Novel Photocatalyst(新型光触媒)研究综述
Novel Photocatalyst 新型光触媒 - Synthesis conditions for the novel photocatalyst, including calcination temperature and copper loading, were varied before photocatalysis to obtain at the optimal reaction efficiency. [1] Indeed, a series of experiments were carried out in a continuous planar reactor using a novel photocatalyst/TiO2 technology with metal wires e. [2] A novel photocatalyst was developed by combining TiO2 (P25), reduced graphene oxide (rGO), and multi-core@shell clustered carbon dots (CDs) by one-step hydrothermal method for the high efficiency visible-light degradation of organic dyes and antibacterial application. [3] Recent advancements in the synthesis and fundamental physical/mechanistic studies of novel photocatalysts for hydrogen evolution from biomass conversion are summarized. [4] coli using LF as a novel photocatalyst was successfully demonstrated as an alternative and promising method for disinfection purposes. [5] The Mo/Bi2MoO6/Bi3ClO4 nanocomposite as a novel photocatalyst not only exhibited an excellent visible-light photocatalytic desulfurization performance of thiophene (~97%), but also had better photodesulfurization efficiency than Mo/Bi2MoO6 and Bi3ClO4 nanostructures. [6] We suggest that the MoS2 heterophase boundary can serve as a novel photocatalyst. [7] Hence, the design and synthesis of novel photocatalysts based on g-C3N4 is a prosperous approach towards water and wastewater treatment, especially against pollutants of organic nature. [8] Novel photocatalysts based on combination of suitable metals or metal oxides have been developed to facilitate photogeneration of electrons over a wider spectral range for complete mineralization. [9] Recently, we have witnessed a booming development of composites and multi-dopant metal oxides to be employed as novel photocatalysts. [10] To this end, the fabrication of novel photocatalysts with unique electrochemical properties and high catalytic efficiency is of utmost importance and requires adequate attention. [11] The search of novel photocatalysts active under solar radiation has been object of extensive work over the last decades. [12] Hence, photoreduction of Cr(VI) to Cr(III) and degradation of rhodamine B (RhB) using a novel photocatalyst is particularly important. [13] It is hoped that this review will provide a broad picture and inspire the exploration of novel photocatalysts for efficient NH3 production. [14] This work not only paves the way towards stable PTC materials but also provides new insights into the design of novel photocatalysts. [15] In particular, it was realized that future work needs to be directed towards the synthesis of novel photocatalysts or the development of reaction conditions that minimize or completely inhibit photo-corrosion, one of the major issues faced during the light-driven production of H2 from H2S in the presence of several photocatalysts. [16] BACKGROUND This research introduces the application of a novel photocatalyst including Co3O@SiO2@TiO2-Ag nanocomposite with highly photocatalytic stability and core-shell structure for the removal of toxic methyl violet from aqueous solution. [17] The design of antenna–reactor photocatalysts has become a powerful strategy to covert transition metal reactors from traditional thermocatalysts to novel photocatalysts. [18] Both non-metallic g-C3N4 and BiVO4 are novel photocatalysts responsive to