浅池型TiO2/ACF光催化降解水中苯酚的研究

为了提高光催化过程的降解速率，本文以涂覆法制得的二氧化钛/活性炭纤维（TiO2/ACF）为光催化剂，300 W(365 nm)高压汞灯为光源，研究了浅池型反应器中苯酚在TiO2/ACF上的光催化降解动力学；探讨了光强度、高压汞灯滤光以及光源种类对降解反应的影响，并对光氧化，光催化和吸附过程进行了比较。结果表明：光氧化对苯酚的降解无效果，光催化降解速率常数与吸附速率常数之比为3.35/1；光强越大，光催化降解速率越快；高压汞灯不滤光时光催化降解速率明显加快，但光催化反应仍遵循准一级反应动力学方程；波长为254 nm紫外杀菌灯的降解效果高于波长为365 nm高压汞灯滤光后的降解效果。     

TiO2/BixTiyOz气相光催化降解苯的动力学模型及反应机理

在密闭不锈钢反应器内考察了TiO2/BixTjyOz催化剂气相光催化降解苯的性能.结果表明,TiO2负载于Bi12TiO20,Bi2Ti2O7和Bi4Ti3O12上制成的催化剂,光催化活性得到很人的提高,TiO2最佳负载量为2.0%;其中,TiO2/Bi12TiO20的光催化活性最高,苯最高转化率是纯TiO2的2倍,催化剂使用寿命也延长了1倍.在本文实验条件下,TiO2/Bi12TiO20上苯气相光催化降解符合Lang-muir-Hinshelwood动力学模型,光催化反应速率常数k和Langmuir吸附常数K分别为0.006 4mg/(L·min)和9.670 2L/mg.采用红外光谱对失活的催化剂进行表征,结果表明催化剂表面出现了羰基与羟基等的振动峰,同时检测到主要的中间产物是2,6-二叔丁基-4-甲基苯酚,它吸附在催化剂表面活性化上而导致催化剂失活.最后推测了苯在催化剂表面气相光催化降解的反应机理.     

SO4^2—／TiO2固体酸催化剂的酸强度及光催化性能

SO4^2-/TiO2固体酸可用于光催化降解溴代甲烷,其光催化性能明显优于TiO2光催化剂,晨相同反应条件下,SO4^2-/TiO2的光催化活性比TiO2提高2－10倍,当H2S4浸渍液浓度为1mol/L时,制得的SO4^2-/TiO2酸性最强（H0＜－12.14）,具有超强酸性和最高的光催化活性。     

循环流动固定床光催化反应器动力学数学模拟

以甲基橙为模型反应物,研究了连续循环固定床光催化反应器的动力学过程.根据光催化氧化过程特点,分析并建立了准一级反应动力学方程,对该反应系统的动力学过程进行动态数学模拟,用四阶Runge-Kutta法进行数值计算,结果表明数学模拟与实验数据相吻合.在该光催化反应体系中,处理量增加时实际反应速率常数k基本不变,而表观反应速率常数kapp变小,二者之间关系与反应器体积对处理量体积比（γ）密切相关;反应速率常数受起始浓度影响很大,在15～150 μmol•L－1浓度范围内,lnk=－0.48ln[c0]＋1.42;反应速率常数与光强的关系为k∝I0.5;反应速率常数受溶液pH值的影响也很大.     

纳米TiO_2光催化芳香醛的缩醛反应研究

本文以纳米TiO2为催化剂,UV-LED（=365 nm）为紫外光源,在自制的恒温石英玻璃光催化反应器中成功实现了芳香醛的非均相光催化缩醛反应.以乙醇等作为溶剂和反应物,快速高效和高选择性地合成了苯甲醛二乙基缩醛（BDA）.在光强为0.6 mw/cm2,苯甲醛初始浓度为0.05 mol/L,催化剂TiO2（P25）用量为5.0 g/L,反应时间为15 min的条件下,苯甲醛二乙缩醛的产率可达99.86%.研究表明,氧气的存在是顺利发生光催化缩醛反应的重要条件.反应液pH值、醇溶剂种类及苯环对位取代基等因素都会对光催化缩醛反应速率和产率产生影响.pH值及醇溶剂的pKa越小,缩醛反应速率越快.苯环上对位取代基会抑制缩醛反应的进行,其中供电子取代基相对吸电子取代基更有利于缩醛反应进行.结合实验,提出了光催化缩醛反应的机理.     

