TiO2光催化降解4-氯苯酚过程中的电分析监测

 采用循环伏安法和紫外光谱法对有机物的光催化降解进行机理研究和在线监测．以标准光催化剂DegussaP25在紫外光照射下催化降解4－氯苯酚,发现在降解过程中至少有两对氧化还原中间产物：对苯二酚－苯醌和羟基氢醌－羟基苯醌．由4－氯苯酚及中间产物的电极响应,可以观测到它们在光催化降解过程中的含量变化,从而对整个过程实现在线监测,并由此全面了解光催化反应机理．从不同反应时间后测得的紫外光谱可以看到,苯环特征峰逐渐消失．这表明4－氯苯酚的苯环逐渐被打开,直至被彻底降解．     

新型仿生光催化剂HMS-FePcS催化孔雀绿在可见光下的降解历程

在可见光照射下,采用合成的新型仿生光催化剂HMS-FePcS催化降解孔雀绿模拟染料废水.由不同反应时间段反应液的HPLC谱和MS谱中产物峰的变化可知,孔雀绿的催化降解过程为先脱色后矿化.采用固体萃取法对孔雀绿降解的中间产物进行了富集和分离,并使用GC-MS对所得的中间产物进行了鉴定,确定出10余种中间产物.在此基础上对孔雀绿的降解历程进行了推测,指出孔雀绿的光催化降解主要从中心碳原子与二甲氨基苯基之间的C-C键处断裂,4-二甲氨基苯甲酮是此反应最常见的中间产物.当4-二甲氨基苯甲酮被羟基自由基进攻时,生成苯甲酸、对二甲氨基苯甲酸及对二甲氨基苯酚等化合物.这些小分子芳香类中间产物进一步发生羟基化反应,开环生成小分子脂肪酸类化合物.     

超声协同纳米TiO2光催化降解水中苯酚机理的研究

本文考察了声光催化技术降解水中苯酚的降解效率,测定了超声波联合光催化降解苯酚的主要中间产物,初步探讨了声光催化降解苯酚的反应机理。实验结果表明：超声波与光催化之间存在协同效应;光催化与声光催化降解苯酚的反应历程和产物基本一致。这两个反应的中间产物都是苯醌、邻苯二酚和对苯二酚;最终产物是水和二氧化碳。     

甲基叔丁基醚光催化降解的反应历程

以自制的TiO2为催化剂,在间歇式光催化反应装置中考察了水中甲基叔丁基醚的光催化降解反应.结果表明,水中MTBE在TiO2催化剂、氧气和紫外光照射的条件下能被光催化转化成无毒产物并最终被矿化.MTBE光催化降解过程中产生的主要中间产物有甲酸叔丁酯、叔丁醇和丙酮,尽管降解速率不同,它们也都能被光催化降解.通过对反应物、中间物及产物的追踪分析,认为MTBE的光催化降解首先是通过羟基化过程来进行,进而提出MTBE光催化降解的可能反应历程.     

MoS_2负载量对MoS_2/TiO_2光催化降解苯酚效率的影响及其作用机理研究

通过水解法制备TiO_2纳米颗粒,与经过超声处理后的MoS_2片层纳米材料复合制备MoS_2/TiO_2纳米催化剂,考察不同MoS_2负载量对其光催化降解苯酚效率及路径的影响。XRD、SEM、EDS、FT-IR和UV-vis DRS等表征结果表明,复合催化剂主要由锐钛矿型TiO_2和MoS_2组成;剥离后的MoS_2呈现薄片层状结构,均匀地分散在TiO_2纳米颗粒当中。光催化降解苯酚性能测试结果显示,对于MoS_2/TiO_2催化剂,MoS_2负载量的提高有利于光催化降解苯酚效率的提高;当MoS_2负载量为27%时,复合M o S2/TiO_2纳米颗粒的光催化性能最佳,反应80 min后可将苯酚完全降解。通过对苯酚降解过程中生成中间产物跟踪发现,MoS_2负载量的提高有利于促进中间产物苯醌、对苯二酚以及邻苯二酚的生成,进而提升了MoS_2/TiO_2复合材料的光催化性能。     

