Submitted Successfully!
To reward your contribution, here is a gift for you: A free trial for our video production service.
Thank you for your contribution! You can also upload a video entry or images related to this topic.
Version Summary Created by Modification Content Size Created at Operation
1 -- 3255 2023-07-18 13:40:02 |
2 layout & references Meta information modification 3255 2023-07-19 03:08:06 | |
3 add figure citation + 15 word(s) 3270 2023-08-02 08:53:54 |

Video Upload Options

Do you have a full video?


Are you sure to Delete?
If you have any further questions, please contact Encyclopedia Editorial Office.
Zhu, W.; Li, X.; Wang, D.; Fu, F.; Liang, Y. Advanced Photocatalytic Uranium Extraction Strategies. Encyclopedia. Available online: (accessed on 15 June 2024).
Zhu W, Li X, Wang D, Fu F, Liang Y. Advanced Photocatalytic Uranium Extraction Strategies. Encyclopedia. Available at: Accessed June 15, 2024.
Zhu, Wangchuan, Xiang Li, Danjun Wang, Feng Fu, Yucang Liang. "Advanced Photocatalytic Uranium Extraction Strategies" Encyclopedia, (accessed June 15, 2024).
Zhu, W., Li, X., Wang, D., Fu, F., & Liang, Y. (2023, July 18). Advanced Photocatalytic Uranium Extraction Strategies. In Encyclopedia.
Zhu, Wangchuan, et al. "Advanced Photocatalytic Uranium Extraction Strategies." Encyclopedia. Web. 18 July, 2023.
Advanced Photocatalytic Uranium Extraction Strategies

The development of simple, efficient, and economical uranium extraction methods is of great significance for the sustainable development of nuclear energy and the restoration of the ecological environment. Photocatalytic U(VI) extraction technology as a simple, highly efficient, and low-cost strategy, received increasing attention from researchers.

photocatalysis structures U(VI) extraction mechanism

1. Mechanism of Photocatalytic Uranium Reduction and Identification of Reduction Products

The photocatalytic uranium extraction strategy, as an important technology for uranium resource recovery and ecosystem restoration, widely attracted increasing attention. Only in 2022, there were 67 research articles relevant to the photocatalytic reduction of U(VI), showing a gradually increasing tendency. Current research mainly focuses on how to improve the catalytic efficiency of photocatalysts, while the forms of uranium and the conversion processes were rarely investigated [1]. In nature, uranium species mainly exist in uranium mine wastewater and seawater in four valence states: III, IV, V, and IV [2]. Among them, U(IV) and U(VI) species are the most stable in a natural water environment, and uranyl ions (UO22+) usually participate in migration and transformation process [3][4][5].
U(VI) can exist as all kinds of U species in aqueous solutions, and the types of U(VI) species change with various acidic and alkaline environments [6]. In acidic solutions, U(VI) species mainly exist in the form of UO22+. When pH is higher than 4, UO22+ species decrease, UO2OH+, (UO2)3OH5+, and (UO2)2OH22+ species gradually increase, leading to a complex distribution of uranium species. The distribution of U(VI) species is greatly influenced by pH. Due to the complexity and diversity of natural water environments, the photocatalysts used for U extraction must have a relatively wide selectivity for different U(VI) species to improve uranium extraction efficiency. Herein, the studies on photocatalytic uranium extraction in recent years are listed in Table 1 [7][8][9][10][11][12][13][14][15][16][17][18][19][20][21][22][23][24][25][26][27][28][29][30][31][32][33][34][35][36][37][38][39][40][41][42][43][44].
Table 1. The photocatalytic U(VI) reduction performance over different catalysts.
The main purpose of photocatalytic uranium extraction is to convert soluble U(VI) into insoluble UO2 and (UO2)(O2)·4H2O [48] in order to recover them from solution. In general, photocatalytic U(VI) extraction includes the following process in the presence of catalyst. Light is irradiated on the catalyst to generate electron-hole pairs, which are used directly to reduce the soluble U(VI) to insoluble U species. Previous studies showed that uranium reduction may involve three different mechanisms of electron transfer [49][50]
The first proposed mechanism is a two-step single-electron transfer process, where U(VI) is first reduced to U(V) by accepting an electron (U(VI) + e → U(V)) and then further reduced to U(IV) by accepting another electron (U(V) + e → U(IV)) [51][52][53][54]. Furthermore, U(V) can undergo disproportionation under certain conditions to form both U(IV) and U(VI) (U(V) → U(IV) + U(VI)) [41].
The second mechanism involves a two-electron reduction process, where U(VI) accepts two electrons and is directly reduced to U(IV) (UO22+ + 2e → UO2) [9][55].
The third mechanism involves the reaction of U(VI) with one electron and four protons to produce U(IV) and two water molecules in acidic solution (UO22+ + 4H+ + e → U4+ + 2H2O), or the reaction of U(V) generated from the first mechanism with one electron and four protons to produce U(IV) and two water molecules (UO2+ + 4H+ + e → U4+ + 2H2O). In addition, in some specific photocatalytic systems, excess electrons at the conduction band (CB) position will react with dissolved oxygen to generate ·O2 (O2 + e·O2), which can also reduce U(VI) via UO2+ + O2 → UO2 + 2O2 [44].
Obviously, the photocatalytic reduction of U(VI) involves various electron transfer processes. Suitable band structure and high carrier mobility are key factors in the design of photocatalysts. In general, when the redox potential of a target substance falls between the valence band maximum and the CB minimum of a catalyst, the substance may undergo a redox reaction. For the semiconductor itself, a CB potential higher than the U(VI) reduction potential (+0.41 V) is required to facilitate electron transfer [56]. Based on semiconductor photocatalysts, cadmium sulfide (CdS) received wide attention due to its narrow bandgap relative to visible light response and suitable CB position [57]. Qin et al. synthesized NiS@CdS interface Schottky heterojunction photocatalysts with different Ni/Cd molar ratios. The simulated removal efficiency of U(VI) in U-containing wastewater was as high as 99% under 90 min under solar light irradiation. This result is attributed to their good zeta potential and optical properties, narrow bandgap, and the high stability of the composite material [58].
The effective adsorption sites on the photocatalyst surface are very pivotal for photocatalytic uranium reduction, due to these sites determining the interaction between the catalyst and uranium species and the triggering of the reduction reaction [7]. Moreover, the final product of photocatalytic uranium extraction is mainly adsorbed on the surface of the catalyst, hence the type of product U species can be identified by various characterization methods, such as X-ray diffraction (XRD), X-ray photoelectron spectroscopy (XPS), Fourier-transform infrared spectroscopy (FT-IR), transmission electron microscopy (TEM), and X-ray absorption near edge structure (XANES) [59]. For instance, Chen et al. [60] use TT-POR COF-Ni as a photocatalyst to remove uranium. After photocatalytic reaction, the form of uranium was characterized by XPS, FT-IR, and PXRD. The high-resolution O 1s XPS indicated three different oxygen species, attributable to U-Operoxo, U = Oaxial, and H2O, respectively. While the high-resolution U 4f XPS showed a characteristic peak that corresponded to U 4f7/2 in UO2(O)2·2H2O at 381.9 eV, implying no change in the valence state of uranium. Moreover, the PXRD pattern also appeared at some new diffraction peaks at 2θ = 16.8°, 20.2°, 23.4°, and 25.1°, which can be attributed to metastudtite phase (UO2(O)2·2H2O, and the characteristic peak of UO2 at 2θ = 28.1° was not found. In addition, the appearance of peaks at 902 cm−1 assigned to the uranyl group and at 3460 cm−1 belonged to O-H vibration from H2O in the FTIR spectra after light irradiation further corroborated the formation of (UO2(O)2·2H2O.
Additionally, to identify the uranium-containing products of the photocatalytic experiments, U LIII-edge XANES spectroscopy, Fourier transform extended X-ray absorption fine structure spectroscopy (FT-EXAFS) and wavelet transform (WT) contour maps were measured [61]