气相苯在TiO2光催化剂上吸附常数和光催化反应常数测定

采用溶胶-凝胶法制备TiO2光催化剂以及掺杂Fe3 和Ce3 的TiO2光催化剂,进行间歇式光催化降解气相苯动力学实验,基于光催化Langmuir-Hinshelwood反应动力学模型(L-H模型),测定气相苯在3种光催化剂上的降解动力学常数和吸附平衡常数.根据光催化降解气相苯实验动力学曲线和L-H模型,估算出TiO2、Fe3 /TiO2和Ce3 /TiO2光催化剂光催化降解苯的反应速率常数k和Langmuir吸附常数K分别为0.5247g/m3·min、1.523g/m3·min、1.010g/m3·min和8.605×10-2m3/g、2.390×10-2m3/g、3.928×10-2m3/g.掺杂Fe3 和Ce3 可明显提高光催化剂光催化降解苯的反应速率常数k,其中Fe3 /TiO2,的反应速率常数k最大.     

TiO2光催化降解苯和甲苯的动力学研究

利用溶胶-凝胶法制备了粒径约为13nm、晶型为锐钛矿相和金红石相混晶的TiO2光催化剂,并利用此催化剂对挥发性有机污染物苯和甲苯进行了光催化降解研究,对不同的催化剂用量、光源、污染物的初始浓度以及氧气对光催化反应速率的影响进行了研究。结果表明,光催化降解甲苯和苯的反应均符合假一级动力学方程,光强与光催化降解甲苯的反应的速率常数之间呈指数关系,光波长对光催化降解苯的影响也很显著;随着甲苯和苯初始浓度的增加,光催化反应速率常数降低;氧气加快了光催化降解甲苯和苯的速率;对于光催化降解初始浓度为37.6μmol/L的甲苯而言,催化剂的最佳使用量为0.30g,对于光催化降解初始浓度为9.0μmol/L的苯来说,催化剂的最佳用量为0.10g。     

碳含量对C/TiO2复合材料光催化活性的影响

 通过热解单层分散在TiO2表面的蔗糖制得了碳均匀覆盖的C/TiO2复合材料,并采用X射线衍射、紫外-可见漫反射吸收光谱和N2物理吸附等方法对复合材料进行了表征. 以亚甲基蓝和罗丹明B为模型化合物评价了C/TiO2复合材料在紫外和可见光照射下的光催化性能,考察了碳含量对催化活性的影响. 结果表明,光源不同,污染物不同,碳含量不同对催化活性的影响均不相同. 对于考察的三个碳含量的C/TiO2催化剂,在紫外光照射下,前驱体中蔗糖/氧化钛质量比为0.1时制得的C/TiO2光催化降解亚甲基蓝的活性最高,蔗糖/氧化钛质量比为0.2时制得的C/TiO2光催化降解罗丹明B的活性最高; 在可见光照射下,蔗糖/氧化钛质量比为0.05时制得的C/TiO2光催化降解亚甲基蓝和罗丹明B的活性都最高.     

微反应器中二氧化钛/过氧化氢协同光催化降解及其应用

在微流控芯片中利用二氧化钛/过氧化氢(TiO2/H2O2)催化体系进行有机物的光催化降解及环境水样重金属分析.通过在微流控芯片中涂覆多孔纳米TiO2涂层,并以UV-LED为光源,制备光催化微反应器.以H2O2为光催化氧化剂,在光强为80 mW/cm2,流速为1000 μL/h,H2O2浓度为8%时,光反应时间为19 s的条件下,0.2 mmol/L 亚甲基兰降解率可达99.6%.将此方法应用于含富里酸水样中Cd2+和Zn2+含量的测定,水样中2.5 g/L富里酸可在96 s内基本降解完全,释放出被吸附的Cd2+和Zn2+,实现准确测定.本方法具有降解效率高, 二次污染少, 分析速度快等优点,在环境水样分析中有较好的应用前景.     

TiO2－SnO2复合纳米膜的制备及其光催化降解甲苯的活性

 采用溶胶－凝胶法制备了nano－TiO2－SnO2复合溶胶，经一次镀膜就能在玻璃上得到没有缺陷、结构紧密均匀的nano－TiO2－SnO2复合膜．通过扫描电镜观察到复合膜颗粒为球形，比纯TiO2膜的颗粒小，平均粒径为15nm，且粒径分布非常均匀．以空气中的有机挥发物甲苯模拟污染物，测定了nano－TiO2－SnO2复合膜的光催化降解性能．结果表明，n（SnO2）／n（TiO2）＝0．05的nano－TiO2－SnO2复合膜催化剂具有最高的光催化活性，且比纯TiO2膜的活性高；甲苯初始浓度为920mg／m3时，反应5h甲苯完全降解．XRD分析表明，此复合物具有锐钛矿和金红石两种TiO2晶相，没有检测到SnO2的特征峰．     

