臭氧提高纳米TiO2光催化活性的ESR分析

以5,5-二甲基-1-吡咯啉-N-氧化物(DMPO)为自由基捕获剂,分别以去离子水和二甲基亚砜(DMSO)为溶剂,利用电子自旋共振(ESR)方法对UV、O₃、TiO₂/O₃、TiO₂/UV/O₂、UV/O₃和TiO₂/UV/O₃这6种体系中形成的羟基自由基(·OH)和超氧阴离子自由基(·O₂^-)进行了检测,同时考察了反应时间、催化剂投量以及体系溶解氧对TiO₂/UV/O₃体系形成·OH和·O₂^-的影响.结果显示,在纳米TiO₂光催化体系中加入臭氧,能显著增加反应体系中·OH和·O₂^-自由基的生成量,6种体系中DMPO-·OH和DMPO-·O₂^-加合物的ESR波谱峰信号强度分别为:TiO₂/UV/O₃>TiO₂/UV/O₂>UV/O₃>UV>TiO₂/O₃>O₃和TiO₂/UV/O₃≈TiO₂/UV/O₂>TiO₂/O₃>UV>UV/O₃>O₃,在TiO₂/UV/O₃体系中成功监测到·O₃^-自由基的存在.     

水体中壬基酚光降解机理研究

在模拟太阳光条件下, 通过测定光解过程中壬基酚(NP)残留率和中间产物, 考察了溶解氧(DO), H₂O₂, NO₃^-及Cl^-对水体中NP光解的影响, 并推测了降解途径. 结果表明: DO浓度越低NP降解越慢, 产物有4-壬基-邻苯二酚、壬醇、壬醛和壬酸, 其中以壬酸为主, 推测NP在 O₂^·-作用下, 生成邻酚, 再发生共轭加成. H₂O₂, NO₃^-的添加显著加快NP降解速率, 产物有碳链缩短(2～8碳)的酚、4-壬基-邻苯二酚、壬醇、壬醛、壬酸, 其中以壬醛为主, H₂O₂, NO₃^-在光照下生成·OH, ·OH进攻NP电子云较集中的位置, NO₃^-吸收光同时产生·NO₂, 检测到2-硝基-4-壬基酚. 在H₂O₂存在下, Cl^-的添加对NP降解先促进后抑制, 并检测到壬酰氯, 推测·OH与Cl^-共存, 形成Cl₂^-参与反应, 氯代产物的前驱体可能是壬醛.     

在TiO2上CO的光催化氧化

最近在“氧化的”TiO₂(即表面无氧空位和Ti³⁺)上进行的CO光催化氧化研究发现:室温下,以黑光灯(峰值λ=365nm)光照时,“氧化的”TiO₂无CO催化氧化的活性,但以杀菌灯(峰值λ=253.7nm)光照时,则对CO产生显著的催化活性.参照CO在过渡金属表面的催化氧化机理,对本现象进行了解释:黑光灯照时,O₂在TiO₂表面只生成O_2(a)^-,而O_2(a)^-不能使CO氧化,只有以杀菌灯照时,TiO₂表面产生O_(a)^-,CO氧化反应才能发生.     

H2O2/TiO2超声协同光降解活性艳橙的研究

以活性艳橙溶液为模拟废水,通过H₂O₂/TiO₂超声(US)协同作用光降解活性艳橙溶液,探讨了TiO₂催化剂用量、H₂O₂用量、活性艳橙溶液的初始浓度、pH值、TiO₂催化剂锻烧温度等对活性艳橙溶液降解率的影响,并比较了几种不同作用方式对活性艳橙溶液的降解效果.结果表明:UV/H₂O₂/TiO₂/US协同作用降解活性艳橙溶液的效果最好;当活性艳橙溶液的初始浓度为20 mg·L^-1,pH＝5,TiO₂用量为0.4 g·L^-1,H₂O₂用量为0.4 ml·L^-1时,降解率可达92.06%.     