2. Photocatalysts for Uranium Recovery from Solution

In the past decade, photocatalytic uranium extraction was regarded as a simple, efficient, and environmentally friendly method to solve U(VI) contamination in water. In general, TiO2 is the most widely used photocatalytic material in recent years for solving U(VI) pollution problems [9][44][62][63][64][65][66][67]. However, TiO2 as a photocatalyst indicated some potential disadvantages for the removal of U(VI): (1) recombination of photogenerated electron-hole pairs in TiO2 leads to the decline in photocatalytic efficiency [68]; (2) an artificial UV light source is required, and it is difficult to achieve U(VI) removal using sunlight, which demands high energy consumption [69]. With development of hybrid nanocomposite and heterojunction-structured catalysts, the separation efficiency of photogenerated carriers was remarkably improved and therefore promoted photocatalytic performance [8][26][55]. In addition, the surface structure of the photocatalyst itself including defects, vacancies, and heteroatom doping often influences catalytic activity.

2.1. Semiconductor Heterojunction Structure

A heterojunction represents the interface between two different semiconductors with unequal band structure, which can result in band alignments [70]. The energy level difference in semiconductor heterojunction drives the effective separation and migration of photogenerated charges, and therefore improves the photocatalytic ability for water pollution treatment and the degradation of organic pollutants [70][71]. In recent years, heterojunction materials were widely used in the photocatalytic extraction of U(VI) [72][73].
The schematic diagram of electron-hole separation in different types of heterojunctions is presented in Figure 1. According to the relative positions of the band structures of photocatalysts, binary heterojunction photocatalysts can be divided into three types, type I (straddling gap alignment, Figure 1A), type II (staggered gap alignment, Figure 1B), and type III (broken gap alignment, Figure 1C) [56]. Among them, the II-type heterojunction attracted extensive attention due to its unique band structure arrangement, ensuring effective separation of photogenerated charge carriers [74][75]. For example, g-C3N4/TiO2 binary heterojunction showed high U(VI) reduction ability compared with single g-C3N4 or TiO2 during photocatalytic extraction of uranium [26]. The g-C3N4/TiO2 with II-type heterojunction arrangement has a lower recombination rate of photogenerated electrons and holes and higher charge transfer efficiency, which was confirmed by the photoluminescence spectroscopy (PL), photocurrent response, and electrochemical impedance spectroscopy, revealing the origin of the enhancement of the photocatalytic activity. For a niobate/titanate (Nb/TiNFs) heterojunction prepared using a one-step hydrothermal method [16], electrons generated on titanate migrate to the CB of niobate due to their CB offset, which greatly suppresses the recombination of electron-hole pairs. The I-type heterojunction structure of the titanate and niobate composite materials compensates for the low photocatalytic activity of the monomer materials in U(VI) extraction. Moreover, composite materials, such as MoS2@TiO2 [24], MoS2@g-C3N4 [72], ZnS@g-C3N4 [76], CuS/TiO2, and so on, were used as excellent photocatalysts for U(VI) reduction.
Figure 1. Schematic diagram of electron-hole separation in different types of heterojunctions, (A) type-I heterojunction, (B) type-II heterojunction, (C) type-III heterojunction, (D) Z-scheme heterojunction, (E) Schottky heterojunction, and (F) p-n heterojunction.
The direct Z-scheme heterojunction and type II heterojunction have a similar energy band structure arrangement, but the direct Z-scheme heterojunction involves the recombination of electrons from the CB of semiconductor A and holes from the valence band of semiconductor B. This unique internal charge transfer mechanism allows the direct Z-scheme heterojunction to maintain both high oxidation and reduction abilities. Liu et al. [77] recently reported a ZnS/WO3 Z-type heterojunction photocatalyst with excellent visible light photocatalytic reduction performance for U(VI). When the two materials come into contact, electron transfer causes negative charge accumulation on the WO3 side and consumption of negative charge on the ZnS side, resulting in the formation of an internal electric field at the material interface. The internal electric field can serve as a one-way electron channel from WO3 to ZnS. Under illumination, the accumulated e in the CB of WO3 migrates to the contact interface and recombines with the photo-induced h+ in the VB of ZnS, resulting in a long separation lifetime of e. This greatly enhances the photocatalytic performance of the catalyst.
Note that when a metal/semiconductor forms a Schottky junction, the metal will accumulate a large number of electrons or holes. The resulting Schottky barrier will prevent electrons and holes from transferring to the semiconductor, ensuring single one-way transfer of electrons and holes, promoting the separation of photo-generated electrons and holes, and correspondingly improving the photocatalytic performance. Qin et al. [58] synthesized a NiS/CdS composite photocatalyst and demonstrated the existence of an interface Schottky junction between CdS and NiS, boosting spatial charge separation through density functional theory (DFT) calculations for highly efficient photocatalytic reduction in U(VI). The resultant U(VI) extraction efficiency reached 99% within 90 min from the uranium-containing solution. Dai et al. [78] first synthesized a magnetic graphene oxide-modified graphitic carbon nitride (mGO/g-C3N4) nanocomposite material, which can effectively catalyze the reduction in U(VI) from wastewater under visible light irradiation from LEDs, achieving a U(VI) extraction efficiency as high as 96.02%. Wan et al. [79] used S-injected engineering to functionalize the atoms into the TiO2/N-doped hollow carbon sphere (TiO2/NHCS) heterostructure to form Schottky junctions for spatially separating photogenerated electrons and optimizing the TiO2 energy level structure. The results show that the reduction efficiency of U(VI) within 20 min exceeded 90% and the removal rate per unit mass reached 448 mg g−1.