visible light, but their low charge separation efficiency restricts their inconspicuous photocatalytic activity. [19] In this work, a novel photocatalyst, MoS2/SnIn4S8, was synthesized through hydrothermal method by introducing few-layer MoS2 nanosheets and then employed to establish an integrated photocatalytic reduction/oxidation system for the remediation of TBBPA under visible light. [20] In this study, novel photocatalysts MVO4/g-C3N4 (M = La, Gd) were prepared by the hydrothermal method, through which different loading amounts of 10–50%MVO4 and g-C3N4 were mixed and ultrasonically oscillated to gain heterojunction catalysts. [21] Design and preparation of a novel photocatalyst, based on polyhydromethylsiloxane (PHMS) was reported. [22] It is anticipated that the present work can facilitate the development of novel photocatalysts for selective oxidation based on ·CO3−. [23] However, the expeditious discovery of novel photocatalysts and synthetic pathways remains challenging. [24] Modification and bandgap engineering are proposed to be extremely significant in improving the photocatalytic activity of novel photocatalysts. [25] coli can be effectively removed by the novel photocatalyst under LED light illumination. [26] The present work offers a unique synthesis strategy to develop the novel photocatalyst with efficient photocatalytic performance. [27] The investigation may lead to the development of novel photocatalyst for the degradation of toxic dye which is discharged into sewage from various chemical industries. [28] Herein, novel photocatalysts are reported through coupling Sb2MoO6 with g-C3N4 nanotube (abbreviated as GCN nanotube) by a simple reflux method. [29] A novel photocatalyst of Fe3O4/ZnO nanoparticles embedded carboxylate-rich carbon (Fe3O4/ZnO/CRC) was developed, and its photocatalytic activity was evaluated for the degradation of crystal violet (CV) under natural sunlight. [30] Recently, we have witnessed a booming development of composites and multi-dopant metal oxides to be employed as novel photocatalysts. [31] The superior reusability and structural stability further indicated the MXene-based novel photocatalyst is promising for application in environmental remediation. [32] Ps-FNPs have been extensively studied for photocatalytic activity test against Rhodamine B, Methylene blue and nigrosine showed potential dye degradation in the presence of sunlight proved to be novel photocatalysts. [33] This outcome provides a new route for the design of novel photocatalysts with improved efficiency and selectivity. [34] This novel photocatalyst with modulated charge transfer was prepared by hydrothermal treatment and subsequent cation-exchange reactions. [35] In this work, a novel photocatalyst, Ce0. [36] This investigation opens up the possibility of adopting ACN-coated DMSTNs as novel photocatalysts for energy conversion in visible light environment. [37] Herein, a series of novel photocatalysts with Type-II In2S3/bismuth molybdate (Bi2MoO6) heterostructures were handily fabricated through hydrothermal route. [38] A novel photocatalyst was successfully synthesized by immobilizing hydrated titanium dioxide (HTO) nanoparticle within rice straw (RS) via a sol–gel method. [39] Here, we propose a novel photocatalyst of europium doped calcium titanate (Eu:CaTiO3) were synthesized by simple sol–gel method. [40] The design of novel photocatalyst with high efficiency and