微波诱导组装CuS@MoS2核壳纳米管及其光催化类芬顿反应研究

采用微波诱导组装,先将Cu纳米线硫化成空心CuS纳米管,再将片状MoS₂均匀插层并组装在CuS纳米管表面上,形成CuS@MoS₂核壳纳米管,用于可见光（λ>420 nm）催化类芬顿反应降解高浓度污染物罗丹明B（RhB）,30 min内降解率达100%.高活性归因于MoS₂独特的多层次结构增加了催化剂对光的吸收,提高了光利用率.同时,MoS₂与CuS之间形成的异质结结构有利于光生电子的转移,抑制了光生载流子的复合.更为重要的是构建了光催化与类芬顿反应的协同作用机制,光催化组分CuS中的铜离子与双氧水作用构成类芬顿循环体系并生成羟基自由基（·OH）,光生电子一方面与双氧水反应生成·OH,另一方面与MoS₂活化的分子氧反应产生超氧自由基（·O₂^-）,·OH和·O₂^-协同氧化污染物,可大幅度提高污染物去除效率.本工作开发的可循环光催化-芬顿反应体系,为实际污染治理开辟了新途径.     

离子色谱法同时测定饮水中9种阴离子

建立离子色谱抑制电导检测法同时测定饮水中F^-、Cl O₂^-、Cl^-、NO₂^-、Cl O₃^-、Br^-、NO₃^-、H₂PO₄^-和SO₄^2-9种阴离子的方法。采用SH-AP-2型阴离子交换柱为分离柱，以4.0 mmol/L Na₂CO₃-4.0 mmol/L Na HCO₃溶液为淋洗液，流量为0.80 m L/min，采用等度洗脱方式将9种阴离子完全分离，利用抑制电导检测。Cl O₂^-、Cl O₃^-的质量浓度在0.05～2.0 mg/L范围内，SO₄^2-     

C/Cr2O3/TiO2复合材料的制备及其光催化性能研究

本文以制革含铬革屑为原材料,基于矿物鞣剂复鞣的原理,将Ti(IV)均匀、稳定地负载到含铬革屑上,在氮气氛围下,经高温热解制备得到C/Cr₂O₃/TiO₂光催化剂,并研究了其对四环素(TC)的光催化降解效果及机理。结果表明,C/Cr₂O₃/TiO₂光催化剂具有明显的介孔结构,比表面积较大,为277.47 m²·g^-1,Cr₂O₃和TiO₂已实现复合并负载在生物炭(C)上。通过光催化降解发现,在模拟自然光照下,当催化剂用量为0.04 g,TC初始浓度为50 mg·L^-1,溶液pH为2时,TC的去除率可高达99.99%。结合自由基捕获实验发现,C/Cr₂O₃/TiO₂光催化剂对TC的降解作用主要依靠反应体系中产生的大量·O₂^-,·OH和h⁺。     

可漂浮CA/TiO2/RGO光催化剂的制备及其性能探究

首先利用氧化石墨烯(GO)改性TiO₂,然后以碳酸钙-碳酸钠为造孔剂，通过海藻酸钙(CA)固载TiO₂/GO制备CA/TiO₂/GO凝胶微球，最后该微球经抗坏血酸水浴还原GO,获得可漂浮CA/TiO₂/RGO微球作光催剂；并采用FT-IR、XRD、SEM、UV-Vis DRS以及TGA等测试手段对CA/TiO₂/RGO形貌及结构进行表征分析，初步探究CA/TiO₂/RGO对氨基黑10B降解性能和机理。结果表明：于30 mg/L氨基黑10B染料溶液中，投加CA/TiO₂/RGO光催剂浓度为1.84 g/L,220 min内CA/TiO₂/RGO对氨基黑10B的降解率可达80%,降解过程符合一级反应动力学模型，其光催化降解的主要活性物种是·O₂^-,而·OH和h⁺在本降解中起到作用相对较小。     