2.2. Defective Semiconductors

In photocatalysis, defect is a vital parameter to be pre-considered for the design of photocatalysts and catalytic performance. Crystallographic defects, which often occur at where the perfect periodic arrangement of atoms or molecules in the crystalline materials is disrupted or broken, inevitably lead to the imperfection of perfect crystal structure and therefore widely exist in all photocatalytic materials and increase active sites and greatly promote photocatalytic performance [80]. For semiconductors, the band structure can be improved by adjusting the defects, and thereby improving their light absorption capacity [59]. In addition, surface defect centers can also act as reactive sites, increasing the effectively active surface area. As one of the most common defects in semiconductor materials, vacancies can improve the photocatalytic performance by adjusting the electronic structure and light absorption capability [81][82]; for example, oxygen vacancy-rich tungsten oxide nanowires (WO3-x) have a narrower bandgap energy and higher charge carrier separation efficiency compared to regular WO3 [83]. DFT calculations further demonstrated that the introduction of oxygen vacancies (OVs) in WO3-x resulted in the spin-polarized state of W 3d electrons in WO3-x, greatly suppressing the recombination of photogenerated electrons and holes. Compared to WO3, WO3-x exhibited higher photocatalytic performance in U(IV) reduction. Hydrothermal reaction of a carbonized bacterial cellulose (BC) with thiourea and sodium molybdate dihydrate afforded a heterojunction-structured BC-MoS2, followed by H2/Ar mixed plasma treatment to generate S-vacancies (SVs) in MoS2 and form BC-MoS2-x heterojunction containing Schottky junction and SVs, which were used as photocatalysts for efficient uranium reduction. The resultant removal rate of uranium over a wide range of U(VI) concentrations was up to 91% [5]. Li et al. constructed an oxygen vacancy (OVs)-rich g-C3N4-CeO2-x heterojunction [84], kinetic characterization, and DFT calculations show that photogenerated electrons were transferred from g-C3N4 to a CeO2-x heterojunction through the built-in electric field generated by the heterojunction and were captured by shallow traps created by surface vacancies, and thereby achieving spatial separation. The separation rate and lifetime of photoinduced carriers were significantly increased, and photocatalytic activity for U(VI) reduction was significantly enhanced (39 times higher than that of g-C3N4).

2.3. Elemental Doping of Semiconductors

Doping can modify the surface structure, light absorption, defects, charge density, and carrier separation efficiency of photocatalytic materials [85]. In recent years, element-doped materials received extensive attention in the field of photocatalytic U(VI) reduction. Wang et al. [86] used non-metallic-doped photocatalysts and carbon-doped boron nitride (BN) BCN nanosheets for photocatalytic uranium reduction. By optimizing composite, calculations of energy gap and density of state of BCN, and experimental date, the results show that the doping in the form of carbon rings could regulate the bandgap and electronic structure by manipulating carbon amount. The introduction of carbon rings improved the surface structure and light absorption capacity of the catalyst, and the extraction rate of U(VI) reached 97.4% under visible light irradiation for 1.5 h. For the Ag-doped CdSe (Ag-CdSe) nanosheet, the doping of Ag resulted in an increase in the density of photogenerated carriers and a narrowed bandgap, while also suppressing the recombination of photogenerated electrons and holes [87]; 3% Ag-CdSe nanosheets reached a removal rate of U(VI) of 96%, which is 1.9 times higher than that of the original CdSe nanosheets (50%). To achieve higher photocatalytic efficiency in the extraction of U(VI), up-conversion Er-doped ZnO nanosheets were used as a photocatalyst [88]. Er doping induced up-conversion properties and suppressed recombination of photogenerated carriers, therefore enhancing light absorption capacity and accelerating U(VI) extraction. At an initial U(VI) concentration of 200 mg L−1, 4% Er-doped ZnO reached a high extraction efficiency of uranium at about 91.8% within 3 min.