环境湿度对TiO2/活性炭纤维气-固光催化氧化甲苯的影响

在恒温控湿的环境舱中,以自制的TiO2/ACF(活性炭纤维)为光催化剂,研究了环境湿度对甲苯光催化降解过程的影响.通过N2吸附和扫描电子显微镜分别对TiO2/ACF光催化剂的孔径结构和形貌特征进行了表征;利用GC-MS和GC-FID对甲苯光催化过程中生成的中间产物进行了定性及定量分析.结果表明,环境舱中相对湿度增大,甲苯光催化转化率提高;不同相对湿度下,积累在光催化剂表面的中间产物种类相同,但支链氧化产物(苯甲醇、苯甲醛和苯甲酸)的积累量远多于苯环氧化产物(甲酚和对甲基苯酚)的积累量;随环境相对湿度的增大,苯甲醛在光催化剂表面的积累量减小,其余中间产物的积累量均有不同程度的增加.这说明水分子在甲苯光催化过程中起重要作用,相对湿度不仅影响甲苯的光催化转化效率,还影响其光催化转化的过程.尽管在各湿度条件下,支链氧化都是甲苯光催化降解的主要途径,但环境湿度增大更有利于苯环氧化途径的进行.讨论了水蒸气在甲苯光催化氧化过程中的作用机理.     

原位红外光谱法研究La/TiO2对有机污染物的光催化降解

本工作采用改进的溶胶-凝胶法和浸渍法制备了TiO₂掺杂稀土离子La³⁺的La/TiO₂光催化剂，运用XRD、N₂吸附脱附、紫外可见漫反射光谱(DRS)、表面光电压谱(SPS)等手段进行表征，同时利用原位红外技术考察了La/TiO₂样品光催化降解乙烯、丙酮、苯的气-固相光催化氧化反应，对其光催化降解有机污染物的过程进行了研究。结果表明，TiO₂经适量La³⁺掺杂后，锐钛矿晶型的含量增加，晶粒度减小，比表面积增大，禁带宽度增加，表面光电压信号增强，光生电子-空穴对有效分离；La/TiO₂样品对乙烯、丙酮、苯的光催化性能与纯TiO₂相比均有不同程度的改善，乙烯可以被光催化氧化完全矿化生成CO₂，而丙酮被光催化氧化可能生成中间产物丙酸，苯被光催化氧化可能生成中间产物苯酚和苯醌。     

2,4-二氯苯酚的电化学氧化降解反应研究

采用循环伏安法和原位红外光谱技术研究了2,4-二氯苯酚在Pt电极上的电化学氧化降解反应,结合Fukui函数值预测了2,4-二氯苯酚在电化学氧化过程中的反应位点. 结果表明,Pt电极对2,4-二氯苯酚有良好的电催化活性,2,4-二氯苯酚在电极表面反应主要有3个途径：直接通过电化学反应脱去氯离子,生成苯酚;在·OH的进攻下,C—Cl键断裂,4位Cl较2位Cl先脱去,生成苯二酚,并可进一步氧化生成苯醌以及不饱和羧酸;在·OH的进攻下发生苯环开环反应,生成含氯不饱和羧酸. 在1700 mV左右,2,4-二氯苯酚可经电化学氧化生成CO₂.     

取代基结构-活性关系对电化学降解取代苯胺的影响

以Na2SO4为支持电解质, 使用Ti/PbO2电极, 研究了带有推电子基(—CH3)和吸电子基(—NO2, —Cl)的邻或对位取代基苯胺类化合物的电催化氧化降解过程. 研究结果表明, 带有取代基苯胺类化合物的氧化降解是在羟基自由基进攻下生成氨基酚类化合物, 然后在电极表面失去电子生成苯醌继续氧化的过程. 带有推电子基团苯胺的电催化降解速度比带有吸电子基团的苯胺降解速度快, 这是因为推电子基团使苯环电子云密度提高, 有利于羟基自由基的进攻; 吸电子基团使苯环电子云密度降低, 不利于羟基自由基的进攻. 由于阴极还原反应的作用, 化学反应活性和电化学反应活性并不完全一致. 氯代苯胺在羟基自由基进攻下—Cl离去, 以Cl-离子形式进入溶液中, 被氧化生成有效氯, 加快降解反应速度. 硝基虽然是强吸电子基, 但是可以转化为对苯二胺, 进一步活化苯环, 其降解速度较快.     

