负载型杂多酸对罗丹明B光催化降解的研究

以ZrO2-MoO3为载体制备了负载型硅钨杂多酸催化剂.以其为光催化剂,研究其对罗丹明B染料废水光催化降解的影响.实验结果表明:酸度、催化剂用量、溶液初始浓度是影响催化降解效果的重要因素.最佳催化条件为降解溶液酸度pH=2,催化剂最佳用量为0.5g/L,溶液的初始浓度为30mg/L,催化时间为2.5h.     

分光光度法研究PbSnO3纳米粒子对甲基橙溶液的光降解性

采用共沉淀法制备出完整的立方相锡酸铅纳米粒子,并研究了其对甲基橙溶液的光催化降解性能.结果表明：PbSnO3催化剂对甲基橙溶液有良好的光催化降解效果.当催化剂用量为60mg/L,反应时间为80min时,降解率可达90％以上.     

纳米氧化铁/膨润土催化剂的制备、表征及复相光降解罗丹明B的研究

钠基膨润土与羟基铁溶液反应,经过焙烧,制得性能良好的纳米复合型催化剂,结合比表面孔隙分析(BET)、X射线衍射谱(XRD)和高分辨扫描电镜(HRTEM)对催化剂的比表面积、晶相和粒度进行表征。用光度法对该催化剂降解染料罗丹明B进行了研究,详细考察了溶液起始pH值、H₂O₂浓度、催化剂用量和起始浓度对降解的影响以及催化剂的可重复使用性,紫外-可见光谱对降解过程进行跟踪检测,并对复相光助Fenton过程与均相光助Fenton过程进行了比较。结果表明,复合型催化剂具有很高的比表面积,铁以高催化活性的α-Fe₂O₃存在于复合催化剂中;在pH 3.0,催化剂浓度为0.3 g·L-1,H₂O₂浓度为10 mmol·L-1实验条件下,100 mL 2.5×10-5 mol·L-1罗丹明B,紫外光照射4 h后,紫外-可见光谱显示罗丹明B的特征峰消失,其脱色率和COD_Cr去除率分别为97%和71%,对该催化剂进行处理后,可以重复使用,复相光降解率要远大于均相光降解率。     

钨掺杂氧化钛纳米管光催化降解结晶紫染料的性能

采用水热合成法制备了介孔TiO2纳米管,并以介孔TiO2纳米管为载体,钨酸铵为钨源,采用传统浸渍方法制备了WO3/TiO2纳米管复合材料.讨论了以WO3/TiO2纳米管为催化剂,影响结晶紫光催化降解率的主要因素,实验结果表明:光催化降解结晶紫溶液较好的符合一级反应动力学过程.以500℃焙烧的WO3/TiO2纳米管复合材料为光催化剂,当催化剂用量为500mg/L,结晶紫溶液的起始浓度20mg/L时,光照90min,结晶紫的降解率达到95％以上.另外,催化剂具有较高的稳定性,失活后的催化剂可以通过简单的培烧再生.     

TiO2柱撑蒙脱土的制备及其对品红降解的催化反应

基于TiO2光催化剂的优良光催化活性,采用酸性溶胶法合成了TiO2柱撑蒙脱土复合光催化剂,利用IR,UV-Vis,TG/DTA,XRD及SEM等手段对复合催化剂进行了表征,通过太阳光对酸性品红光催化降解实验,考察了催化剂的光催化活性。该催化剂比纳米TiO2对酸性品红的光催化降解反应表现出更高的催化活性,而且更易于沉降、回收。当TiO2柱撑蒙脱土光催化剂的用量为0.2 g.(100 mL)-1,酸性品红溶液的pH值为3时,在太阳光下40 min内酸性品红基本降解完全,而且该降解过程符合Langmuir-Hin-shelwood方程。X射线衍射(XRD)分析表明钛柱撑蒙脱土的层间距较钠基蒙脱土有明显的增大,紫外-可见吸收光谱表明TiO2柱撑蒙脱土比纳米TiO2具有更高的光吸收效率。     

非均相类Fenton反应催化氧化脱色降解直接桃红12B

研究了以Fe-Ni-Mn/Al2O3为催化剂(FA催化剂),用微波促进非均相类Fenton反应催化氧化脱色降解有机染料直接桃红12B及相关机理。内容包括直接桃红12B溶液的浓度-吸光度工作曲线,初始pH值、H2O2用量、FA催化剂用量对脱色降解直接桃红12B的影响,微波单独脱色处理直接桃红12B、微波+FA催化剂脱色处理直接桃红12B、微波+H2O2脱色处理直接桃红12B、微波-FA催化剂-H2O2体系脱色处理直接桃红12B、阳光-FA催化剂-H2O2体系脱色处理直接桃红12B等对照试验研究。在优化条件下,比较了采用光助非均相类Fenton与微波促进非均相类Fenton反应的脱色效率,并探讨了微波促进非均相类Fen-ton反应的机理。研究表明微波可以明显加快非均相类Fenton法催化氧化脱色降解直接桃红12B溶液的过程。论文所用表征方法均为紫外-可见光谱法。     

Pr掺杂TiO2光催化剂的制备及其对酸性品红降解反应的催化性能

以钛酸四丁酯为前躯物,采用溶胶-凝胶法制备了掺杂不同含量Pr的TiO2光催化剂,利用XRD,TG-DTA,AFM,UV-Vis,FTIR等手段对催化剂进行了表征。并通过酸性品红光催化降解实验对其光催化性能进行了评价,考查了实验条件,如催化剂用量,烧结温度,掺杂量等对催化剂催化活性的影响。Pr2O3的掺杂阻碍了TiO2晶相由锐钛矿型向金红石型的转变,使TiO2的粒径减小,比表面积增大,催化活性增强。当Pr掺杂量为0.8%,催化剂用量为0.03g,烧结温度为500℃时,酸性品红的降解率达到97%以上,酸性品红的降解反应为准一级反应。     