Photocatalytic reactivity of surface platinized TiO2: substrate specificity and the effect of Pt oxidation state

Surface platinized TiO(2) (Pt/TiO(2)) has been frequently studied, but its photocatalytic reactivities reported in the literature are not consistent in some cases. To understand the discrepancies, the effects of Pt speciation on TiO(2) on the photocatalytic degradation (PCD) of a few chlorinated organic compounds (trichloroethylene (TCE), perchloroethylene (PCE), dichloroacetate, etc.) were investigated with several Pt/TiO(2) samples that were prepared differently. The oxidation state of Pt deposits was analyzed by X-ray photoelectron spectroscopy and was found to be the most important factor in determining the initial PCD rates of chlorinated organic compounds. TiO(2) with oxidized Pt species (Pt(ox)/TiO(2)) was less reactive than TiO(2) with metallic Pt (Pt(0)/TiO(2)) for all substrates tested. In particular, Pt(ox)/TiO(2) strongly inhibited the PCD of TCE and PCE whereas it was more reactive than pure TiO(2) for the PCD of other compounds. The photocurrents obtained with the Pt(ox)/TiO(2) electrode were lower than those with the Pt(0)/TiO(2) electrode, which was ascribed to the role of Pt(ox) species as a recombination center. It is proposed that TCE adsorbed on Pt(ox) chemically mediates the charge recombination through the redox cycle of TCE. The Pt effects in photocatalysis are highly substrate-specific and depend on the Pt-substrate interaction as well as the properties of Pt deposits.     

对甲基苯磺酸废水光催化氧化处理的正交试验研究(英文)

在TiO2悬浮体系下,采用对甲基苯磺酸模拟废水进行半导体光催化氧化降解静态试验;利用正交试验研究了光催化氧化降解的主要影响因素(pH值、催化剂用量、光照强度、光照时间).结果表明:在一定条件下,催化剂投加量、溶液pH、照射光强度及光照时间均存在一个最佳值;依据其影响对甲基苯磺酸废水光催化降解反应的大小,各因素排列顺序为:光照时间(光照强度(初始pH(催化剂用量.在试验最佳条件下(pH=3,催化剂用量80 mg.L-1,光照强度500 W,光照时间120 min),对甲基苯磺酸能够完全降解.     

GAS-PHASE PHOTOCATALYTIC OXIDATION OF CHCl CCl_2 AND Ph Me BY SUPPORTED TITANIA

ＧＡＳ┐ＰＨＡＳＥＰＨＯＴＯＣＡＴＡＬＹＴＩＣＯＸＩＤＡＴＩＯＮＯＦＣＨＣｌＣＣｌ２ＡＮＤＰｈＭｅＢＹＳＵＰＰＯＲＴＥＤＴＩＴＡＮＩＡＬｉＬｉｎ（ＤｅｐａｒｔｍｅｎｔｏｆＣｈｅｍｉｃａｌＥｎｇｉｎｅｅｒｉｎｇ，ＴｓｉｎｇｈｕａＵｎｉｖｅｒｓｉｔｙ，Ｂ...     

Preparation and Performances of RuO2/TiO2 Films Photocatalyst Supported on Float Pearls

"RuO2/TiO2 films were deposited on float pearls (FP) by the sol-gel-dipping method. The substrates were coated with RuO2/TiO2 precursor sol, air-dried at 120 oC and further heated at 500 oC to obtain the coupled photocatalyst of RuO2/TiO2 films supported on FP (RuO2/TiO2/FP). The structure of coupled photocatalyst was characterized by SEM, XRD, and FT-IR technique, respectively. The results showed TiO2 has anatase structure and doped RuO2 was highly dispersed on the surface of TiO2 particles as amorphous. The average thickness of RuO2/TiO2 films (3 layers) on FP was determined to be about 1 1m. This study was carried out under the following conditions: volume 60 mL, initial concentration of beta-cypermethrin (BEC) 45 mg/L, pH 6.5, amount of RuO2/TiO2/PF 5 g/L, air flow rate 200 mL/min, reaction time 60 min. The degradation rates of BEC are 88.1% (125 W Hg lamp), 82.8% (8 W UV lamp), and 75.1% (8 W solar lamp), respectively. The photocatalytic degradation of BEC was experimentally demonstrated to follow the Langmuir-Hinshelwood kinetic model, and the reaction rate constant (17.5 mg/(L min)) and the adsorption constant (3.486 L/g) were determined, respectively. It was also found that the RuO2/TiO2 /FP photocatalyst has significantly the visible light photoactivity for degradation of BEC."     

