Water pollution is one of the most serious environmental issues globally due to its harmful consequences on the ecosystem and public health. Various technologies have been developed for water treatment such as photocatalysis, which has recently drawn scientists’ attention. Photocatalytic techniques using semiconductors have shown an efficient removal of various water contaminants during water treatment as well as cost effectivity and low energy consumption. Tungsten disulfide (WS2) is among the promising Transition Metal Dichalcogenides (TMDs) photocatalysts, as it has an exceptional nanostructure and special properties including high surface area and high carrier mobility. It is usually synthesized via hydrothermal technique, chemical vapor deposition (CVD), and liquid-phase exfoliation (LPE) to obtain a wide variety of nanostructures such as nanosheets and nanorods. Most common examples of water pollutants that can be removed efficiently by WS2-based nanomaterials through semiconductor photocatalytic techniques are organic contaminants, pharmaceuticals, heavy metals, and infectious microorganisms.

photocatalysis tungsten disulfide water treatment heterostructure nanomaterials

1. Introduction

Currently, the world is suffering from great water concerns including waterborne infections and the lack of clean water supply due to the enormous development of the industry. Today’s most serious environmental aspect is water, and it is predicted to be the reason for wars in the future. Among the top priorities for the long-term economic situation are providing access to safe and valid drinking water. Chemicals such as dyes, pesticides, and pharmaceuticals as well as heavy metals and pathogenic microorganisms are among the most common pollutants that create significant threats to the natural environments and human health. This leads scientists to continuously investigate efficient water treatment technologies. Water treatment using photocatalysts can solve the problem of freshwater shortage taking place in many countries worldwide in recent decades [1][2][3][4].
Photocatalysis is the process that converts the energy of photons into chemical energy via semiconductors [5]. Photocatalytic systems have been widely used as a fascinating era in environment remediation and water cleaning, which is attributed to their effectiveness in removing contaminants [6]. The semiconductor photocatalytic technique is being studied and invested as a promising tool for water purification, as it is sustainable, has high efficiency and consumes low energy [7]. Moreover, it is considered cost-effective, environmentally friendly, and produces almost no by-products [8]. This technique implements light to degrade the pollutants into less harmful molecules [9]. Photocatalysis is considered an effective photochemical advanced oxidation process (AOP), as it is capable of degrading contaminants in gaseous and liquid mediums, as well as killing pathogenic microorganisms by using the naturally existing solar energy as a renewable light source, which makes the process sustainable and eco-friendly [10][11]. Photocatalysis produces the hydroxyl radical (OH) with oxidizing power of 2.80 V, which is considered relatively high [6].
Two-dimensional (2D) nanostructured materials are extensively used in water treatment for the removal of organic substances, pharmaceuticals, and heavy metal ions from water. These materials have a large surface area prepared out of layered structured materials that are strongly bonded within planes and weekly bonded between nanolayers via van der Waal forces. Generally, several approaches can be used to enhance the efficiency of photocatalytic 2D materials including doping and forming heterojunctions [12].
Recently, transition metal dichalcogenides (TMDs) are considered among the promising photocatalysts because of their tunable bandgaps, enhanced catalytic properties, ultra-thin thickness, and 2D structure [13]. Moreover, this type of nanomaterial is known for its excellent photocatalytic and electronic performances because it shows good stability, excellent carrier mobility, increased surface area, and controllable interfaces [14]. TMDs are known as 2D-layered materials in the form of (X-M-X), where M represents the transition metal sandwiched between two X, which represents the chalcogen. The thickness of each layer of TMDs is around 6–7 Å [15]. The transition-metal sulfide material is not active [16]. However, when the size is nano-scaled, the properties are significantly influenced. There is a diversity in the properties of bulk TMDs where they can be insulators such as HfS2, semimetals such as WTe2, metals such as NbS2, and semiconductors such as WS2. When these materials are exfoliated into few layers, they preserve their properties in addition to new characteristics generated by the confinement effect [17][18]. TMDs can exploit sunlight as an energy source for the removal of the bad chemicals present in water because of the significant photocatalytic potential of their nanostructure. Recent studies on TMDs show that the photocatalysts that are based on TMDs can be useful in a wider range of applications compared to other traditional photocatalysts, including TiO2 and ZnO, which are active only under the UV light region, whereas TMDs can react to visible light as well [19].
Tungsten disulfide (WS2) is a TMD that consists of S-W-S planes bound to each other via van der Waals interactions. The first forms of WS2 were described in 1992 as inorganic polyhedral, cylinders, and fullerene-like (IF) nanomaterials [20]. WS2 can be implemented in plenty of applications including photodetectors, solar cells, batteries, etc. The bandgap of the semi-conductive version ranges from 1.3 to 2.1 eV depending on the number of layers. WS2 is a promising photocatalyst due to its direct bandgap transition, large spin-orbit coupling, and strong quantum confinement effect [21]. Exfoliating the bulk WS2 to nanosheets can control its bandgap from indirect to direct type [22].