NH3与Cl2在y-Al2O3颗粒物表面的非均相反应

使用离子色谱分析了常温、常压、湿润和氧气存在条件下,NH₃和Cl₂在γ-Al₂O₃颗粒物表面非均相反应的产物及其受NH₃浓度、反应时间等的影响;并定量分析了NH₃、Cl₂、SO₂和NO₂单独及共存条件下,γ-Al₂O₃表面Cl^-、NO₃^-和SO₄^2-等二次无机颗粒物的生成总量.结果表明：NH₃和Cl₂在γ-Al₂O₃表面具有协同作用,2 h后Cl^-的生成总量可达589.65 μg,其生成量随时间延长而不断增加.表面氯化物的生成量在NH₃浓度为400 ppm时达到峰值,且随NH₃浓度的增加呈先增加而后减少的趋势.活性氯存在下,NH₃对颗粒物表面Cl^-、NO₃^-和SO₄^2-的生成有促进作用,且四种气体共存时复合正反馈效应最明显.同时,本研究对NH₃和Cl₂在颗粒物表面的非均相反应机理及活性氯和氨的排放对大气中二次无机颗粒物的贡献进行了探讨.     

几种光催化反应体系中羟基自由基表观生成率的实验研究

采用邻二氮啡-Fe(Ⅱ)(橙红色)分光光度法间接测定了Fenton、UV/Fenton、UV/草酸铁/H₂O₂、UV/TiO₂4种体系中在不同条件下·OH的表观生成率,初步探讨了体系中各影响因子的作用机制.结果分析表明:对于Fenton体系、UV/Fenton、UV/草酸铁/H₂O₂而言,其最佳反应条件为pH=4.0、m(H₂O₂)/m(Fe)=1/25、铁离子的质量浓度以25 mg/L左右为宜;TiO₂光催化体系催化产生的·OH尽管受环境pH的影响相对较小,但在同等条件下·OH的表观生成率最低;4种体系中以UV/草酸铁/H₂O₂体系中·OH表观生成率最高,而且以线性的规律递增.     

TiO2负载Pt对光催化去除低浓度NO性能的影响

以溶胶-凝胶法以及湿式浸渍法制备了Pt/TiO2催化剂,采用了XRD、BET、UV-vis、TEM、XPS等方法进行表征,并进行了对NO的催化氧化性能测试.结果表明铂的负载能显著提高TiO2光催化剂对NO的氧化转化能力和去除率.0.5%Pt/TiO2对NO的氧化率与去除率分别为45.0%和38.1%,与纯锐钛矿TiO2(13.6%,10.7%)相比,氧化效率提高3.3倍,去除效率提高3.6倍.通过比较不同方法制备的负载Pt催化剂的活性,初步讨论了催化剂表面发生的反应机理:铂氧化物以及催化剂表面吸附的O2分子通过与光生电子和光生空穴结合,产生了强氧化性自由基,将NO氧化得到NO2.     

TiO2光催化降解胸腺嘧啶的动力学和机理

考察了用于降解来自嘧啶家族的一种核酸—胸腺嘧啶(C5H6N2O2)的高级氧化过程。结果发现,在光催化剂TiO2作用下,胸腺嘧啶的光降解进行得很快,且在紫外光照射和水溶液中时更为明显。研究了胸腺嘧啶在TiO2催化剂上的吸附、降解动力学、以及pH值对光催化降解胸腺嘧啶性能的影响。另外,考察了胸腺嘧啶降解产物的矿化;比较和讨论了在光催化过程中胸腺嘧啶的消失和矿化速率。同时还研究了氮的矿化,确立了中间产物的识别方法。最后,采用电子密度计算提出了在紫外光照射下TiO2催化剂上胸腺嘧啶降解的可能化学途径。     

Kinetics of heterogeneous photocatalytic degradation of reactive dyes in an immobilized TiO2 photocatalytic reactor

