<th id="5nh9l"></th><strike id="5nh9l"></strike><th id="5nh9l"><noframes id="5nh9l"><th id="5nh9l"></th><strike id="5nh9l"></strike>
<progress id="5nh9l"><noframes id="5nh9l"><th id="5nh9l"><noframes id="5nh9l">
<th id="5nh9l"></th> <strike id="5nh9l"><noframes id="5nh9l"><span id="5nh9l"></span>
<progress id="5nh9l"><noframes id="5nh9l"><span id="5nh9l"><noframes id="5nh9l"><span id="5nh9l"></span><strike id="5nh9l"><noframes id="5nh9l"><strike id="5nh9l"></strike>
<span id="5nh9l"><noframes id="5nh9l">
<span id="5nh9l"><noframes id="5nh9l">
<span id="5nh9l"></span><span id="5nh9l"><video id="5nh9l"></video></span>
<th id="5nh9l"><noframes id="5nh9l"><th id="5nh9l"></th>
<progress id="5nh9l"><noframes id="5nh9l">

水熱反應前驅液pH對鎢酸鉍形貌結構及光催化性能調控

Mechanism of morphology regulation and photocatalytic performance of bismuth tungstate by precursor pH in hydrothermal reactions

  • 摘要: 氟伐他汀作為常用的降血脂藥物,常隨人體排泄物排入水體. 環境水體中的氟伐他汀很難被自然光所降解,長期累積會對環境構成一定的威脅. 本研究采用鎢酸鉍(Bi2WO6)可見光催化降解氟伐他汀,研究不同水熱反應前驅液pH制備Bi2WO6的形貌結構及光電性能變化規律,結合活性自由基及中間產物解析揭示氟伐他汀降解機理. 結果表明,前驅液pH由酸性轉向中性時Bi2WO6晶體發育過程被破壞引起納米片堆疊,前驅液pH為堿性時形成無序的八面體物相高聚體. 隨著pH升高,Bi2WO6的比表面積和孔徑逐漸減小. 當pH值為0.5時,Bi2WO6呈現有序的三維納米花球結構,具有最佳光催化性能,光照120 min后氟伐他汀降解率達69.84%. 經過四輪循環實驗后,催化劑性能仍較為穩定. 電化學實驗結果表明,當前驅液pH值為0.5時,Bi2WO6具有最佳的光生電子–空穴(e–h+)分離性能,進而促進活性自由基高效產生. 自由基實驗結果表明,在降解過程中h+發揮主要的氧化作用,·OH和·\mathrmO_2^- 起輔助作用. Bi2WO6降解氟伐他汀的機理是以h+為主,·OH和·\mathrmO_2^- 為輔,聯合攻擊氟伐他汀分子的C—C鍵,形成小分子環狀有機物、直鏈有機物和羥基化衍生物,進而將其礦化為CO2和H2O.

     

    Abstract: Fluvastatin, a widely used lipid-lowering drug, is frequently released into water bodies via human excreta. Due to its resistance to natural light degradation, its prolonged accumulation in the environment may pose significant ecological risks. Semiconductor photocatalysis has gained increasing attention as an eco-friendly and versatile method for removing refractory pollutants. Among various photocatalysts, bismuth tungstate (Bi2WO6) has emerged as a promising photocatalyst due to its strong visible-light response and high chemical stability. However, its application remains limited by its energy band structure, low separation efficiency of photogenerated carriers, and small specific surface area. In this study, Bi2WO6 was utilized for the visible-light driven photocatalytic degradation of fluvastatin. The research investigates the influence of precursor pH during hydrothermal synthesis on the morphological structure and photoelectric properties of Bi2WO6. Additionally, reactive radicals and intermediates analyses were conducted to elucidate the degradation mechanism of fluvastatin. The morphology, crystal phase, optical absorption performance, specific surface area, electrochemical performance, and carrier separation ability of the synthesized Bi2WO6 photocatalyst were characterized using an electrochemical workstation and steady-state fluorescence spectroscopy. Its performance and stability were evaluated through degradation and cyclic experiments, and the effects of different pH conditions on photocatalytic efficiency were also examined. Additionally, active species analysis and intermediate product identification were employed to elucidate the degradation mechanism of fluvastatin. The results indicate that as the precursor pH shifts from acidic to neutral, the crystal growth of Bi2WO6 is disrupted, leading to the stacking of nanosheets. Under alkaline conditions, disordered octahedral phase polymers are formed. The optimal precursor pH was found to be 0.5, yielding an ordered, three-dimensional nanoflower morphology. Although variations in precursor pH did not significantly affect the light absorption capacity of Bi2WO6, increasing the pH resulted in a decrease in specific surface area and pore volume, from 57 m2·g–1 and 0.045 cm3·g–1 to 3.5 m2·g–1 and 0.002 cm3·g–1, respectively. Electrochemical experiments and steady-state fluorescence spectra further revealed that the efficiency of photogenerated carrier separation gradually decreases with increasing precursor pH. At pH 0.5, Bi2WO6 exhibited the highest photocatalytic performance, achieving 69.84% fluvastatin degradation after 120 min of illumination. Moreover, after four cycles of testing, the catalyst demonstrated stable performance, with the degradation rate remaining nearly unchanged. Free radical experiments demonstrated that h+ ions play the primary oxidative role in the degradation process, with ·OH and ·\mathrmO_2^- radicals contributing as supplementary effects. These reactive species attack the C–C bonds in fluvastatin molecule, breaking them down into small cyclic organics, straight-chain organics, and hydroxylated derivatives, which are ultimately converted into CO2 and H2O.

     

/

返回文章
返回
<th id="5nh9l"></th><strike id="5nh9l"></strike><th id="5nh9l"><noframes id="5nh9l"><th id="5nh9l"></th><strike id="5nh9l"></strike>
<progress id="5nh9l"><noframes id="5nh9l"><th id="5nh9l"><noframes id="5nh9l">
<th id="5nh9l"></th> <strike id="5nh9l"><noframes id="5nh9l"><span id="5nh9l"></span>
<progress id="5nh9l"><noframes id="5nh9l"><span id="5nh9l"><noframes id="5nh9l"><span id="5nh9l"></span><strike id="5nh9l"><noframes id="5nh9l"><strike id="5nh9l"></strike>
<span id="5nh9l"><noframes id="5nh9l">
<span id="5nh9l"><noframes id="5nh9l">
<span id="5nh9l"></span><span id="5nh9l"><video id="5nh9l"></video></span>
<th id="5nh9l"><noframes id="5nh9l"><th id="5nh9l"></th>
<progress id="5nh9l"><noframes id="5nh9l">
259luxu-164