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研究生: 林政瑋
Lin, Cheng-Wei
論文名稱: 製備金屬氧化物活化過一硫酸氫鉀催化降解布洛芬
Efficient activation of peroxymonosulfate (PMS) by metal oxides for degradation of ibuprofen (IBF)
指導教授: 劉守恒
Liu, Shou-Heng
學位類別: 碩士
Master
系所名稱: 工學院 - 環境工程學系
Department of Environmental Engineering
論文出版年: 2021
畢業學年度: 109
語文別: 英文
論文頁數: 104
中文關鍵詞: 布洛芬 、過一硫酸氫鉀 、金屬氧化物 、新興污染物 、高級氧化 、單線氧非自由基
外文關鍵詞: Ibuprofen, metal oxides, PMS, emerging contaminants, advanced oxidation process (AOP), singlet oxygen nonradical process
相關次數: 點閱:162  下載:0 
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  • 近幾年來,科學家們致力於研究環境水體中之新興污染物,主要項目包含農藥、工業用品、介面活性劑、藥物與個人保健用品等,而藥物與個人保健用品例如藥水、抗生素、針劑中存在數種會影響身體內分泌系統之干擾物質。布洛芬(Ibuprofen)為生活中廣泛使用的抗生素並且屬於非類固醇抗消炎藥(non-steroidal anti-inflammatory drugs),主要用於緩解各種疾病所引起的疼痛。由於布洛芬很難通過自然降解和傳統的廢污水處理程序中去除,因此可以在廢水、地下水及地表水中檢測出微量殘留。目前主要應用於去除新興污染物的技術包括活性炭吸附、高級氧化法、微生物系統和薄膜處理。但上述方法都需要大量的時間和高成本,有鑒於此,本研究以觸媒活化過一硫酸氫鉀(PMS)程序應用於降解布洛芬,可提供快速且環境友善處理新興汙染物的方式之一。在本研究中通過快速、簡便的共沉澱方法製備一系列金屬氧化物,以SEM、TEM、XRD、FT-IR、XPS、Raman、BET等進行物化特性分析,並探討所製備觸媒降解布洛芬效能的差異。在批次實驗結果中顯示,負載鈣、鎂、鋇等鹼土金屬氧化物中,修飾氧化鈣於氧化銅的複合金屬氧化物具有較多的表面官能基、氧空位與三價銅能有效活化PMS,因此有最佳的降解布洛芬效能,並進一步改變修飾氧化鈣的含量(1~20%)以探討其最適含量,結果發現在氧化鈣含量5%的條件下,有較穩定的球狀結構、均勻分布的氧化鈣與較多的Cu-OH鍵結,因此具有最好降解效能(6分鐘內達到99.9%的布洛芬去除率)。進一步研究不同的操作條件下(觸媒濃度、布洛芬含量、PMS劑量、溫度、pH值及不同淬滅劑),對5%氧化鈣/氧化銅的複合金屬氧化物觸媒降解效能的影響。最後透過液相層析質譜儀分析布洛芬的降解中間產物,並結合EPR及淬滅劑實驗,發現此反應之主要機制是由單線氧為主的非自由基系統。

    In the recent years, scientists have devoted to the research of emerging contaminants (ECs) in the water body environment. The ECs consist of pesticides, industrial chemicals, surfactants and pharmaceuticals and personal care products (PPCPs) such as antibiotics, syrups, and injections. Among the ECs, endocrine disrupting substances are commonly known as environmental hormones. Ibuprofen (IBF), regarded as one kind of pharmaceuticals, personal care products and non-steroidal anti-inflammatory drugs (NSAID), is applied to relieve pain caused by toothache, headache, muscle pain, arthritis, or physical pain. Because it is hard to remove by natural degradation and traditional wastewater treatment systems, it can be found in effluent water, surface water and groundwater. Current technologies for treating ECs include activated carbon adsorption, membrane treatments, biological treatments, and advanced oxidation. However, all the above methods require a lot of time and high cost. Therefore, using catalysts to activate the peroxymonosulfate for degrading ibuprofen may be a feasible and eco-friendly strategy. In this research, a series of metal oxides were prepared via a fast and facile coprecipitation method. The morphologies and physicochemical properties of the catalysts were analyzed by SEM, TEM, FT-IR, XPS, Raman, XRD and BET analyses. The degradation of IBF was carried out in a batch reactor under magnetic stirring and their corresponding degradation performance of IBF via prepared catalysts is also studied. The experimental results show that among the alkaline earth metal oxides such as MgO, CaO and BaO, the decoration of CaO onto CuO possess more surface functional groups, more oxygen vacancies and more Cu3+ species which can degrade IBF most effectively. In terms of different CaO ratios (1~20%) onto CuO, the CaOCuO catalysts (5% CaO) have the best degradation efficiency (IBF removal efficiency = ca. 99.9%) within 6 min because of more complete sphere structure, uniform dispersion of CaO and more Cu-OH bondings. The effects of different operating conditions (catalyst, IBF concentrations, peroxymonosulfate dosages, temperature, pH, and quenchers) on catalyst performance are also discussed. The intermediate products of the degraded IBF and its mechanism were also analyzed by liquid chromatography mass spectrometer, EPR and quenching tests. The results show that the 1O2 is the main reactive species involved in the degradation of IBF via the CaOCuO (5%)/PMS system.