The photocatalytic degradation of two reactive dyes has been investigated by UV/TiO2/H2O2 using an immobilized TiO2 photocatalytic reactor. Reactive Blue 8 (RB 8) and Reactive Blue 220 (RB 220) textile dyes were used as model compounds. Photocatalytic degradation processes were performed using a 5-L solution containing dyes. The initial concentrations of dyes were 50 mg/L. The radiation source was two 15 W UV-C lamps. A batch mode immersion photocatalytic reactor was utilized. UV-vis and ion chromatography (IC) analyses were employed to obtain the details of the photodegradation of the selected dyes. Colored synthetic waters were completely decolorized in relatively short time after UV irradiation in the presence of various concentrations of hydrogen peroxide. Formate, acetate, oxalate, and glyoxylate anions were detected as dominant aliphatic intermediates where they were further oxidized slowly to CO2. The UV/TiO2/H2O2 process was able to oxidize the dyes with partial mineralization of carbon, nitrogen, and sulfur heteroatoms into CO2, NO3-, and SO4(2-), respectively. Kinetics analysis indicates that the photocatalytic decolorization rates of the dye can be approximated by a pseudo-first-order model. The UV/TiO2/H2O2 process proved to be capable of decolorization and mineralization of the reactive dyes (RB 8 and RB 220).     

氟离子对TiO2/膨润土光催化降解酸性桃红的影响

研究了在紫外光照射下, 添加氟离子对P25(锐钛矿)和TiO2/膨润土光催化降解酸性桃红(SRB)的影响. 紫外可见光谱测定结果表明无氟的反应体系, pH值越小, 光降解速率越快; pH值固定, 添加氟离子越多, 反应速率越快, 在TiO2/膨润土催化剂上, 当氟离子浓度达到一定程度时, 反应速率不再变化. 在P25和TiO2/膨润土催化剂上, 添加氟离子对H2O2的产生量影响不同, 通过电子顺磁共振(EPR)技术探测到了超氧自由基和羟基自由基, 这两个体系添加氟离子对其产生强度影响不同, 这可能是因为TiO2/膨润土催化剂为层状结构, BET 比表面积较大, 经XRD和TEM测试表明其晶粒直径约为57.9 nm. TiO2/膨润土催化剂连续循环使用11次, 光催化活性基本不变, 这个现象说明TiO2/膨润土催化剂既易于从分散体系中分离出来, 而且其稳定性也好, 它是一个有应用前途的催化剂.     

石墨烯/电气石/二氧化钛复合材料的制备及其光催化降解异丙醇性能

光催化是一种理想的应对全球能源短缺和环境污染问题的绿色化学技术,可以实现有机物降解、水分解和二氧化碳光还原等.光催化反应效率受诸多因素影响,其中光生载流子(电子和空穴)的分离和传输具有至关重要的作用.以往研究表明,构筑多元复合光催化材料体系有利于光生电子和空穴有效分离和传递,促进催化剂表面的还原和氧化反应,从而提高其光催化效率.基于以上考虑,我们提出了一种新型的石墨烯/电气石/TiO2三元复合光催化材料体系,其中TiO2因其价格低廉、无毒和抗光腐蚀等优点而被广泛用作光催化材料;石墨烯(G)拥有独特的二维结构、高的电子迁移率、大的比表面积,是一种优异的催化剂载体;电气石(T)的一个重要性质是表面存在自发极化的静电场,该静电场将会影响光激发载流子的分离、传递和光催化反应过程.利用水热法合成了不同成分的石墨烯/电气石/TiO2三元复合材料体系.为了对比研究石墨烯表面电荷性质的影响,其中一组的石墨烯(氧化石墨)为直接采用改良的Hummers法所制备,其表面带负电;另一组的石墨烯经聚二烯丙基二甲基氯化铵(PDDA)修饰,使其表面带正电.X射线衍射结果显示,三元复合材料中TiO2为锐钛矿相,其结晶性没有因为与石墨烯和电气石的复合而受到影响.扫描和透射电子显微分析表明,TiO2的平均颗粒大小为15 nm左右,并且与石墨烯和电气石均匀复合.傅里叶变换红外光谱和zeta电位表征分析证实,PDDA可以有效地对石墨烯进行功能化改性,使其表面带正电.紫外-可见分光光谱显示,石墨烯/电气石/TiO2三元复合材料与TiO2的吸收带边一致,复合材料中石墨烯和电气石并没有改变TiO2的光吸收特征.光催化降解异丙醇实验表明,石墨烯/电气石/TiO2三元复合材料优于单纯的TiO2、石墨烯/TiO2以及电气石/TiO2二元复合材料,当石墨烯和电气石的质量百分比分别为0.5%和5%时,三元复合材料降解异丙醇产生丙酮的速率达到最高(223μmol/h).特别值得指出的是,由表面带负电的石墨烯组成的复合材料比由带正电荷的PDDA-石墨烯组成的复合材料具有更高的光催化性能,原因如下:在水溶液中显示正zeta电位值的TiO2与带负电的石墨烯/电气石复合物静电吸引而均匀紧密复合,有利于TiO2中光生电子和空穴的快速分离和传递,从而使得石墨烯/电气石/TiO2三元复合材料具有较高的光催化性能;而带正电的PDDA-石墨烯/电气石复合物和TiO2颗粒相互排斥而不宜复合,导致PDDA-石墨烯基复合材料的光催化活性降低.机理研究揭示,在三元复合材料光催化降解异丙醇的反应中起主要作用的是光生电子和空穴.基于以上研究结果,我们提出了三元复合材料光催化降解异丙醇的反应机理.     