2. WS2 as a Photocatalyst

2.1. Structure

WS2 is found in two different phases, which are prismatic trigonal 2H phase and octahedral 1T phase, and each phase has different properties, where 2H-WS2 is semiconducting, and 1T-WS2 exhibits metallic properties. Both phases can be transformed into one another under certain conditions [23][24][25]. The bulk hexagonal WS2 (2H-WS2) shows an indirect band gap, whereas it exhibits an indirect-to-direct band gap transition when it is a monolayer [26][27]. The lattice parameters a and c for 2H-WS2 are 3.155 Å and 12.349 Å, respectively, and the internal coordinate z that determines the interlayer sulfur plane distance for bulk 2H-WS2 is 1.573 Å [28][29].

2.2. Properties

Among the 2D materials, WS2 is more abundant in the crust of Earth, has less toxicity, and is cheaper compared to other TMDs. Moreover, it is special for its extraordinary properties including high surface area, favorable electrochemical activity, photocatalytic and electronic efficiency, high carrier mobility, biocompatibility, and its tunable bandgap. In addition, WS2 is commonly used as a light-absorbing material due to its broad absorption spectrum, which makes it an efficient photocatalytic material. However, WS2 shows some limitations for some photocatalytic applications, as the band edge potential of its conduction band minimum does not match the potential requirements for photocatalytic water splitting for instance [30]. WS2 can show a low indirect band gap (less than 1.5 eV) and a higher direct bandgap (larger than 2 eV) depending on the synthesis technique used [31][32][33]. This relatively narrow band gap increases the light absorption region to 910 nm, which enables it to undergo the redox chemistry required for degradation of organic pollutants [34].

2.3. Synthesis

Various methods have been employed for the WS2 synthesis, among them are the mechanical activation method, sol-gel method, thermal evaporation technique, liquid-phase exfoliation method, hydrothermal method, and chemical deposition techniques. In addition, WS2 can be synthesized with a wide range of morphologies including nanosheets, nanofibers, and nanorods [20].
The hydrothermal route is among the promising techniques, as it is a simple process, yields a highly pure product, and is environmentally friendly. Cao, Liu, Hussain, and others succeeded in synthesizing different nanostructures of WS2 with various morphologies including nanorods, nanofibers, nanoparticles, and nanosheets via a hydrothermal route with the addition of the surfactants polyethylene glycol (PEG) and cetyltrimethylammonium ammonium bromide (CTAB). The surfactants were found to affect the fabrication of different morphologies of WS2 nanostructures [35].

3. Photocatalytic Water Treatment Using WS2 and Heterostructures

When different semiconductors having different energy gaps are coupled to form heterostructures, this will result in controlling the recombination process of the photogenerated charge carriers, improving the photocatalytic activity, reducing the bandgap, and moving the optical response to be in the visible light region to enable the investment of the solar energy. Forming a well-matched conduction band and valence band levels leads to a dimensional separation between the photogenerated electrons and holes [36]. The construction of heterojunctions is among the most common methods for photocatalysts fabrication and modification because it provides high activity and visible light response [37]. When using WS2 as a cocatalyst, semiconductor–semiconductor, or metal-semiconductor, heterojunctions will be constructed, which will result in creating more interfaces [38]. As a result, the charge separation and migration can be improved, and hence, the photoactivity will be enhanced [39].

