“…On the basic of various characterization and experimental results, a possible mechanism photodegrading CIP and LEV of 20% Bi-Bi 2 WO 6 /BiOI heterojunctions was proposed, as indicated in Figure 12. The Fermi level of Bi 0 (approximately -0.17 eV) is more negative than the CB independent of Bi 2 WO 6 and BiOI, so the photogenerated charge of Bi 0 can be easily transferred to BiOI or Bi 2 WO 6 [64]. According to literature reports, Bi 2 WO 6 is a typical n-type semiconductor, and BiOI is a typical p-type semiconductor, and the combination between n-type Bi 2 WO 6 and p-type BiOI will result in the formation of p-n heterojunc-tions [65].…”
A flower-like metallic Bi-modified Bi2WO6/BiOI heterojunction was fabricated by a two-step approach of hydrothermal method and in situ ethylene glycol reduction method. The ternary system was confirmed by structural analysis and surface and morphological studies. Compared with Bi2WO6, BiOI, and their binary nanomaterials, the catalyst exhibits excellent photocatalytic performance for the degradation of ciprofloxacin (CIP) and levofloxacin (LEV) under visible light irradiation. The improvement of photocatalytic performance was ascribed to the synergistic effect between metal Bi nanoparticles and Bi2WO6/BiOI p-n heterojunction, which enhanced the light absorption capacity and the separation efficiency of photogenerated carriers. By studying the effect of solution pH on CIP degradation, it was found that when
pH
=
10
, the degradation efficiency of the catalyst on ciprofloxacin reached 100% within 40 min. It provides a new idea for the design and synthesis of ternary photocatalysts for purification of alkaline domestic sewage.
“…On the basic of various characterization and experimental results, a possible mechanism photodegrading CIP and LEV of 20% Bi-Bi 2 WO 6 /BiOI heterojunctions was proposed, as indicated in Figure 12. The Fermi level of Bi 0 (approximately -0.17 eV) is more negative than the CB independent of Bi 2 WO 6 and BiOI, so the photogenerated charge of Bi 0 can be easily transferred to BiOI or Bi 2 WO 6 [64]. According to literature reports, Bi 2 WO 6 is a typical n-type semiconductor, and BiOI is a typical p-type semiconductor, and the combination between n-type Bi 2 WO 6 and p-type BiOI will result in the formation of p-n heterojunc-tions [65].…”
A flower-like metallic Bi-modified Bi2WO6/BiOI heterojunction was fabricated by a two-step approach of hydrothermal method and in situ ethylene glycol reduction method. The ternary system was confirmed by structural analysis and surface and morphological studies. Compared with Bi2WO6, BiOI, and their binary nanomaterials, the catalyst exhibits excellent photocatalytic performance for the degradation of ciprofloxacin (CIP) and levofloxacin (LEV) under visible light irradiation. The improvement of photocatalytic performance was ascribed to the synergistic effect between metal Bi nanoparticles and Bi2WO6/BiOI p-n heterojunction, which enhanced the light absorption capacity and the separation efficiency of photogenerated carriers. By studying the effect of solution pH on CIP degradation, it was found that when
pH
=
10
, the degradation efficiency of the catalyst on ciprofloxacin reached 100% within 40 min. It provides a new idea for the design and synthesis of ternary photocatalysts for purification of alkaline domestic sewage.
“…Q. Wang et al (2019) prepared a Bi-modified BiOI-Bi 2 O 3 heterojunction using an in situ reduction method applying UV light with BiOI-Bi 2 O 3 previously prepared by single immersion at room temperature method reported by Cong et al (2017) . Using high-resolution transmission electron microscopy (HRTEM), the morphology of the Bi/BiOI-Bi 2 O 3 film was investigated; results, showed that the Bi 0 (012) planes and BiOI (110) planes were predominant, where Bi 0 was in direct contact with BiOI.…”
An important target of photoelectrocatalysis (PEC) technology is the development of semiconductor-based photoelectrodes capable of absorbing solar energy (visible light) and promoting oxidation and reduction reactions. Bismuth oxyhalide-based materials BiOX (X = Cl, Br, and I) meet these requirements. Their crystalline structure, optical and electronic properties, and photocatalytic activity under visible light mean that these materials can be coupled to other semiconductors to develop novel heterostructures for photoelectrochemical degradation systems. This review provides a general overview of controlled BiOX powder synthesis methods, and discusses the optical and structural features of BiOX-based materials, focusing on heterojunction photoanodes. In addition, it summarizes the most recent applications in this field, particularly photoelectrochemical performance, experimental conditions and degradation efficiencies reported for some organic pollutants (e.g., pharmaceuticals, organic dyes, phenolic derivatives, etc.). Finally, as this review seeks to serve as a guide for the characteristics and various properties of these interesting semiconductors, it discusses future PEC-related challenges to explore.
“…Unfortunately, the narrow band gap of BiOI and the fast recombination rate of photogenerated electron-hole carriers largely limit its practical application. 16 To address these questions, a series of strategies, such as heteroatom doping, 17 morphology control, 18 vacancy engineering, 18 surface functionalization, 19 and especially heterojunction construction, 20 for example, BiOI/CdS, 21 BiOI/ g-C 3 N 4 , 22 BiOI/Bi 2 O 3 , 23 BiOI/WO 3 , 24 BiOI/BiOX (X = Cl, Br) 25,26 have been developed to improve the catalytic performance of BiOI. However, most of these inorganic semiconductors lack porosity 27 and are coagulating rather than dispersing in wastewater, 28 which induce kinetic shielding and hampers the diffusion of molecular reactants and products.…”
Herein, a series of crystalline Z-scheme photocatalytic heterojunctions BiOI@PCN-222 (BP-X, X donates Zr6:Bi, X = 1, 3 and 5) is constructed by highly dispersed integration of BiOI into the channel...
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