    摘要 I Abstract II Content IV List of Tables VI List of Figures IX Chapter 1 INTRODUCTION 1 1.1 Motivations 1 1.2 Objectives 2 Chapter 2 LITERATURES REVIEW 3 2.1 Emerging Contaminants 3 2.1.1 Ibuprofen (IBF) 5 2.1.2 Treatment processes to remove emerging contaminants 7 2.2. Peroxymonosulfate (PMS) 15 2.2.1 Reactive oxygen species (ROS) 18 2.3. Metal oxide catalyst 19 2.3.1 Homogeneous and heterogeneous system 19 2.3.2 The PMS activation mechanism of metal oxides 21 2.3.3 Copper (II) oxide 23 2.3.4 Alkaline earth metals 24 Chapter 3 EXPERIMENTAL METHODS 25 3.1 Experiment processes 25 3.2 Chemicals preparation 26 3.2.1 Chemicals 26 3.2.2 Synthesis of metal oxides 27 3.2.3 Ibuprofen standard aqueous solution 28 3.3 Batch experiment 29 3.4 Characterization and Analysis 30 3.4.1 Scanning Electron Microscope (SEM) 30 3.4.2 Transmission Electron Microscope (TEM) 31 3.4.3 X-ray Diffraction (XRD) 31 3.4.4 Fourier Transform – Infrared Spectrometer (FT-IR) 32 3.4.5 X-ray Photoelectron Spectroscope (XPS) 32 3.4.6 Raman Spectroscopy 32 3.4.7 Brunauer-Emmett-Teller (BET) 33 3.4.8 Electron Paramagnetic Resonance Spectrometer (EPR) 33 3.4.9 High Performance Liquid Chromatography-UV Detector (HPLC-UV) 34 3.4.10 Liquid Chromatography-Mass Spectrometry (LC-MS) 35 Chapter 4 RESULTS AND DISCUSSION 36 4.1 Degradation of IBF via activation of PMS by MCuO 36 4.1.1 SEM 36 4.1.2 TEM 39 4.1.3 XRD 41 4.1.4 FT-IR 43 4.1.5 XPS 44 4.1.6 Raman 47 4.1.7 BET 48 4.1.8 The degradation efficiency of IBF by MCuO 49 4.2 Degradation of IBF via activation of PMS by CaOCuO (X%) 52 4.2.1 SEM 52 4.2.2 TEM 55 4.2.3 XRD 57 4.2.4 FT-IR 57 4.2.5 XPS 58 4.2.6 BET 63 4.2.7 The degradation efficiency of IBF by CaOCuO (X%) 64 4.3 Operating conditions 67 4.3.1 Effect of catalyst concentrations 67 4.3.2 Effect of IBF concentrations 70 4.3.3 Effect of PMS dosages 73 4.3.4 Effect of temperature 76 4.3.5 Effect of pH 80 4.3.6 Effect of scavengers 82 4.4 EPR studies 85 4.5 Stability experiments 86 4.6 Reaction mechanism 87 4.7 Degradation intermediates of IBF 89 4.8 Bioassay analysis 95 Chapter 5 CONCLUSIONS 96 REFERENCES 97

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