3.1. Photocatalytic Degradation of Organic Substances

Enormous quantities of organic pollutants such as synthetic dyes, fertilizers, solvents, and pesticides are being released into the environment and the aquatic ecosystem, which can cause serious environmental problems [1]. These organic compounds are mostly stable and do not undergo biodegradation or photodegradation naturally and hence cause harm to humans and animals in both the short and long term [40]. In addition, organic pollutants can harm human health by causing cancers and mutations, nausea, mental confusion, and Alzheimer’s. Thereby, searching for new technologies for the removal of organic pollutants is demanded. This is because the traditional techniques showed some restrictions and limitations such as unaffordable operation costs, poor removal efficiency, complicated processes, and low adaption to many organic structures [41][42]. AOPs can be used to eliminate organic pollutants from wastewater via direct and indirect processes where hydroxyl radicals are employed to hydroxylate or dehydrogenate the pollutants, and then, they will finally mineralize [43][44]. Therefore, the main advantage of using AOP for the degradation of organic pollutants is the complete destruction it guarantees instead of changing them into another phase, and without the need for toxic oxidants such as chlorination [45]. Photocatalysis can be utilized for degrading organic pollutants, as it provides good reproducibility, simplicity, high efficiency, and low cost. Photocatalysis can degrade organic pollutants into harmless products. The photocatalysis process is mainly a reaction between the organic pollutants and oxidizing and reducing agents, which are holes and electrons generated under UV or visible light irradiation on the photocatalyst’s surface [37].

3.2. Microorganisms’ Disinfection

Microbial pollution is among the most popular problems, as it is directly related to health and the environment [46]. Wastewater treatment plants cannot usually remove the pathogenic microorganisms because of the shortage in financial resources, which causes hazardous effects on public health [47]. Currently, pathogenic microorganisms contaminating water such as viruses, fungi, and bacteria and their corresponding infections are of particular concern. It is known that pathogens infections have been creating disasters such as cholera, which is caused by Vibrio cholerae, and plague, which is caused by Yersinia pestis. The enterotoxin-genic Escherichia coli, which causes diarrheal illness and passes through contaminated water, kills about 1.3 million children annually [48][49]. Referring to the WHO Guidelines for drinking water quality, drinking water is considered safe if it is free from fecal organisms including Escherichia coli, Clostridium perfringens, Enterococcus spp., Total coliforms, Thermotolerant coliforms [50]. The antibacterial photocatalytic mechanism begins by damaging the bacterial cell membrane, which causes damage to the internal components of the bacterial cell consequently. After that, the photocatalytic reactions will oxidize the remaining parts of the leaked bacterial cell [51][52].

3.3. Heavy Metals Reduction

Heavy metals are metals with high atomic weights, atomic numbers, and densities that are greater than 5 g/cm3. The presence of heavy metals in water can cause poisoning of the living creatures, which leads to biodiversity damage, in addition to endangering human health when accumulating in the human body, causing cancers and organ failure. Examples of common heavy metals present in the environment are lead, cadmium, chromium, and arsenic [53][54]. Adopting strategies for the removal of heavy metal ions contaminating water is a great challenge for the scientific community currently. Some convenient methods such as chemical precipitation and reverse osmosis are used. However, these techniques showed some restrictions and limitations, as they cannot achieve complete removal of the metal ions, as well as the formation of sludge in large amounts, which are difficult to be disposed of and managed properly [55][56][57]. Furthermore, photocatalysis can provide a continuous operation, as it does not need energy input except light energy. In addition, the photocatalytic redox reactions do not produce polluting intermediates, which makes it a green process for heavy metals reduction. Moreover, photocatalysis works on depositing heavy metals to be easily reduced on the surface of the photocatalyst as solids to be directly separated from the solution [58][59][60][61].

3.4. Pharmaceuticals Photodegradation

Pharmaceutical waste is one of the most serious existing pollutants in water worldwide. There are several ways by which these pollutants were introduced to the environment such as hospital and domestic sewage, industrial discharge, and wastewater treatment plants. Pharmaceuticals are among the most significant contaminants of water, as they play a role in the alteration of the metabolic activity of the existing biota and hence can produce noticeable biochemical modifications. Currently, the world witnesses an extensive consumption of antibiotics, which caused an enormous increase in antibiotic wastes, and hence led to generating resistant bacteria, which threatens human health severely [62][63][64].