2.4. Other Strategies

The band structure, light absorption, and carrier separation efficiency of photocatalysts are some key factors in affecting the photocatalytic performance. However, since the photocatalytic extraction of U(VI) occurs on the surface of the catalyst, optimizing the surface structure of the catalyst is another important method for improving photocatalytic performance. To further enhance the U(VI) extraction ability of carbon nitride photocatalysts, a one-step molten salt method was adopted to prepare a new bifunctional carbon nitride material (CN550) [89]. Compared with g-C3N4, CN550 has a high surface area, good adsorption capacity, and a high photocatalytic activity. More recently, various porous framework materials, such as metal–organic frameworks (MOFs), covalent organic frameworks (COFs), and hydrogen-bonded organic frameworks (HOFs), were regarded as the state-of-the-art materials for photocatalytic uranium extraction due to their high surface area and more active sites. Li et al. [45] proposed a new uranium extraction strategy based on post-synthetically functionalized MOF PCN-222, which is an extremely robust MOF, composed of Zr63-O)43-OH)4(H2O)4(OH)4 clusters and photoactive meso-tetra(4-carboxyphenyl)porphyrin (TCPP) linkers. PCN-222 was treated with aminomethylphosphonic acid and ethanephosphonic acid to afford PN-PCN-222 and P-PCN-222, respectively. The uranium uptake results show that PN-PCN-222 can completely remove uranyl ions in an extremely wide uranyl concentration range in solution and reach a very high absorption capacity at about 1289 mg g−1, breaking the maximum adsorption capacity of previously reported MOF materials. Under visible light irradiation, the photo-induced electrons in the PN-PCN-222 matrix reduce the U(VI) pre-enriched in PN-PCN-222, producing neutral uranium species that disperse the MOF structure, exposing more active sites to capture more U(VI). Overall, the development of photocatalytic strategies for efficient U(VI) extraction is recognized as an efficient, environmentally friendly, and cost-effective approach, while rational design and optimization of photocatalysts made significant progress in photocatalytic technology. At present, many articles describe the design of photocatalysts and the principles of photocatalytic systems in detail, and researchers can obtain more inspiration from them [59][90][91].