Photodegradation of the aminoazobenzene acid orange 52 by three advanced oxidation processes: UV/H2O2, UV/TiO2 and VIS/TiO2: Comparative mechanistic and kinetic investigations

This paper presents the results obtained from the oxidation of the aminoazobenzene dye AO52 by the UV/H₂O₂, UV/TiO₂ and VIS/TiO₂ systems. In the former case, we investigated the formation of first by-products by means of GC/MS, HPLC and ¹H NMR. spectroscopy. We conclude that hydroxyl radicals are added to aromatic rings in the ipso position with respect to the sulfonate group or to the azo-linkage-bearing carbon. The reaction of the inorganic radical with the N,N-dimethylamino substituent, leading to demethylation, adds to the multiplicity of the possible pathways. Degradation by the UV/TiO₂ system is pH dependent. Whereas hydroxyl radicals are the main oxidative agent in neutral and alkaline solutions, positive hole-induced oxidation competes with the reduction of the protonated dye molecules in acid media. Moreover, FTIR spectroscopy of AO52/TiO₂ wafers provided an insight to the nature of the photoproducts. This process is very efficient since only ultimate breakdown products, i.e. aliphatic acids and inorganic salts, are detected. Similar results were obtained using visible light as the irradiation source in the case of wafers whereas in heterogeneous solutions, the dye seems to be resistant to degradation.     

Interaction of NO2 with TiO2 surface under UV irradiation: products study

The interaction of NO(2) with TiO(2) solid films was studied under UV irradiation using a low pressure flow reactor (1-10 Torr) combined with a modulated molecular beam mass spectrometer for monitoring of the gaseous species involved. HONO, NO, and N(2)O were observed as the products of the reactive uptake of NO(2) to the illuminated TiO(2) surface with the sum of their yields corresponding nearly to 100% of the nitrogen mass balance. The yield of the products was measured as a function of different parameters such as irradiance intensity, relative humidity (RH), temperature, and concentrations of NO(2) and O(2). The yield of N(2)O was found to be 0.15 ± 0.05 independent of the experimental conditions. The distribution of the products between NO and HONO was found to be independent of temperature in the range T = 280-320 K and was governed by relative humidity: increase in RH led to lower NO and higher HONO yield, with a maximum of nearly 65% reached at ~5% RH. Presence of molecular oxygen was shown to shift the HONO/NO distribution to HONO at low RH (<5%) with no effect at higher RH where the HONO yield is maximum. The following values for the yield of the products of NO(2) interaction with pure TiO(2) under real atmospheric conditions can be recommended from this work: 0.65 ± 0.10, 0.05 ± 0.05, and 0.15 ± 0.05 for HONO, NO, and N(2)O, respectively. The mechanism of the photoinitiated heterogeneous reaction and possible atmospheric implications of the obtained results are discussed.     