4. Conclusion

The investigation of the fundamentals of synthesis and applications of WS2-nanostructured materials is still in continuous progress worldwide. The broad spectrum of applications in which WS2 is employed has emerged from its superior properties as a TMD such as large specific surface area, tunable band gap, and high mobility. This entry focused on the recent research work conducted on WS2-based nanomaterials and their significant role in the photocatalytic water treatment process including the degradation of organic substances such as dyes and pesticides, disinfection of water, and killing pathogens, reduction of heavy metals, and degradation of drugs and pharmaceuticals. The mechanism by which photocatalysis degrades pollutants in water was also explained. In addition, the entry highlighted the main techniques by which WS2 nanostructures are synthesized such as hydrothermal, CVD, and LPE. It can be concluded that heterostructure construction is an essential solution to approach maximum degradation efficiency by reducing electron-hole pair separation and lowering the bandgap energy. Future research should consider the need of sufficient understanding of the growth conditions and behaviors of WS2. In addition, optimizing the operation parameters and developing new effective designs to enhance the performance of WS2 for water treatment applications is urgently needed. In addition, new studies must focus on incorporating WS2 nanostructures in a hybrid/composite photocatalyst to extend its advantages as a green and cost-effective system for water purification and environmental remediation.

References

  1. Jing, L.; Zhou, W.; Tian, G.; Fu, H. Surface tuning for oxide-based nanomaterials as efficient photocatalysts. Chem. Soc. Rev. 2013, 42, 9509–9549.
  2. Alharbi, N.S.; Hu, B.; Hayat, T.; Rabah, S.O.; Alsaedi, A.; Zhuang, L.; Wang, X. Efficient elimination of environmental pollutants through sorption-reduction and photocatalytic degradation using nanomaterials. Front. Chem. Sci. Eng. 2020, 14, 1124–1135.
  3. Garg, A.; Singhania, T.; Singh, A.; Sharma, S.; Rani, S.; Neogy, A.; Wang, X. Photocatalytic Degradation of Bisphenol-A using N, Co Codoped TiO2 Catalyst under Solar Light. Sci. Rep. 2019, 9, 765.
  4. Qutub, N.; Singh, P.; Sabir, S.; Sagadevan, S.; Oh, W.-C. Enhanced photocatalytic degradation of Acid Blue dye using CdS/TiO2 nanocomposite. Sci. Rep. 2022, 12, 5759.
  5. Zhang, J.; Zhang, L.; Ma, X.; Ji, Z. A study of constructing heterojunction between two-dimensional transition metal sulfides (MoS2 and WS2) and (101), (001) faces of TiO2. Appl. Surf. Sci. 2018, 430, 424–437.
  6. Ahmad, R.; Ahmad, Z.; Khan, A.U.; Mastoi, N.R.; Aslam, M.; Kim, J. Photocatalytic systems as an advanced environmental remediation: Recent developments, limitations and new avenues for applications. J. Environ. Chem. Eng. 2016, 4, 4143–4164.
  7. Li, S.; Wang, C.; Cai, M.; Yang, F.; Liu, Y.; Chen, J.; Zhang, P.; Li, X.; Chen, X. Facile fabrication of TaON/Bi2MoO6 core–shell S-scheme heterojunction nanofibers for boosting visible-light catalytic levofloxacin degradation and Cr(VI) reduction. Chem. Eng. J. 2022, 428, 131158. Available online: https://reader.elsevier.com/reader/sd/pii/S138589472102739X?token=D799FE216F506B28FC9A76E8F9EFC7EEA687C2DB4A2C5E4FC1B6619450B2316178BE5B5C01908DFCF9277A19062DAC7F&originRegion=eu-west-1&originCreation=20211216102211 (accessed on 16 December 2021).