  1. Li, P.; Wang, J.; Wang, Y.; Liang, J.; Pan, D.; Qiang, S.; Fan, Q. An overview and recent progress in the heterogeneous photocatalytic reduction of U(VI). J. Photochem. Photobiol. C 2019, 41, 100320.
  2. Wang, J.; Wang, Y.; Wang, W.; Ding, Z.; Geng, R.; Li, P.; Pan, D.; Liang, J.; Qin, H.; Fan, Q. Tunable mesoporous g-C3N4 nanosheets as a metal-free catalyst for enhanced visible-light-driven photocatalytic reduction of U(VI). Chem. Eng. J. 2020, 383, 123193.
  3. Abney, C.W.; Mayes, R.T.; Saito, T.; Dai, S. Materials for the recovery of uranium from seawater. Chem. Rev. 2017, 117, 13935–14013.
  4. Chen, T.; Li, M.; Zhou, L.; Feng, X.; Lin, D.; Ding, X.; Li, C.; Yan, R.; Duan, T.; He, R.; et al. Harmonizing the energy band between adsorbent and semiconductor enables efficient uranium extraction. Chem. Eng. J. 2021, 420, 127645.
  5. Chen, T.; Liu, B.; Li, M.; Zhou, L.; Lin, D.; Ding, X.; Lian, J.; Li, J.; He, R.; Duan, T.; et al. Efficient uranium reduction of bacterial cellulose-MoS2 heterojunction via the synergistically effect of Schottky junction and S-vacancies engineering. Chem. Eng. J. 2021, 406, 126791.
  6. Song, S.; Huang, S.; Zhang, R.; Chen, Z.; Wen, T.; Wang, S.; Hayat, T.; Alsaedi, A.; Wang, X. Simultaneous removal of U(VI) and humic acid on defective TiO2−x investigated by batch and spectroscopy techniques. Chem. Eng. J. 2017, 325, 576–587.
  7. Li, Z.-J.; Huang, Z.-W.; Guo, W.-L.; Wang, L.; Zheng, L.-R.; Chai, Z.-F.; Shi, W.-Q. Enhanced photocatalytic removal of uranium (VI) from aqueous solution by magnetic TiO2/Fe3O4 and its graphene composite. Environ. Sci. Technol. 2017, 51, 5666–5674.
  8. Zhu, M.; Cai, Y.; Liu, S.; Fang, M.; Tan, X.; Liu, X.; Kong, M.; Xu, W.; Mei, H.; Hayat, T. K2Ti6O13 hybridized graphene oxide: Effective enhancement in photodegradation of RhB and photoreduction of U(VI). Environ. Pollut. 2019, 248, 448–455.
  9. Li, P.; Wang, J.; Wang, Y.; Liang, J.; He, B.; Pan, D.; Fan, Q.; Wang, X. Photoconversion of U(VI) by TiO2: An efficient strategy for seawater uranium extraction. Chem. Eng. J. 2019, 365, 231–241.
  10. Wu, L.; Yang, X.; Chen, T.; Li, Y.; Meng, Q.; Zhu, L.; Zhu, W.; He, R.; Duan, T. Three-dimensional C3N5/RGO aerogels with enhanced visible-light response and electron-hole separation efficiency for photocatalytic uranium reduction. Chem. Eng. J. 2022, 427, 131773.
  11. Guo, Y.; Li, L.; Li, Y.; Li, Z.; Wang, X.; Wang, G. Adsorption and photocatalytic reduction activity of uranium (VI) on zinc oxide/rectorite composite enhanced with methanol as sacrificial organics. J. Radioanal. Nucl. Chem. 2016, 310, 883–890.
  12. Hu, L.; Yan, X.-W.; Zhang, X.-J.; Shan, D. Integration of adsorption and reduction for uranium uptake based on SrTiO3/TiO2 electrospun nanofibers. Appl. Surf. Sci. 2018, 428, 819–824.
  13. Dutta, D.P.; Nath, S. Low cost synthesis of SiO2/C nanocomposite from corn cobs and its adsorption of uranium (VI), chromium (VI) and cationic dyes from wastewater. J. Mol. Liq. 2018, 269, 140–151.
  14. Lu, C.; Zhang, P.; Jiang, S.; Wu, X.; Song, S.; Zhu, M.; Lou, Z.; Li, Z.; Liu, F.; Liu, Y.; et al. Photocatalytic reduction elimination of UO22+ pollutant under visible light with metal-free sulfur doped g-C3N4 photocatalyst. Appl. Catal. B 2017, 200, 378–385.
  15. Wang, H.; Guo, H.; Zhang, N.; Chen, Z.; Hu, B.; Wang, X. Enhanced photoreduction of U(VI) on C3N4 by Cr(VI) and bisphenol A: ESR, XPS, and EXAFS investigation. Environ. Sci. Technol. 2019, 53, 6454–6461.
  16. Liu, X.; Du, P.; Pan, W.; Dang, C.; Qian, T.; Liu, H.; Liu, W.; Zhao, D. Immobilization of uranium (VI) by niobate/titanate nanoflakes heterojunction through combined adsorption and solar-light-driven photocatalytic reduction. Appl. Catal. B 2018, 231, 11–22.
  17. Yu, C.; Zhang, Z.; Dong, Z.; Xiong, Y.; Wang, Y.; Liu, Y.; Cao, X.; Dong, W.; Liu, M.; Liu, Y. Fabrication of heterostructured CdS/TiO2 nanotube arrays composites for photoreduction of U(VI) under visible light. J. Solid State Chem. 2021, 298, 122053.
  18. Chen, T.; Zhang, J.; Ge, H.; Li, M.; Li, Y.; Duan, T.; He, R.; Zhu, W. Efficient extraction of uranium in organics-containing wastewater over g-C3N4/GO hybrid nanosheets with type-II band structure. J. Hazard. Mater. 2020, 384, 121383.
  19. Zhang, H.; Dai, Z.; Sui, Y.; Xue, J.; Ding, D. Adsorption of U(VI) from aqueous solution by magnetic core–dual shell Fe3O4@2. J. Radioanal. Nucl. Chem. 2018, 317, 613–624.
  20. Dai, Z.; Zhen, Y.; Sun, Y.; Li, L.; Ding, D. ZnFe2O4/g-C3N4 S-scheme photocatalyst with enhanced adsorption and photocatalytic activity for uranium (VI) removal. Chem. Eng. J. 2021, 415, 129002.
  21. Huang, X.; Xiao, J.; Mei, P.; Wang, H.; Ishag, A.; Sun, Y. The Synthesis of Z-Scheme MoS2/g-C3N4 Heterojunction for Enhanced Visible-Light-Driven Photoreduction of Uranium. Catal. Lett. 2022, 152, 1981–1989.
  22. Ke, L.; Li, P.; Wu, X.; Jiang, S.; Luo, M.; Liu, Y.; Le, Z.; Sun, C.; Song, S. Graphene-like sulfur-doped g-C3N4 for photocatalytic reduction elimination of UO22+ under visible Light. Appl. Catal. B 2017, 205, 319–326.