Pathway of oxygen incorporation from O2 in TiO2 photocatalytic hydroxylation of aromatics: oxygen isotope labeling studies

The hydroxylation process is the primary, and even the rate-determining step of the photocatalytic degradation of aromatic compounds. To make clear the hydroxylation pathway of aromatics, the TiO(2) photocatalytic hydroxylation of several model substrates, such as benzoic acid, benzene, nitrobenzene, and benzonitrile, has been studied by an oxygen-isotope-labeling method, which can definitively assign the origin of the O atoms (from oxidant O(2) or solvent H(2)O) in the hydroxyl groups of the hydroxylated products. It is found that the oxygen source of the hydroxylated products depends markedly on the reaction conditions. The percentage of the products with O(2)-derived hydroxyl O atoms increases with the irradiation time, while it decreases with the increase of substrate concentration. More intriguingly, when photogenerated valence-band holes (h(vb)(+)) are removed, nearly all the O atoms (>97?%) in the hydroxyl groups of the hydroxylated products of benzoic acid come from O(2), whereas the scavenging of conduction-band electrons (e(cb)(-)) makes almost all the hydroxyl O atoms (>95?%) originate from solvent H(2)O. In the photocatalytic oxidation system with benzoic acid and benzene coexisting in the same dispersion, the percentage of O(2)-derived hydroxyl O atoms in the hydroxylated products of strongly adsorbed benzoic acid (ca. 30?%) is much less than in that of weakly adsorbed benzene (phenol) (>60?%). Such dependences provide unique clues to uncover the photocatalytic hydroxylation pathway. Our experiments show that the main O(2)-incorporation pathway involves the reduction of O(2) by e(cb)(-) and the subsequent formation of free (?)OH via H(2)O(2), which was usually overlooked in the past photocatalytic studies. Moreover, in the hydroxylation initiated by h(vb)(+), unlike the conventional mechanism, the O atom in O(2) cannot incorporate into the product through the direct coupling between molecular O(2) and the substrate-based radicals.     

CO Preferential oxidation promoted by UV irradiation in the presence of H2 over Au/TiO2

The catalytic oxidation of CO was performed over Au/TiO(2) under UV irradiation in the presence of H(2) in different reaction systems. It was found that the introduction of H(2) enhanced the CO thermocatalytic oxidation in a CO pre-introduced system (CO/O(2)vs. CO/H(2)/O(2)), but suppressed that in an O(2) pre-introduced (O(2)/CO vs. O(2)/H(2)/CO) system. Although the CO oxidation in both CO/H(2)/O(2) and O(2)/H(2)/CO systems could be remarkably enhanced under UV irradiation, the oxidation of H(2) was suppressed under UV irradiation. It was proposed that the dissociative chemisorption H ([triple bond]Ti-H) at surface oxygen vacancy sites of TiO(2) could act as both the electron-acceptors for the photogeneration electrons and the electron-donors for the chemisorbed O(2) at TiO(2), and thus enhance the CO oxidation during the coinstantaneous process of thermocatalysis and photocatalysis. The suppression of H(2) thermocatalytic oxidation under UV irradiation might be ascribed to the electron transfer effect, i.e., the dissociative chemisorption H on Au (Au-H) could be desorbed at the H(2) molecule via accepting the photogenerated electrons from TiO(2).     

Gd掺杂TiO2/活性炭纤维复合材料的制备及表征

以TiCl4和Gd(NO3)3·6H2O为主要原料,采用酸催化水解法制备Gd掺杂TiO2光催化剂并通过浸涂法将其负载在活性炭纤维(ACF)表面,制得Gd掺杂TiO2/ACF复合材料。 以气相苯为模型物,考察材料的光催化活性。 利用XRD、FTIR及GC-MS对催化剂的晶相结构、光谱特征等进行了表征。 结果表明,Gd掺杂能有效抑制TiO2的晶粒生长。 Gd掺杂量、浸涂次数影响TiO2/ACF光催化活性,Gd2O3掺杂质量分数为0.48%、浸涂2次的TiO2/ACF活性最高。 在苯光催化氧化后的Gd掺杂TiO2/ACF复合材料表面未发现醌类中间产物的存在。 Gd的掺入能减缓催化剂失活,光催化反应100 min后仍能表现出较高活性。