low-toxicity provides a new approach to achieve full utilization of solar energy and efficient environmental purification. [41] A novel photocatalyst of rGO-wrapped Ti3C2/TiO2 nanowires ((Ti3C2/TiO2)@rGO) was successfully synthesized to remove hexavalent chromium (Cr(VI)) and Rhodamine B (RhB) from wastewater. [42] The prepared MoS2/Ag2S/Ag nanocomposites as a novel photocatalysts present effective photocatalytic performance for the photodegradation of congo red (CR), tetracycline hydrochloride (TC-HCl) and disinfection for Pseudomonas aeruginosa (P. [43] Furthermore, a novel photocatalyst of Mo/Er-Yb:TiO2@W18O49 quasi-core/shell heterostructure was designed based on the localized surface plasmon resonances (LSPR) effect of W18O49 through solvothermal process. [44] A novel photocatalyst was prepared by immobilization of TiO2 on the surface of FSM-16 catalyst support, and was characterized by different techniques. [45] In this study, novel photocatalysts Ag3PO4@MWCNTs@PPy with excellent photocatalytic activity and photostability were successfully synthesized. [46] Herein, we report a novel photocatalyst with isolated Pt single atomic sites anchored on nanoporous TiO2 film prepared by a facile immersion and reduction method. [47] Here in this work, we focused on the design of a novel photocatalyst which not only accelerated the transfer rate of Cr(VI) and electrons but also provided specific transfer routes for them. [48] An improved metal-to-ligand charge transfer (MLCT) mechanism was proposed in a novel photocatalyst based on graphitic carbon nitride (g-C3N4). [49] Herein, we report highly reliable and reproducible protein–inorganic hybrid CaMoO4:Eu3+ microstructures as a novel photocatalyst for decontamination of environments using an energy-efficient and cost-effective green synthesis. [50]新型光催化剂的合成条件，包括煅烧温度和铜负载量，在光催化前改变以获得最佳反应效率。 [1] 事实上，一系列实验是在连续平面反应器中进行的，使用新型光催化剂/TiO2 技术和金属线 e。 [2] 采用一步水热法将二氧化钛（P25）、还原氧化石墨烯（rGO）和多核@壳簇碳点（CDs）相结合，开发出一种新型光催化剂，用于高效可见光降解有机染料和抗菌剂。应用。 [3] 总结了用于生物质转化制氢的新型光催化剂的合成和基础物理/机理研究的最新进展。 [4] 使用 LF 作为新型光催化剂的大肠杆菌已被成功证明是一种替代且有前景的消毒方法。 [5] Mo/Bi2MoO6/Bi3ClO4纳米复合材料作为一种新型光催化剂，不仅表现出优异的噻吩可见光催化脱硫性能（~97%），而且比Mo/Bi2MoO6和Bi3ClO4纳米结构具有更好的光脱硫效率。 [6] 我们建议 MoS2 异相边界可以作为一种新型光催化剂。 [7] 因此，基于 g-C3N4 的新型光催化剂的设计和合成是水和废水处理的一种有效方法，尤其是针对有机污染物。 [8] 已经开发出基于合适金属或金属氧化物组合的新型光催化剂，以促进在更宽的光谱范围内光生电子以实现完全矿化。 [9] 最近，我们见证了复合材料和多掺杂金属氧化物作为新型光催化剂的蓬勃发展。 [10] 为此，制备具有独特电化学性能和高催化效率的新型光催化剂至关重要，需要引起足够的重视。 [11] 在过去的几十年中，寻找在太阳辐射下具有活性的新型光催化剂一直是广泛工作的目标。 [12] 因此，使用新型光催化剂将 Cr(VI) 光还原为 Cr(III) 和降解罗丹明 B (RhB) 尤为重要。 [13] 希望这篇综述能够提供广阔的视野，并激发对新型光催化剂的探索，以实现高效的 NH3 生产。 [14] 这项工作不仅为稳定的 PTC 材料铺平了道路，而且为新型光催化剂的设计提供了新的见解。 [15] 特别是，人们意识到未来的工作需要针对新型光催化剂的合成或开发最大限度地减少或完全抑制光腐蚀的反应条件，这是从 H2S 光驱动生产 H2 过程中面临的主要问题之一在几种光催化剂的存在下。 [16] 背景 本研究介绍了一种新型光催化剂（包括具有高光催化稳定性和核壳结构的 Co3O@SiO2@TiO2-Ag 纳米复合材料）在去除水溶液中有毒甲基紫的应用。 [17] 天线-反应器光催化剂的设计已成为将过渡金属反应器从传统热催化剂转变为新型光催化剂的有力策略。 [18] 非金属g-C3N4和BiVO4都是对可见光有响应的新型光催化剂，但它们的低电荷分离效率限制了它们不起眼的光催化活性。 [19] 在这项工作中，通过引入少层MoS2纳米片，通过水热法合成了一种新型光催化剂MoS2/SnIn4S8，然后用于建立光催化还原/氧化一体化体系，用于在可见光下修复TBBPA。 [20] 本研究采用水热法制备新型光催化剂 MVO4/g-C3N4 (M = La, Gd)，将不同负载量的 10-50% MVO4 和 g-C3N4 混合并超声振荡得到异质结催化剂。 [21] 报道了一种基于聚氢甲基硅氧烷（PHMS）的新型光催化剂的设计和制备。 [22] 预计目前的工作可以促进基于·CO3-的新型选择性氧化光催化剂的开发。 [23] 然而，快速发现新型光催化剂和合成途径仍然具有挑战性。 [24] 改性和带隙工程被认为对提高新型光催化剂的光催化活性具有极其重要的意义。 [25] 新型光催化剂在 LED 光照射下可有效去除大肠杆菌。 [26] 目前的工作为开发具有高效光催化性能的新型光催化剂提供了独特的合成策略。 [27] 该研究可能会导致开发用于降解有毒染料的新型光催化剂，这些染料从各种化学工业排放到污水中。 [28] 本文报道了通过简单的回流法将 Sb2MoO6 与 g-C3N4 纳米管（简称 GCN 纳米管）偶联得到新型光催化剂。 [29] 开发了一种新型的嵌入富羧酸碳的 Fe3O4/ZnO 纳米粒子光催化剂（Fe3O4/ZnO/CRC），并评估了其在自然光下降解结晶紫（CV）的光催化活性。 [30] 最近，我们见证了复合材料和多掺杂金属氧化物作为新型光催化剂的蓬勃发展。 [31] 优异的可重复使用性和结构稳定性进一步表明基于 MXene 的新型光催化剂在环境修复中的应用前景广阔。 [32] Ps-FNPs 已被广泛研究用于对罗丹明 B 的光催化活性测试，亚甲基蓝和苯胺黑在阳光存在下显示出潜在的染料降解被证明是新型光催化剂。 [33] 这一结果为设计具有更高效率和选择性的新型光催化剂提供了一条新途径。 [34] 这种具有调制电荷转移的新型光催化剂是通过水热处理和随后的阳离子交换反应制备的。 [35] 在这项工作中，一种新型光催化剂 Ce0. [36] 这项研究开辟了采用 ACN 涂层 DMSTN 作为新型光催化剂在可见光环境中进行能量转换的可能性。 [37] 在此，通过水热法轻松制备了一系列具有 II 型 In2S3/钼酸铋 (Bi2MoO6) 异质结构的新型光催化剂。 [38] 通过溶胶-凝胶法将水合二氧化钛（HTO）纳米颗粒固定在稻草（RS）中，成功合成了一种新型光催化剂。 [39] 在这里，我们提出了一种通过简单的溶胶-凝胶法合成铕掺杂钛酸钙（Eu:CaTiO3）的新型光催化剂。 [40] 新型高效低毒光催化剂的设计为实现太阳能的充分利用和环境的高效净化提供了新途径。 [41] 成功合成了一种新型 rGO 包裹的 Ti3C2/TiO2 纳米线光催化剂 ((Ti3C2/TiO2)@rGO)，以去除废水中的六价铬 (Cr(VI)) 和罗丹明 B (RhB)。 [42] 制备的 MoS2/Ag2S/Ag 纳米复合材料作为一种新型光催化剂，对刚果红（CR）、盐酸四环素（TC-HCl）的光降解和铜绿假单胞菌（P. [43] 此外，基于W18O49的局域表面等离子体共振（LSPR）效应，通过溶剂热过程设计了一种新型Mo/Er-Yb:TiO2@W18O49准核/壳异质结构光催化剂。 [44] 通过在 FSM-16 催化剂载体表面固定 TiO2 制备了一种新型光催化剂，并通过不同的技术对其进行了表征。 [45] 本研究成功合成了具有优异光催化活性和光稳定性的新型光催化剂Ag3PO4@MWCNTs@PPy。 [46] 在此，我们报道了一种新型光催化剂，该光催化剂具有锚定在纳米多孔 TiO2 薄膜上的孤立 Pt 单原子位点，该薄膜通过简便的浸渍和还原方法制备。 [47] 在这项工作中，我们专注于设计一种新型光催化剂，该催化剂不仅可以加快 Cr(VI) 和电子的转移速率，还可以为它们提供特定的转移途径。 [48] 在基于石墨氮化碳 (g-C3N4) 的新型光催化剂中提出了一种改进的金属到配体电荷转移 (MLCT) 机制。 [49] 在这里，我们报告了高度可靠和可重复的蛋白质-无机杂化 CaMoO4:Eu3+ 微结构作为一种新型光催化剂，用于使用节能且具有成本效益的绿色合成来净化环境。 [50]
visible light irradiation 可见光照射
To overcome water instability and low photocatalytic activity of lead-free halide perovskite for the degradation of organic dyes, we report a novel photocatalyst of lead-free halide perovskite with Na incorporation and employ it for the photocatalytic degradation of organic dyes in water solution under visible light irradiation. [1] Under 50 min of visible light irradiation, the novel photocatalyst exhibited approximately 50% gaseous toluene degradation efficiency, which was ca. [2] The novel photocatalyst achieved approximately three times higher photocatalytic degradation within a shorter period of visible-light irradiation than pure Bi2MoO6. [3] In the study, we used two conducting polymers, polyaniline (PANI) and polypyrrole (PPy), to sensitize Ta3N5, thereby enhancing its photocatalytic activity, and then applied this novel photocatalyst to overall water splitting to produce hydrogen and oxygen even under visible light irradiation. [4] Therefore, the novel photocatalysts exhibit a remarkable reduction performance for CO2 reduction under visible light irradiation. [5] In this paper, CaFe2O4 is introduced as a novel photocatalyst for the degradation of POME under visible light irradiation. [6]为了克服无铅卤化物钙钛矿在降解有机染料中的水不稳定性和低光催化活性，我们报道了一种新型的掺钠无铅卤化物钙钛矿光催化剂，并将其用于可见光条件下水溶液中有机染料的光催化降解。光照射。 [1] 在 50 分钟的可见光照射下，新型光催化剂表现出约 50% 的气态甲苯降解效率，约为 50%。 [2] nan [3] 在研究中，我们使用了两种导电聚合物聚苯胺 (PANI) 和聚吡咯 (PPy)，对 Ta3N5 进行敏化处理，从而增强其光催化活性，然后将这种新型光催化剂应用于整体水分解，即使在可见光照射下也能产生氢气和氧气。 . [4] 因此，新型光催化剂在可见光照射下表现出显着的 CO2 还原还原性能。 [5] nan [6]
excellent visible light
In this paper, a novel photocatalyst CNCC with excellent visible light photocatalytic performance was successfully prepared to optimize the CO2 photoreduction performance. [1] This work provided a novel photocatalyst with excellent visible light photocatalytic performance and investigated the mechanism of interface charge transfer. [2] In this work, novel photocatalysts Ag3PO4@MWCNTs@PANI with excellent visible light photocatalytic performance and photostability were successfully prepared by a facile in-situ precipitation method. [3]本文成功制备了一种具有优异可见光光催化性能的新型光催化剂CNCC，以优化CO2光还原性能。 [1] 该工作提供了一种具有优异可见光光催化性能的新型光催化剂，并研究了界面电荷转移的机理。 [2] nan [3]