原位红外光谱法研究三氯乙烯在TiO2表面的光催化降解

通过原位红外光谱技术在线研究了三氯乙烯的直接光降解以及三氯乙烯在TiO2表面的气相光催化降解. 研究结果表明, UV/TiO2体系比UV体系具有更强的降解能力. 在三氯乙烯的光催化降解过程中, 发现有二氯乙酰氯、二氧化碳、一氧化碳、水、氯化氢和光气等中间产物生成. 根据反应结果, 分析了三氯乙烯在TiO2表面的气相光催化降解机理: 三氯乙烯在羟基自由基等作用下生成中间产物二氯乙酰氯, 二氯乙酰氯进一步发生自由基反应, 最终降解为二氧化碳、一氧化碳、水、氯化氢和光气.     

Kinetics and Characterization of Degradation Products of Dihydralazine and Hydrochlorothiazide in Binary Mixture by HPLC-UV,LC-DAD and LC–MS Methods

Dihydralazine and hydrochlorothiazide were stored at high temperature and humidity, under UV/Vis light and different pH, as individual drugs and the mixture. Then, a sensitive and selective HPLC-UV method was developed for simultaneous determination of dihydralazine and hydrochlorothiazide in presence of their degradation products. Finally, the degradation products were characterized through LC-DAD and LC–MS methods. Dihydralazine was sensitive to high temperature and humidity, UV/Vis light and pH?≥?7. At the same time, it was resistant to acidic conditions. Hydrochlorothiazide was sensitive to high temperature and humidity, UV/Vis light and changes in pH. Its highest level of degradation was observed in 1 M HCl. Degradation of the drugs was higher when they were stressed in the mixture. In the case of dihydralazine, the percentage degradation was 5–15 times higher. What is more, dihydralazine became sensitive to acidic conditions. Hydrochlorothiazide was shown to be more sensitive to UV/Vis light and pH?>?4. Degradation of dihydralazine and hydrochlorothiazide followed first-order kinetics. The quickest degradation of dihydralazine was found to be in 1 M NaOH while of hydrochlorothiazide was in 1 M HCl (individual hydrochlorothiazide) or at pH 7–10 (hydrochlorothiazide in the mixture). A number of new degradation products were detected and some of them were identified by our LC-DAD and LC–MS methods. In the stressed individual samples, (phenylmethyl)hydrazine and 1,2,4-benzothiadiazine-7-sulfonamide 1,1-dioxide were observed for the first time. Interactions between dihydralazine and hydrochlorothiazide in the mixture were confirmed by additional degradation products, e.g., 2H-1,2,4-benzothiadiazine-7-sulfonamide 1,1,4-trioxide.     

掺铈纳米TiO2薄膜制备及光催化降解甲醛甲苯

通过Sol-Gel工艺在玻璃表面及多孔陶瓷表面制得了均匀透明的掺铈纳米TiO2薄膜．通过SEM、XRD及UV-Vis等手段对玻璃表面掺铈纳米TiO2薄膜进行了表征．结果表明，薄膜表面无开裂现象、膜内部比表面积大、TiO2分布均匀．薄膜中出现的锐钛矿相在(101)面有一定的择优取向，且UV-Vis研究表明，掺铈纳米TiO2薄膜在近紫外的吸光度有明显提高．利用自行设计的反应器，以多孔陶瓷为介质，对甲醛、甲苯等有机物进行了光催化降解研究．结果表明，掺铈纳米TiO2薄膜对甲醛甲苯有极高的光催化降解效率，由于薄膜成本低廉，易于工业化，为净化室内空气开辟了新的途径．     