  8. Wang, W.; Zeng, Z.; Zeng, G.; Zhang, C.; Xiao, R.; Zhou, C.; Xiong, W.; Yang, Y.; Liu, Y.; Huang, D.; et al. Sulfur doped carbon quantum dots loaded hollow tubular g-C3N4 as novel photocatalyst for destruction of Escherichia coli and tetracycline degradation under visible light. Chem. Eng. J. 2019, 378, 122132. Available online: https://reader.elsevier.com/reader/sd/pii/S1385894719315268?token=E75BCF52D7CADB9C79C9153BB600C5717FE868F4BDB3A4177DF72392C836E5B307F44EBC39C8E62F8F3DF39E862C8B55&originRegion=eu-west-1&originCreation=20211216104206 (accessed on 16 December 2021).
  9. Sahu, K.; Kuriakose, S.; Singh, J.; Satpati, B.; Mohapatra, S. Facile synthesis of ZnO nanoplates and nanoparticle aggregates for highly efficient photocatalytic degradation of organic dyes. J. Phys. Chem. Solids 2018, 121, 186–195. Available online: https://reader.elsevier.com/reader/sd/pii/S0022369717324393?token=5DC0699F806F4278530EE3223AEF547BF5347A5CAF0686D2B3FE4D7A973AA8408AC6906B379906548B22375646CF2A55&originRegion=eu-west-1&originCreation=20211216105136 (accessed on 16 December 2021).
  10. George, R.; Bahadur, N.; Singh, N.; Singh, R.; Verma, A.; Shukla, A.K. Environmentally Benign TiO2 Nanomaterials for Removal of Heavy Metal Ions with Interfering Ions Present in Tap Water. Mater. Today Proc. 2016, 3, 162–166.
  11. Pelaez, M.; Nolan, N.T.; Pillai, S.C.; Seery, M.K.; Falaras, P.; Kontos, A.G.; Dunlop, P.S.M.; Hamilton, J.W.J.; Byrne, J.A.; O’Shea, K.; et al. A review on the visible light active titanium dioxide photocatalysts for environmental applications. Appl. Catal. B Environ. 2012, 125, 331–349.
  12. Garg, A.; Basu, S.; Shetti, N.P.; Reddy, K.R. 2D materials and its heterostructured photocatalysts: Synthesis, properties, functionalization and applications in environmental remediation. J. Environ. Chem. Eng. 2021, 9, 106408.
  13. Wang, Y.; Xiao, X.; Lu, M.; Xiao, Y. 3D network-like rGO-MoSe2 modified g-C3N4 nanosheets with Z-scheme heterojunction: Morphology control, heterojunction construct, and boosted photocatalytic performances. J. Alloys Compd. 2021, 893, 163197.
  14. Wang, Y.; Lei, S.; Zhang, X.; Zhou, S. First-principles study of nitrogen defect g-C3N4/WS2 heterojunction on photocatalytic activity. Curr. Appl. Phys. 2022, 39, 70–76.
  15. Choi, W.; Choudhary, N.; Han, G.H.; Park, J.; Akinwande, D.; Lee, Y.H. Recent development of two-dimensional transition metal dichalcogenides and their applications. Mater. Today 2017, 20, 116–130.
  16. Zhang, D.; Liu, T.; Cheng, J.; Liang, S.; Chai, J.; Yang, X.; Wang, H.; Zheng, G.; Cao, M. Controllable synthesis and characterization of tungsten disulfide nanosheets as promising nanomaterials for electronic devices. Ceram. Int. 2019, 45, 12443–12448.
  17. Shalaby, M.S.; Sołowski, G.; Abbas, W. Recent Aspects in Membrane Separation for Oil/Water Emulsion. Adv. Mater. Interfaces 2021, 8, 2100448.
  18. Zhang, N.; Yang, X.; Wang, Y.; Qi, Y.; Zhang, Y.; Luo, J.; Cui, P.; Jiang, W. A review on oil/water emulsion separation membrane material. J. Environ. Chem. Eng. 2022, 10, 107257.