Mechanistic studies of the photocatalytic oxidation of trichloroethylene with visible-light-driven N-doped TiO2 photocatalysts

Visible-light-driven TiO2 photocatalysts doped with nitrogen have been prepared as powders and thin films in a cylindrical tubular furnace under a stream of ammonia gas. The photocatalysts thus obtained were found to have a band-gap energy of 2.95 eV. Electron spin resonance (ESR) under irradiation with visible light (lambda > or = 430 nm) afforded the increase in intensity in the visible-light region. The concentration of trapped holes was about fourfold higher than that of trapped electrons. Nitrogen-doped TiO2 has been used to investigate mechanistically the photocatalytic oxidation of trichloroethylene (TCE) under irradiation with visible light (lambda > or = 420 nm). Cl and O radicals, which contribute significantly to the generation of dichloroacetyl chloride (DCAC) in the photocatalytic oxidation of TCE under UV irradiation, were found to be deactivated under irradiation with visible light. As the main by-product, only phosgene was detected in the photocatalytic oxidation of TCE under irradiation with visible light. Thus, the reaction mechanism of TCE photooxidation under irradiation with visible light clearly differs markedly from that under UV irradiation. Based on the results of the present study, we propose a new reaction mechanism and adsorbed species for the photocatalytic oxidation of TCE under irradiation with visible light. The energy band for TiO2 by doping with nitrogen may involve an isolated band above the valence band.     

铁锌柱撑膨润土催化剂的制备及其对甲基橙废水的光催化降解性能

采用微波辐照促进的溶胶浸渍法制备了铁锌柱撑膨润土催化剂;用制备的催化剂对甲基橙溶液在可见光照射下进行降解,探讨了铁负载量、H2O2质量浓度、溶液初始pH、反应时间和催化剂投加量对甲基橙降解率的影响,并考察了催化剂的重复利用性能.结果表明,在pH为3、H2O2质量浓度100mg/L、催化剂投加量1.5g/L、反应时间为2h条件下,甲基橙降解率可达97%.     

紫外高级还原技术还原降解水中N-亚硝基二甲胺

采用2种高级还原技术(UV/Na2SO3和UV/Na2S2O4)还原降解N-亚硝基二甲胺(NDMA),考察pH值、光照强度、还原剂质量浓度和溶解氧等因素对NDMA还原降解效果的影响,计算还原降解反应过程中的表观反应动力学常数,推断NDMA的还原降解机理.研究结果表明,弱酸性条件下有利于2种高级还原技术对NDMA的还原降...     

EPR characterization of carbonate ion effect on TCE and PCE decomposition by gamma-rays

Carbonate ions significantly inhibit the decomposition of TCE (trichloroethylene) and PCE (perchloroethylene) by gamma-rays. The inhibition effect is larger in the case of TCE than PCE due to a greater dependence of TCE decomposition on hydroxyl radicals. The inhibition effect of carbonate ions was characterized by an EPR/spin-trapping technique. The intensity of DMPO-OH adduct signal decreased as the carbonate ion concentration increased and the percent of signal reduction was linearly proportional to the logarithm of carbonate ion concentration. This directly proves that the carbonate ions inhibit the decomposition of TCE and PCE by scavenging hydroxyl radicals.     

活性炭负载纳米TiO_2光催化降解甲醛废水研究

甲醛对人和温血动物的毒性很强,如果人类长期饮用被甲醛污染的水源,会引发头昏、贫血以及各种神经系统疾病.为此,研究学者对甲醛废水的处理进行了很多的试验研究.目前处理甲醛废水的主要方法有:芬顿法、光催化氧化法、湿式氧化处理等高级氧化技术,二氧化氯法,蒸汽吹脱法,氧化吸附法,SBR工艺等.     

二氧化钛纳米粒子和纳米管的合成、表征及对硝基苯的光催化性能研究

采用水热合成法, 通过改变反应条件, 控制反应参数, 成功地合成了粒径可控的球形TiO2纳米粒子和长径比、比表面积均比较大的纳米管. 用XRD, TEM, SAED和BET等手段对产物进行了表征. 为了测试产物的光催化性能, 以高浓度的硝基苯(NB)溶液为模拟水样, 进行了一系列提高降解效率的优化实验和光催化降解的对比实验. 通过对硝基苯溶液初始浓度、TiO2加入量和降解体系pH值等条件的考察, 得出硝基苯溶液的质量浓度为300 mg/L, TiO2的加入量为0.4 g/L, 体系的pH值为6~7时, 降解效果最好; 通过对比实验发现, 由于纳米管的大比表面积, 使得其光催化性能明显优于球形纳米粒子, 3 h后的降解率达到90%以上, 3.5 h左右硝基苯几乎被完全降解.