  23. Deng, H.; Li, Z.-J.; Wang, L.; Yuan, L.-Y.; Lan, J.-H.; Chang, Z.-Y.; Chai, Z.-F.; Shi, W.-Q. Nanolayered Ti3C2 and SrTiO3 composites for photocatalytic reduction and removal of uranium (VI). ACS Appl. Nano Mater. 2019, 2, 2283–2294.
  24. Rao, G.; Liu, X.; Liu, P. Fabrication of MoS2@TiO2 hollow-sphere heterostructures with enhanced visible light photocatalytic reduction of U(VI). J. Radioanal. Nucl. Chem. 2022, 331, 263–273.
  25. Niu, Y.; Lu, Z.; Li, J.; Jiang, J.; Lu, J.; Wu, K. Low-cost synthesis of cellular materials with preformed foam for uranium (VI) adsorption. Mater. Lett. 2019, 247, 36–39.
  26. Jiang, X.-H.; Xing, Q.-J.; Luo, X.-B.; Li, F.; Zou, J.-P.; Liu, S.-S.; Li, X.; Wang, X.-K. Simultaneous photoreduction of Uranium (VI) and photooxidation of Arsenic (III) in aqueous solution over g-C3N4/TiO2 heterostructured catalysts under simulated sunlight irradiation. Appl. Catal. B 2018, 228, 29–38.
  27. Lee, S.; Kang, U.; Piao, G.; Kim, S.; Han, D.S.; Park, H. Homogeneous photoconversion of seawater uranium using copper and iron mixed-oxide semiconductor electrodes. Appl. Catal. B 2017, 207, 35–41.
  28. Liang, P.; Yuan, L.; Du, K.; Wang, L.; Li, Z.; Deng, H.; Wang, X.; Luo, S.-Z.; Shi, W. Photocatalytic reduction of uranium (VI) under visible light with 2D/1D Ti3C2/CdS. Chem. Eng. J. 2021, 420, 129831.
  29. Feng, J.; Yang, Z.; He, S.; Niu, X.; Zhang, T.; Ding, A.; Liang, H.; Feng, X. Photocatalytic reduction of Uranium (VI) under visible light with Sn-doped In2S3 microspheres. Chemosphere 2018, 212, 114–123.
  30. Yu, F.; Yu, Z.; Xu, Z.; Xiong, J.; Fan, Q.; Feng, X.; Tao, Y.; Hua, J.; Luo, F. Heteroatom engineering of polymeric carbon nitride heterojunctions for boosting photocatalytic reduction of hexavalent uranium. Mol. Syst. Des. Eng. 2020, 5, 882–889.
  31. Wang, G.; Zhen, J.; Zhou, L.; Wu, F.; Deng, N. Adsorption and photocatalytic reduction of U (VI) in aqueous TiO2 suspensions enhanced with sodium formate. J. Radioanal. Nucl. Chem. 2015, 304, 579–585.
  32. Lu, C.; Chen, R.; Wu, X.; Fan, M.; Liu, Y.; Le, Z.; Jiang, S.; Song, S. Boron doped g-C3N4 with enhanced photocatalytic UO22+ reduction performance. Appl. Surf. Sci. 2016, 360, 1016–1022.
  33. Le, Z.; Xiong, C.; Gong, J.; Wu, X.; Pan, T.; Chen, Z.; Xie, Z. Self-cleaning isotype g-C3N4 heterojunction for efficient photocatalytic reduction of hexavalent uranium under visible light. Environ. Pollut. 2020, 260, 114070.
  34. Zhong, X.; Liu, Y.; Wang, S.; Zhu, Y.; Hu, B. In-situ growth of COF on BiOBr 2D material with excellent visible-light-responsive activity for U(VI) photocatalytic reduction. Sep. Purif. Technol. 2021, 279, 119627.
  35. Li, S.; Yang, X.; Cui, Z.; Xu, Y.; Niu, Z.; Li, P.; Pan, D.; Wu, W. Efficient photoreduction strategy for uranium immobilization based on graphite carbon nitride/perovskite oxide heterojunction nanocomposites. Appl. Catal. B 2021, 298, 120625.
  36. Qiu, M.; Liu, Z.; Wang, S.; Hu, B. The photocatalytic reduction of U (VI) into U (IV) by ZIF-8/g-C3N4 composites at visible light. Environ. Res. 2021, 196, 110349.
  37. Zhang, Y.; Zhu, M.; Zhang, S.; Cai, Y.; Lv, Z.; Fang, M.; Tan, X.; Wang, X. Highly efficient removal of U(VI) by the photoreduction of SnO2/CdCO3/CdS nanocomposite under visible light irradiation. Appl. Catal. B 2020, 279, 119390.
  38. Lei, J.; Liu, H.; Wen, F.; Jiang, X.; Yuan, C.; Chen, Q.; Liu, J.-A.; Cui, X.; Yang, F.; Zhu, W.; et al. Tellurium nanowires wrapped by surface oxidized tin disulfide nanosheets achieves efficient photocatalytic reduction of U(VI). Chem. Eng. J. 2021, 426, 130756.
  39. He, S.; Yang, Z.; Cui, X.; Zhang, X.; Niu, X. Fabrication of the novel Ag-doped SnS2@ InVO4 composite with high adsorption-photocatalysis for the removal of uranium (VI). Chemosphere 2020, 260, 127548.
  40. Yan, Z.-Y.; Xi, H.-L.; Yuan, L.-Y. Metal organic framework MIL-53 (Fe) as a photocatalyst for visible-light catalytic reduction of U(Ⅵ) in aqueous solution. Huan Jing Ke Xue-Huanjing Kexue 2019, 40, 1819–1825.
  41. Chen, J.; Ollis, D.F.; Rulkens, W.H.; Bruning, H. Photocatalyzed deposition and concentration of soluble uranium (VI) from TiO2 suspensions. Colloid Surf. A 1999, 151, 339–349.
  42. Dong, C.; Qiao, T.; Huang, Y.; Yuan, X.; Lian, J.; Duan, T.; Zhu, W.; He, R. Efficient photocatalytic extraction of uranium over ethylenediamine capped cadmium sulfide telluride nanobelts. ACS Appl. Mater. Inter. 2021, 13, 11968–11976.
  43. Wang, Z.; Liu, H.; Lei, Z.; Huang, L.; Wu, T.; Liu, S.; Ye, G.; Lu, Y.; Wang, X. Graphene aerogel for photocatalysis-assist uranium elimination under visible light and air atmosphere. Chem. Eng. J. 2020, 402, 126256.
  44. Kim, Y.K.; Lee, S.; Ryu, J.; Park, H. Solar conversion of seawater uranium (VI) using TiO2 electrodes. Appl. Catal. B 2015, 163, 584–590.
  45. Li, H.; Zhai, F.; Gui, D.; Wang, X.; Wu, C.; Zhang, D.; Dai, X.; Deng, H.; Su, X.; Diwu, J.; et al. Powerful uranium extraction strategy with combined ligand complexation and photocatalytic reduction by postsynthetically modified photoactive metal-organic frameworks. Appl. Catal. B 2019, 254, 47–54.