  19. Mishra, A.K.; Lakshmi, K.V.; Huang, L. Eco-friendly synthesis of metal dichalcogenides nanosheets and their environmental remediation potential driven by visible light. Sci. Rep. 2015, 5, 15718.
  20. Nawaz, A.; Goudarzi, S.; Saravanan, P.; Zarrin, H. Z-scheme induced g-C3N4/WS2 heterojunction photocatalyst with improved electron mobility for enhanced solar photocatalysis. Sol. Energy. 2021, 228, 53–67.
  21. Ma, S.; Zeng, L.; Tao, L.; Tang, C.Y.; Yuan, H.; Long, H.; Cheng, P.K.; Chai, Y.; Chen, C.; Fung, K.H.; et al. Enhanced Photocatalytic Activity of WS2 Film by Laser Drilling to Produce Porous WS2/WO3 Heterostructure Methods and mechanisms for improvement of photocatalytic activity, are important and popular research topics for renewable energy production and waste water treatment OPEN. Sci. Rep. 2017, 7, 3125. Available online: https://nature.com/scientificreports/ (accessed on 1 June 2022).
  22. Hazarika, S.J.; Mohanta, D. Inorganic fullerene-type WS2 nanoparticles: Processing, characterization and its photocatalytic performance on malachite green. Appl. Phys. A 2017, 123, 381.
  23. Chen, S.; Pan, Y.; Wang, D.; Deng, H. Structural Stability and Electronic and Optical Properties of Bulk WS2 from First-Principles Investigations. J. Electron. Mater. 2020, 49, 7363–7369.
  24. Lv, R.; Robinson, J.A.; Schaak, R.E.; Sun, D.; Sun, Y.; Mallouk, T.E.; Terrones, M. Transition metal dichalcogenides and beyond: Synthesis, properties, and applications of single- and few-layer nanosheets. Acc. Chem. Res. 2015, 48, 56–64. Available online: https://pubmed.ncbi.nlm.nih.gov/25490673/ (accessed on 9 May 2022).
  25. Zeng, Z.; Yin, Z.; Huang, X.; Li, H.; He, Q.; Lu, G.; Boey, H.; Zhang, H. Single-layer semiconducting nanosheets: High-yield preparation and device fabrication. Angew. Chem. 2011, 50, 11093–11097. Available online: https://pubmed.ncbi.nlm.nih.gov/22021163/ (accessed on 9 May 2022).
  26. Gutiérrez, H.R.; Perea-López, N.; Elías, A.L.; Berkdemir, A.; Wang, B.; Lv, R.; López-Urías, R.; Crespi, V.H.; Terrones, H.; Terrones, S. Extraordinary room-temperature photoluminescence in triangular WS2 monolayers. Nano. Lett. 2013, 13, 3447–3454. Available online: https://eres.qnl.qa/login?url=https://search.ebscohost.com/login.aspx?direct=true&db=cmedm&AN=23194096&site=ehost-live (accessed on 9 May 2022).
  27. Yun, W.S.; Han, S.W.; Hong, S.C.; Kim, I.G.; Lee, J.D. Thickness and strain effects on electronic structures of transition metal dichalcogenides: 2H-MX2 semiconductors (M = Mo, W; X = S, Se, Te). Phys. Rev. B 2012, 85, 33305.
  28. Liu, L.; Kumar, S.B.; Ouyang, Y.; Guo, J. Performance Limits of Monolayer Transition Metal Dichalcogenide Transistors. IEEE Trans. Electron. Devices 2011, 58, 3042–3047.
  29. Al-Hilli, A.A.; Evans, B.L. The preparation and properties of transition metal dichalcogenide single crystals. J. Cryst. Growth 1972, 15, 93–101.
  30. Jin, Q.; Dai, X.; Song, J.; Pu, K.; Wu, X.; An, J.; Zhao, T. High photocatalytic performance of g-C3N4/WS2 heterojunction from first principles. Chem. Phys. 2021, 545, 111141.
  31. Bin Rafiq, M.K.S.; Amin, N.; Alharbi, H.F.; Luqman, M.; Ayob, A.; Alharthi, Y.S.; Alharthi, N.H.; Bais, B.; Akhtaruzzaman, M. WS2: A New Window Layer Material for Solar Cell Application. Sci. Rep. 2020, 10, 771.