Benzidine photodegradation: a mass spectrometry and UV spectroscopy combined study

The benzidine photodegradation process was studied using UV/Vis spectroscopy and electrospray ionization mass spectrometry (ESI-MS) combined with collision-induced dissociation (CID) and tandem mass spectrometry (MS/MS). Mass spectrometry was used to characterize benzidine and to identify and characterize possible degradation products and intermediates. The MS data showed that benzidine is quite persistent in aqueous medium. Moreover, the MS analysis enabled us to propose the following three degradation products/intermediates: 4'-nitro-4-biphenylamine, tetrahydroxybiphenyl and 4,4'-dinitrobiphenyl. For the benzidine molecular ion and protonated molecule and for the protonated molecules of the degradation products/intermediates detected, fragmentation patterns are proposed based on CID and MS/MS data. For the photodegradation process different catalysts were used, namely the commercial TiO2 Degussa P25, and the laboratory-prepared ZnO, TiO2 anatase and a titanium-zinc oxide with a perovskite type structure. Comparison of the different catalysts showed that degradation was favoured with the commercial TiO2. Nevertheless, the other catalysts appear to be promising and economic alternatives for potential future remediation studies.     

Spinel cobalt manganese oxide nano-composites grown hydrothermally on nanosheets for enhanced photocatalytic mineralization of Acid Black 1 textile dye: XRD,FTIR, FESEM,EDS and TOC studies

Spinel cobalt manganese oxide nano-composites were grown on nanosheets using acetate precursors in mono-ethylene glycol. Crystal structures and morphologies of nano-composites were characterized by X-ray diffraction (XRD), field emission scanning electron microscopy and energy dispersive X-ray spectroscopy to characterize the element composition. Fourier transform infrared spectroscopy was used for structural characterization and UV–Vis diffuse reflectance spectra (UV–Vis DRS) for optical properties. XRD results showed tetragonal spinel cobalt manganese oxide (Co,Mn)(Co,Mn)₂O₄ and cubic spinel cobalt manganese oxide MnCo₂O_4.5 structural phases. The crystallite size calculated by the Scherrer’s equation was 17 nm. The morphological studies displayed the existence of 40–63 nm nano-powders grown on nanosheets with a good degree of crystallization. Optical properties of cobalt manganese oxide nano-composites exhibit absorbance edge, and the band gap calculated from UV–Vis DRS results was 1.78 eV. FTIR spectra indicated that hydroxyl and oxide groups were major active sites. The absorption bands observed at 656 and 568 cm^?1 are related to stretching vibrations of Mn–O and Co–O, respectively. The photocatalytic activities of nano-composites for photocatalytic mineralization of Acid Black 1 textile dye showed an outstanding performance. Photocatalytic process yielded 91% total organic carbon removals within 2.5 h of irradiation. The enhanced photocatalytic activity was attributed to better charge separation of the photo-generated electron–hole pairs in nano-composite.     

S掺杂宽光域响应Ti1-xSyO2光催化剂的制备及表征

以TiCl4和硫脲为主要原料, 采用酸催化水解法制得浅黄色S掺杂Ti1-xSyO2光催化剂. 以苯酚为模型物, 考察了Ti1-xSyO2在可见光区、紫外光区及太阳光下的催化活性. 采用XPS、DRS、XRD、FT-IR、SEM、低温氮物理吸附对光催化剂进行表征. 结果表明, 掺杂S以S6+形式置换TiO2晶格中的Ti4+, 适量S 掺杂的Ti1-xSyO2在可见光区、紫外光区及太阳光下均表现出较高的光催化活性.掺杂S 在TiO2表面形成新的能级结构, 使催化剂吸收红移至450-550 nm, 诱发可见光催化活性;紫外光照射下, 新形成的能级结构与体相TiO2形成复合半导体结构, 捕获光生空穴, 提高光生电子鄄空穴分离效率.同时, S掺杂可以改善TiO2的分散性, 增加其比表面积SBET并提高相转变温度.     