graphitic carbon nitride 石墨氮化碳
Herein, we report a novel photocatalyst by implanting zero-dimensional carbon quantum dots (CQDs) within one-dimensional porous tubular graphitic carbon nitride (g-C3N4) on carbon cloth (CC). [1] In this work, graphitic carbon nitride (g-C3N4) decorated with molybdenum-substituted tungstophosphoric acid as a novel photocatalyst (H3PW4Mo8O40/g-C3N4) was used to catalyze the oxidation of alcohols and sulfides. [2] There are different novel photocatalysts including TiO2, graphitic carbon nitride (g- C 3 N4), nanocomposites and membranes that have been developed for microbial disinfection in land and water surfaces. [3]在此，我们通过在碳布 (CC) 上的一维多孔管状石墨氮化碳 (g-C3N4) 中植入零维碳量子点 (CQD) 来报道一种新型光催化剂。 [1] 在这项工作中，以钼取代的钨磷酸修饰的石墨氮化碳 (g-C3N4) 作为一种新型光催化剂 (H3PW4Mo8O40/g-C3N4) 被用于催化醇和硫化物的氧化。 [2] nan [3]
polyaniline tungsten trioxide 聚苯胺三氧化钨
Novel photocatalysts polyaniline/tungsten trioxide (P/W), polyaniline/tungsten trioxide @zeolitic imidazolate frameworks, (P/W@ZIF-8) and polyaniline/tungsten trioxide@ Zr(IV) aminoterephthalate metal–organic frameworks (P/W@UiO-66-NH2 MOFs) were successfully synthesized via the in-situ growth of polyaniline, ZIF-8, and UiO-66-NH 2 MOFs onto the tungsten trioxide nanoparticle. [1]新型光催化剂聚苯胺/三氧化钨 (P/W)、聚苯胺/三氧化钨@沸石咪唑酯骨架 (P/W@ZIF-8) 和聚苯胺/三氧化钨@ Zr(IV) 氨基对苯二甲酸金属-有机骨架 (P/W@通过在三氧化钨纳米颗粒上原位生长聚苯胺、ZIF-8 和 UiO-66-NH 2 MOFs 成功合成了 UiO-66-NH2 MOFs。 [1]
Developing Novel Photocatalyst 开发新型光催化剂
BRGO-Fe3O4-MWCNT as effective nanocomposite for application as advanced supercapacitor electrode and developing novel photocatalyst for remedy of environmental problems. [1] Developing novel photocatalysts with high efficiency will inject expectation into the field of photocatalysis towards the realization of practical applications. [2] Development of atomic layers and their heterostructures opened new avenues in developing novel photocatalysts for enhanced light–matter interaction. [3] Developing novel photocatalysts for green synthesis of important organic intermediates under mild conditions is of great significance in industry. [4] This research sheds light on developing novel photocatalysts for efficient hydrogen evolution. [5]BRGO-Fe3O4-MWCNT 作为有效的纳米复合材料，可用作先进的超级电容器电极，并开发用于解决环境问题的新型光催化剂。 [1] 开发高效的新型光催化剂将为光催化领域的实际应用注入期待。 [2] 原子层及其异质结构的发展为开发用于增强光与物质相互作用的新型光催化剂开辟了新途径。 [3] 开发用于在温和条件下绿色合成重要有机中间体的新型光催化剂在工业上具有重要意义。 [4] nan [5]
Designing Novel Photocatalyst
Perovskite and perovskite-related structures offer a broad scope in designing novel photocatalysts for this process. [1] In addition, we provide a new strategy for designing novel photocatalysts with high efficiency by controlling their surface configurations and morphologies. [2]钙钛矿和钙钛矿相关结构为设计用于该过程的新型光催化剂提供了广泛的范围。 [1] 此外，我们通过控制其表面构型和形态，为高效设计新型光催化剂提供了一种新策略。 [2]
Develop Novel Photocatalyst 开发新型光催化剂
Although photocatalytic materials have been under extensive investigation for several decades, attempts to improve the current well-studied photocatalysts and develop novel photocatalysts for indoor air purification are still ongoing. [1] A powerful and attractive route to develop novel photocatalysts for C-N bond formation involves the use of pyrrolidine as the substrate and cocatalyst simultaneously. [2]尽管光催化材料已经进行了几十年的广泛研究，但改进目前已充分研究的光催化剂和开发用于室内空气净化的新型光催化剂的尝试仍在进行中。 [1] 开发用于 C-N 键形成的新型光催化剂的一个强有力且有吸引力的途径涉及同时使用吡咯烷作为底物和助催化剂。 [2]