  32. Green, M.A. Thin-film solar cells: Review of materials, technologies and commercial status. J. Mater. Sci. Mater. Electron. 2007, 18, 15–19.
  33. Fatima, T.; Husain, S.; Narang, J.; Khanuja, M.; Shetti, N.P.; Reddy, K.R. Novel tungsten disulfide (WS2) nanosheets for photocatalytic degradation and electrochemical detection of pharmaceutical pollutants. J. Water Process. Eng. 2022, 47, 102717.
  34. Voiry, D.; Yamaguchi, H.; Li, J.; Silva, R.; Alves, D.C.B.; Fujita, T.; Chen, M.; Asefa, T.; Shenoy, V.B.; Eda, G.; et al. Enhanced catalytic activity in strained chemically exfoliated WS2 nanosheets for hydrogen evolution. Nat. Mater. 2013, 12, 850–855.
  35. Cao, S.; Liu, T.; Hussain, S.; Zeng, W.; Peng, X.; Pan, F. Hydrothermal synthesis of variety low dimensional WS2 nanostructures. Mater. Lett. 2014, 129, 205–208.
  36. Zhu, D.; Zhou, Q. Action and mechanism of semiconductor photocatalysis on degradation of organic pollutants in water treatment: A review. Environ. Nanotechnol. Monit. Manag. 2019, 12, 100255.
  37. Wang, H.; Zhang, L.; Chen, Z.; Hu, J.; Li, S.; Wang, Z.; Liu, J.; Wang, X. Semiconductor heterojunction photocatalysts: Design, construction, and photocatalytic performances. Chem. Soc. Rev. 2014, 43, 5234–5244.
  38. Fan, Y.; Chen, G.; Li, D.; Li, F.; Luo, Y.; Meng, Q. Enhancement of photocatalytic H2 evolution on hexagonal CdS by a simple calcination method under visible light irradiation. Mater. Res. Bull. 2011, 46, 2338–2341.
  39. Zong, X.; Wu, G.; Yan, H.; Ma, G.; Shi, J.; Wen, F.; Wang, L.; Li, C. Photocatalytic H2 evolution on MoS2/CdS catalysts under visible light irradiation. J. Phys. Chem. C 2010, 114, 1963–1968.
  40. Es’haghzade, Z.; Pajootan, E.; Bahrami, H.; Arami, M. Facile synthesis of Fe3O4 nanoparticles via aqueous based electro chemical route for heterogeneous electro-Fenton removal of azo dyes. J. Taiwan Inst. Chem. Eng. 2017, 71, 91–105.
  41. Yao, L.; Zhang, L.; Wang, R.; Chou, S.; Dong, Z.L. A new integrated approach for dye removal from wastewater by polyoxometalates functionalized membranes. J. Hazard. Mater. 2016, 301, 462–470.
  42. Tekin, G.; Ersöz, G.; Atalay, S. Degradation of benzoic acid by advanced oxidation processes in the presence of Fe or Fe-TiO2 loaded activated carbon derived from walnut shells: A comparative study. J. Environ. Chem. Eng. 2018, 6, 1745–1759.
  43. Akerdi, A.G.; Es’Haghzade, Z.; Bahrami, S.H.; Arami, M. Comparative study of GO and reduced GO coated graphite electrodes for decolorization of acidic and basic dyes from aqueous solutions through heterogeneous electro-Fenton process. J. Environ. Chem. Eng. 2017, 5, 2313–2324.
  44. Byrne, C.; Subramanian, G.; Pillai, S.C. Recent advances in photocatalysis for environmental applications. J. Environ. Chem. Eng. 2018, 6, 3531–3555.
  45. Akerdi, A.G.; Bahrami, S.H. Application of heterogeneous nano-semiconductors for photocatalytic advanced oxidation of organic compounds: A review. J. Environ. Chem. Eng. 2019, 7, 103283.
  46. Liao, Y.; Yao, Y.; Yu, Y.; Zeng, Y. Enhanced Antibacterial Activity of Curcumin by Combination With Metal Ions. Colloids Interface Sci. Commun. 2018, 25, 1–6.
  47. Schwarzenbach, R.P.; Egli, T.; Hofstetter, T.B.; Von Gunten, U.; Wehrli, B. Global water pollution and human health. Annu. Rev. Environ. Resour. 2010, 35, 109–136.