  46. Yu, F.; Zhu, Z.; Wang, S.; Peng, Y.; Xu, Z.; Tao, Y.; Xiong, J.; Fan, Q.; Luo, F. Tunable perylene-based donor-acceptor conjugated microporous polymer to significantly enhance photocatalytic uranium extraction from seawater. Chem. Eng. J. 2021, 412, 127558.
  47. Li, P.; Wang, J.; Wang, Y.; Dong, L.; Wang, W.; Geng, R.; Ding, Z.; Luo, D.; Pan, D.; Liang, J.; et al. Ultrafast recovery of aqueous uranium: Photocatalytic U(VI) reduction over CdS/g-C3N4. Chem. Eng. J. 2021, 425, 131552.
  48. Hu, Y.; Tang, D.; Shen, Z.; Yao, L.; Zhao, G.; Wang, X. Photochemically triggered self-extraction of uranium from aqueous solution under ambient conditions. Appl. Catal. B 2023, 322, 122092.
  49. Wang, Z.; Li, B.; Shang, H.; Dong, X.; Huang, L.; Qing, Q.; Xu, C.; Chen, J.; Liu, H.; Wang, X.; et al. Photo-induced removal of uranium under air without external photocatalysts. Green Chem. 2022, 24, 7092–7099.
  50. Tatarchuk, T.; Shyichuk, A.; Mironyuk, I.; Naushad, M. A review on removal of uranium (VI) ions using titanium dioxide based sorbents. J. Mol. Liq. 2019, 293, 111563.
  51. Bonato, M.; Allen, G.; Scott, T. Reduction of U(VI) to U(IV) on the surface of TiO2 anatase nanotubes. Micro Nano Lett. 2008, 3, 57–61.
  52. Litter, M.I. Last advances on TiO2-photocatalytic removal of chromium, uranium and arsenic. Curr. Opin. Green Sustain. 2017, 6, 150–158.
  53. Miyake, C.; Nakase, T.; Sano, Y. EPR study of uranium (V) species in photo-and electrolytic reduction processes of UO2(NO3)2-2TBP. J. Nucl. Sci. Technol. 1993, 30, 1256–1260.
  54. Salomone, V.N.; Meichtry, J.M.; Zampieri, G.; Litter, M.I. New insights in the heterogeneous photocatalytic removal of U(VI) in aqueous solution in the presence of 2-propanol. Chem. Eng. J. 2015, 261, 27–35.
  55. Guo, Y.; Guo, Y.; Wang, X.; Li, P.; Kong, L.; Wang, G.; Li, X.; Liu, Y. Enhanced photocatalytic reduction activity of uranium (vi) from aqueous solution using the Fe2O3–graphene oxide nanocomposite. Dalton Trans. 2017, 46, 14762–14770.
  56. Lei, J.; Liu, H.; Yuan, C.; Chen, Q.; Liu, J.-A.; Wen, F.; Jiang, X.; Deng, W.; Cui, X.; Duan, T.; et al. Enhanced photoreduction of U(VI) on WO3 nanosheets by oxygen defect engineering. Chem. Eng. J. 2021, 416, 129164.
  57. Cheng, L.; Xiang, Q.; Liao, Y.; Zhang, H. CdS-based photocatalysts. Energy Environ. Sci. 2018, 11, 1362–1391.
  58. Qin, Z.; Yang, C.; Shuai, W.; Jin, J.; Tang, X.; Chen, F.; Shi, T.; Ye, Y.; Liang, Y.; Wang, Y. interfacial Schottky junction boosting spatial charge separation for highly efficient photocatalytic reduction of U(VI). Sep. Purif. Technol. 2023, 307, 122816.
  59. Chen, T.; Yu, K.; Dong, C.; Yuan, X.; Gong, X.; Lian, J.; Cao, X.; Li, M.; Zhou, L.; Hu, B.; et al. Advanced photocatalysts for uranium extraction: Elaborate design and future perspectives. Coord. Chem. Rev. 2022, 467, 214615.
  60. Chen, L.; Hang, J.; Chen, B.; Kang, J.; Yan, Z.; Wang, Z.; Zhang, Y.; Chen, S.; Wang, Y.; Jin, Y.; et al. Photocatalytic uranium removal from basic effluent by porphyrin-Ni COF as the photocatalyst. Chem. Eng. J. 2023, 454, 140378.
  61. Chen, Z.; Wang, J.; Hao, M.; Xie, Y.; Liu, X.; Yang, H.; Waterhouse, G.I.; Wang, X.; Ma, S. Tuning excited state electronic structure and charge transport in covalent organic frameworks for enhanced photocatalytic performance. Nat. Commun. 2023, 14, 1106.
  62. Liu, N.; Zhang, H.; Liu, Q.; Zhu, J.; Chen, R.; Yu, J.; Li, Y.; Li, R.; Wang, J. Magnetron sputtering ultra-thin TiO2 films for photocatalytic reduction of uranium. Desalination 2022, 543, 116121.
  63. Amadelli, R.; Maldotti, A.; Sostero, S.; Carassiti, V. Photodeposition of uranium oxides onto TiO2 from aqueous uranyl solutions. J. Chem. Soc. 1991, 87, 3267–3273.
  64. Lyulyukin, M.; Filippov, T.; Cherepanova, S.; Solovyeva, M.; Prosvirin, I.; Bukhtiyarov, A.; Kozlov, D.; Selishchev, D. Synthesis, characterization and visible-light photocatalytic activity of solid and TiO2-supported uranium oxycompounds. Nanomaterials 2021, 11, 1036.
  65. Gong, X.; Tang, L.; Zou, J.; Guo, Z.; Li, Y.; Lei, J.; Liu, H.; Liu, M.; Zhou, L.; Huang, P.; et al. Introduction of cation vacancies and iron doping into TiO2 enabling efficient uranium photoreduction. J. Hazard. Mater. 2022, 423, 126935.
  66. Wang, Q.; Yang, G. Unraveling the photocatalytic mechanisms for U(VI) reduction by TiO2. Mol. Catal. 2022, 533, 112770.
  67. Xu, Y.; Zhang, H.; Liu, Q.; Liu, J.; Chen, R.; Yu, J.; Zhu, J.; Li, R.; Wang, J. Surface hybridization of π-conjugate structure cyclized polyacrylonitrile and radial microsphere shaped TiO2 for reducing U(VI) to U(IV). J. Hazard. Mater. 2021, 416, 125812.
  68. Garcia-Segura, S.; Brillas, E. Applied photoelectrocatalysis on the degradation of organic pollutants in wastewaters. J. Photochem. Photobiol. C 2017, 31, 1–35.
  69. Ye, Y. Micropollutant Degradation in Water by Photochemical Processes. Ph.D. Thesis, Wageningen University and Research, Wageningen, The Netherlands, 2018.