WOx/TiO2光催化剂的可见光催化活性机理探讨

采用磁控溅射技术在用浸渍提拉法制得的TiO2薄膜上,溅射氧化钨层,通过气相反应中光催化降解二甲苯的实验表明,WOx/TiO2薄膜具有可见光活性.通过UV-Vis吸收光谱、X射线光电子能谱(XPS)等方法对其可见光活性的机理进行探索.UV-Vis吸收光谱表明WOx,TiO2对可见光响应的范围有一定的扩展,吸收强度增加.XPS表明WOx/TiO2薄膜表面形成了明显的W杂质能级和Ti缺陷能级,这是WOx/TiO2在可见光范围有一吸收的主要原因,也是光催化剂具有可见光活性的必要条件之一,同时杂质能级的存在使半导体费米能级上移,载流子增加,光催化效率提高.     

苯二胺对聚苯胺电化学合成及其降解的影响

运用循环伏安法和紫外 可见吸收光谱分别研究了邻、间、对 3种苯二胺单体对苯胺聚合及其生成膜降解过程的影响 .结果表明 ,对苯二胺在催化苯胺聚合的同时加速了膜的降解 ,而邻、间苯二胺对聚合与膜的降解均起抑制作用 .这可能是由于 3种苯二胺结构的不同影响了聚合机理 ,并在一定程度上改变了膜的化学物理性质所致 .扫描电镜显示 ,苯二胺的加入对聚合膜的形态结构也有明显影响 ,与纯聚苯胺膜相比 ,共聚膜变得更加致密、光滑 .     

Synthesis,Characterization, and Photocatalytic Activities of BiVO4 by Carbon Adsorption Hydrothermal Method

A new idea of prepared method for BiVO₄ nano-powders hydrothermal synthesis process was developed to avert the existent shortcomings of hydrothermal method. The thermal stability, phase structure, light absorption property, and morphology of the catalyst prepared were characterized by thermogravimetric analyzer (TG), X-ray diffraction (XRD), ultraviolet visible spectrophotometer (UV/Vis), and transmission electron microscopy (TEM), respectively. Using methyl orange (MO) as the target degradation material and a 500-W dysprosium lamp as the visible light source to investigate photocatalytic performance of BiVO₄. We successfully prepared BiVO₄ powders with small particle size, less agglomeration and uniform distribution by carbon adsorption hydrothermal method, and the absorption wavelength of light was red-shifted, these all rendered the absorption capacity of visible light region enhancing with 94 % high photocatalytic degradation rate of methyl orange at 60 min. And the possible mechanism was also discussed in this study.     

Role of oxygen in the degradation of atrazine by UV/Fe(III) process

In this study, the role of oxygen in the regeneration of Fe(III) during the degradation of atrazine in UV/Fe(III) process was studied. The degradations of atrazine in UV/Fe(III) and UV-photolysis processes in the presence and absence of oxygen were compared. The results showed that the degradations of atrazine in these processes followed the pseudo-first-order kinetics well. The process exhibiting the highest rate constant (k) was UV/Fe(III)/air process, because k-value for UV/Fe(III)/air process was about 1.47, 2.23 and 2.56 times of those for UV/Fe(III)/N₂, UV/air and UV/N₂ processes, respectively. The degradation of atrazine was enhanced by oxygen in UV/Fe(III) process and the enhancement was more remarkable at higher initial concentrations of Fe(III). The investigation into the changes of Fe(III) concentrations demonstrated that the presence of oxygen led to the regeneration of Fe(III), which resulted in the enhancement of atrazine degradation. With air bubbling, the ferric ions were 25% more than those with N₂ bubbling. The experimental data showed the regeneration of Fe(III) required the excited organic molecules and oxygen and on the basis of these results, the regeneration mechanism of Fe(III) was proposed. It was also found that due to the oxidation of Fe(II), the degradation of atrazine in UV/Fe(II)/air process was effective at a low Fe(II) concentration of 7 mg/L, similar to that in UV/Fe(III)/air process. This study makes clear the role of oxygen in the regeneration of Fe(III), and thus it provides a guide to reduce the input of Fe(III) and is helpful to the application of UV/Fe(III) process in practice.