  48. Santosham, M.; Chandran, A.; Fitzwater, S.; Fischer-Walker, C.; Baqui, A.H.; Black, R. Progress and barriers for the control of diarrhoeal disease. Lancet 2010, 376, 63–67.
  49. Staedel, C.; Darfeuille, F. MicroRNAs and bacterial infection. Cell. Microbiol. 2013, 15, 1496–1507.
  50. WHO. Guidelines for Drinking-Water Quality; World Health Organization: Geneva, Switzerland, 2011; Volume 216, pp. 303–304.
  51. Rengifo-Herrera, J.A.; Mielczarski, E.; Mielczarski, J.; Castillo, N.C.; Kiwi, J.; Pulgarin, C. Escherichia coli inactivation by N, S co-doped commercial TiO2 powders under UV and visible light. Appl. Catal. B Environ. 2008, 84, 448–456.
  52. Rengifo-Herrera, J.A.; Pierzchała, K.; Sienkiewicz, A.; Forró, L.; Kiwi, J.; Pulgarin, C. Abatement of organics and Escherichia coli by N, S co-doped TiO2 under UV and visible light. Implications of the formation of singlet oxygen (1O2) under visible light. Appl. Catal. B Environ. 2009, 88, 398–406.
  53. Fu, F.; Wang, Q. Removal of heavy metal ions from wastewaters: A review. J. Environ. Manag. 2011, 92, 407–418.
  54. Litter, M.I. Mechanisms of removal of heavy metals and arsenic from water by TiO2-heterogeneous photocatalysis. Pure Appl. Chem. 2015, 87, 557–567.
  55. Engates, K.E.; Shipley, H.J. Adsorption of Pb, Cd, Cu, Zn, and Ni to titanium dioxide nanoparticles: Effect of particle size, solid concentration, and exhaustion. Environ. Sci. Pollut. Res. 2011, 18, 386–395.
  56. Skubal, L.R.; Meshkov, N.K.; Rajh, T.; Thurnauer, M. Cadmium removal from water using thiolactic acid-modified titanium dioxide nanoparticles. J. Photochem. Photobiol. A Chem. 2002, 148, 393–397.
  57. Regmi, P.; Garcia Moscoso, J.L.; Kumar, S.; Cao, X.; Mao, J.; Schafran, G. Removal of copper and cadmium from aqueous solution using switchgrass biochar produced via hydrothermal carbonization process. J. Environ. Manag. 2012, 109, 61–69.
  58. Gao, X.; Meng, X. Photocatalysis for heavy metal treatment: A review. Processes 2021, 9, 1729.
  59. Meng, X.; Zhang, Z.; Li, X. Synergetic photoelectrocatalytic reactors for environmental remediation: A review. J. Photochem. Photobiol. C Photochem. Rev. 2015, 24, 83–101.
  60. Kubota, Y.; Watanabe, K.; Tsuda, O.; Taniguchi, T. Deep ultraviolet light-emitting hexagonal boron nitride synthesized at atmospheric pressure. Science 2007, 317, 932–934.
  61. Xie, W.; Zhang, M.; Liu, D.; Lei, W.; Sun, L.; Wang, X. Photocatalytic TiO2/porous BNNSs composites for simultaneous LR2B and Cr (VI) removal in wool dyeing bath. J. Photochem. Photobiol. A Chem. 2017, 333, 165–173.
  62. Kumar, E.; Holt, W. V Impacts of Endocrine Disrupting Chemicals on Reproduction in Wildlife. In Advances in Experimental Medicine and Biology; Springer: New York, NY, USA, 2014; Volume 753, pp. 55–70.
  63. Cesaro, A.; Belgiorno, V. Removal of Endocrine Disruptors from Urban Wastewater by Advanced Oxidation Processes (AOPs): A Review. Open Biotechnol. J. 2016, 10, 151–172.
  64. Petrie, B.; Barden, R.; Kasprzyk-Hordern, B. A review on emerging contaminants in wastewaters and the environment: Current knowledge, understudied areas and recommendations for future monitoring. Water Res. 2015, 72, 3–27.
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