  70. Low, J.; Yu, J.; Jaroniec, M.; Wageh, S.; Al-Ghamdi, A.A. Heterojunction photocatalysts. Adv. Mater. 2017, 29, 1601694.
  71. Wang, Z.; Lin, Z.; Shen, S.; Zhong, W.; Cao, S. Advances in designing heterojunction photocatalytic materials. Chin. J. Catal. 2021, 42, 710–730.
  72. Zhang, Z.; Liu, C.; Dong, Z.; Dai, Y.; Xiong, G.; Liu, Y.; Wang, Y.; Wang, Y.; Liu, Y. Synthesis of flower-like MoS2/g-C3N4 nanosheet heterojunctions with enhanced photocatalytic reduction activity of uranium (VI). Appl. Surf. Sci. 2020, 520, 146352.
  73. Zhang, Y.; Sun, H.; Gao, F.; Zhang, S.; Han, Q.; Li, J.; Fang, M.; Cai, Y.; Hu, B.; Tan, X.; et al. Insights into photothermally enhanced photocatalytic U(VI) extraction by a step-scheme heterojunction. Research 2022, 2022, 9790320.
  74. Kumar, A.; Khan, M.; He, J.; Lo, I.M. Recent developments and challenges in practical application of visible–light–driven TiO2–based heterojunctions for PPCP degradation: A critical review. Water Res. 2020, 170, 115356.
  75. Yao, X.; Chen, L.; Liu, M.; Feng, D.; Wang, C.; Lu, F.; Wang, W.; Wang, X.; Cheng, Y.; Liu, H.; et al. Rational design of Si/TiO2 heterojunction photocatalysts: Transfer matrix method. Appl. Catal. B 2018, 221, 70–76.
  76. Wu, F.; Zhang, Z.; Cheng, Z.; Zhou, R.; Lin, Y.; Liu, Y.; Wang, Y.; Cao, X.; Liu, M.; Liu, Y. The enhanced photocatalytic reduction of uranium (VI) by 3N4 heterojunctions under sunlight. J. Radioanal. Nucl. Chem. 2021, 329, 1125–1133.
  77. Liu, N.; Li, R.; Zhu, J.; Liu, Q.; Chen, R.; Yu, J.; Li, Y.; Zhang, H.; Wang, J. Z-scheme heterojunction ZnS/WO3 composite: Photocatalytic reduction of uranium and band gap regulation mechanism. J. Colloid Interface Sci. 2023, 630, 727–737.
  78. Dai, Z.; Sun, Y.; Zhang, H.; Ding, D.; Li, L. Photocatalytic reduction of U(VI) in wastewater by mGO/g-C3N4 nanocomposite under visible LED light irradiation. Chemosphere 2020, 254, 126671.
  79. Wan, H.; Li, Y.; Wang, M.; Zhao, Q.; Fu, Y.; Chen, Y.; He, P.; Wu, L.; Meng, Q.; Ma, T.; et al. Boosting efficient U(VI) immobilization via synergistic Schottky heterojunction and hierarchical atomic-level injected engineering. Chem. Eng. J. 2022, 430, 133139.
  80. Bai, S.; Zhang, N.; Gao, C.; Xiong, Y. Defect engineering in photocatalytic materials. Nano Energy 2018, 53, 296–336.
  81. Xue, J.; Fujitsuka, M.; Majima, T. Defect-mediated electron transfer in photocatalysts. Chem. Commun. 2021, 57, 3532–3542.
  82. Zhou, W.; Fu, H. Defect-mediated electron–hole separation in semiconductor photocatalysis. Inorg. Chem. Front. 2018, 5, 1240–1254.
  83. Yang, X.; Li, F.; Liu, W.; Chen, L.; Qi, J.; Sun, W.; Pan, F.; Duan, T.; Sun, F. Oxygen vacancy-induced spin polarization of tungsten oxide nanowires for efficient photocatalytic reduction and immobilization of uranium (VI) under simulated solar light. Appl. Catal. B 2023, 324, 122202.
  84. Li, S.; Pan, D.; Cui, Z.; Xu, Y.; Shang, H.; Hua, W.; Wu, F.; Wu, W. Synergistic effects of oxygen vacancies and heterostructures for visible-light-driven photoreduction of uranium. Sep. Purif. Technol. 2022, 301, 121966.
  85. Devi, L.G.; Kavitha, R. A review on non metal ion doped titania for the photocatalytic degradation of organic pollutants under UV/solar light: Role of photogenerated charge carrier dynamics in enhancing the activity. Appl. Catal. B 2013, 140, 559–587.
  86. Wang, Y.; Chen, G.; Weng, H.; Wang, L.; Chen, J.; Cheng, S.; Zhang, P.; Wang, M.; Ge, X.; Chen, H.; et al. Carbon-doped boron nitride nanosheets with adjustable band structure for efficient photocatalytic U(VI) reduction under visible light. Chem. Eng. J. 2021, 410, 128280.
  87. Li, G.; Dong, C.; Sun, G.; Li, M.; Cao, X.; Zhou, L.; Chen, T.; Yang, F. Ag-doped CdSe nanosheets as photocatalysts for uranium reduction. ACS Appl. Nano Mater. 2022, 5, 16178–16187.
  88. Gong, X.; Tang, L.; Wang, R.; Guo, Z.; Huang, P.; Zhou, L.; Zou, J.; Lei, J.; Liu, H.; Li, N.; et al. Achieving efficient photocatalytic uranium extraction within a record short period of 3 min by Up-conversion erbium doped ZnO nanosheets. Chem. Eng. J. 2022, 450, 138044.
  89. Liu, S.; Wang, Z.; Lu, Y.; Li, H.; Chen, X.; Wei, G.; Wu, T.; Maguire, D.-J.; Ye, G.; Chen, J. Sunlight-induced uranium extraction with triazine-based carbon nitride as both photocatalyst and adsorbent. Appl. Catal. B 2021, 282, 119523.
  90. Ye, Y.; Jin, J.; Chen, F.; Dionysiou, D.D.; Feng, Y.; Liang, B.; Cheng, H.-Y.; Qin, Z.; Tang, X.; Li, H.; et al. Removal and recovery of aqueous U(VI) by heterogeneous photocatalysis: Progress and challenges. Chem. Eng. J. 2022, 450, 138317.
  91. Wu, Y.; Xie, Y.; Liu, X.; Li, Y.; Wang, J.; Chen, Z.; Yang, H.; Hu, B.; Shen, C.; Tang, Z.; et al. Functional nanomaterials for selective uranium recovery from seawater: Material design, extraction properties and mechanisms. Coord. Chem. Rev. 2023, 483, 215097.
Contributors MDPI registered users' name will be linked to their SciProfiles pages. To register with us, please refer to : , , , ,
View Times: 356
Revisions: 3 times (View History)
Update Date: 02 Aug 2023
Video Production Service