超声波和紫外光协同降解酸性橙Ⅱ水溶液的机理研究

以含有多个苯环的典型偶氮染料-酸性橙Ⅱ为研究对象,研究了超声波和紫外光分别辐照及共同辐照下的降解现象。酸性橙Ⅱ水溶液在超声波及紫外光分别辐照下均发生显著降解,反应过程符合准一级反应动力学规律。在超声波和紫外光共同辐照下,反应过程也符合准一级反应动力学规律,同时酸性橙Ⅱ水溶液降解呈现显著的声光协同效应,即同一辐照时间内超声波和紫外光共同辐照下酸性橙Ⅱ的降解率大于超声波和紫外光单独辐照下各自降解率之和。动力学分析结果表明,该协同效应可归因于紫外光对超声空化过程中产生的过氧化氢的裂解作用。      

紫外光下锐钛矿型二氧化钛对甲基红的催化降解

研究了在紫外光(λ=365nm)照射下,以自制的掺铁锐钛矿型二氧化钛对甲基红的催化降解效果,分析了甲基红初始浓度、二氧化钛的用量、掺铁量、光照时间和溶液初始pH值等因素的影响.结果表明:在15mg/L的甲基红溶液(pH=5)中,加入0.7 g/L自制二氧化钛(掺铁量1％、摩尔分数),室温下紫外光照反应30min,甲基红的降解率达到99.21％.     

掺Fe(Ⅲ)的A-TiO_2的水热法制备、表征及其光催化活性分析

一定条件下用水热法制备了的掺Fe(Ⅲ)的TiO2晶体,XRD分析结果表明它是锐钛矿型Fe(Ⅲ)的TiO2(A-TiO2).研究了以自制的掺Fe(Ⅲ)的A-TiO2为光催化剂对罗丹明B溶液的降解性能.结果表明,在5 mg/L的罗丹明B溶液中,加入0.1650 g自制的掺Fe(Ⅲ)的5%的A-TiO2,用硝酸调节溶液PH=5后,可见光照射下,43℃恒温磁力快速搅拌反应6 h,罗丹明B降解率为76.5%;同样条件下经254nm紫外光照6 h,降解率达到95.7%.     

Investigation on the sonocatalytic degradation of acid red B in the presence of nanometer TiO2 catalysts and comparison of catalytic activities of anatase and rutile TiO2 powders

Here, the nanometer anatase and rutile titanium dioxide (TiO(2)) powders were introduced to act as the sonocatalysts during the ultrasonic degradation of azo dye-acid red B which was chosen as model compound. The ultrasound of low power was used as an irradiation source to induce TiO(2) particles performing catalytic activity. It was found that the processes of sonocatalytic degradation were different between nanometer anatase TiO(2) and nanometer rutile TiO(2). For nanometer anatase TiO(2) catalyst, the acid red B was mainly oxidated by the holes on the surface of nanometer anatase TiO(2) particles, so that the decolorization and degradation happened at the same time. For the nanometer rutile TiO(2) catalyst, the acid red B was mainly oxidated by the *OH radicals from the ultrasonic cavitation, so that the decolorization of azo bond takes place primarily, and then the degradation of naphthyl ring does. The intermediates of acid red B in the presence of nanometer anatase and rutile TiO(2) powders have been monitored by UV-vis spectra and high performance liquid chromatography (HPLC), respectively. All experiments indicated that the degradation effect of acid red B in the presence of nanometer anatase TiO(2) powder was obviously better than that in the presence of nanometer rutile TiO(2) powder. Hence, the method of sonocatalytic degradation for organic pollutants in the presence of nanometer anatase TiO(2) powder is expected to be promising as an advisable choice for the treatment of organic wastewaters in future.     

Sonocatalytic degradation of some dyestuffs and comparison of catalytic activities of nano-sized TiO2, nano-sized ZnO and composite TiO2/ZnO powders under ultrasonic irradiation

Here, a novel sonocatalyst, composite TiO2/ZnO powder, was prepared through the combination of nano-sized TiO2 and ZnO powders. Because of the appropriate adsorbability to organic pollutants and special crystal interphase between TiO2 and ZnO particles, the composite TiO2/ZnO powder exhibits a high sonocatalytic activity under ultrasonic irradiation during the degradation of acid red B. Especially, the sonocatalytic activity of composite TiO2/ZnO powder with 4:1 molar proportion treated at 500 degrees C for 50 min showed obvious improvement compared with pure nano-sized TiO2 and ZnO powders. When the experimental conditions such as 10mg/L acid red B concentration, 1.0 g/L catalyst addition amount, pH=7.0, 20 degrees C system temperature, 100 min ultrasonic time and 50 mL total volume were adopted, the satisfactory degradation ratio and rate were obtained. All experiments indicate that the sonocatalytic method using composite TiO2/ZnO powder may be a more advisable choice for the treatments of non- or low-transparent organic wastewaters in future.     

Sonocatalytic degradation of acid red B and rhodamine B catalyzed by nano-sized ZnO powder under ultrasonic irradiation

Nano-sized ZnO powder was introduced to act as the sonocatalyst after the treatment of high-temperature activation, and the ultrasound of low power was used as an irradiation source to induce nano-sized ZnO powder performing sonocatalytic degradation of acid red B and rhodamine B. At the same time, the effects of operational parameters such as solution pH value, initial concentration of dyestuff and addition amount of nano-sized ZnO powder have been examined in this paper. We found that the degradation ratios of acid red B and rhodamine B in the presence of nano-sized ZnO powder were much higher than that with only ultrasonic irradiation. However, the degradation ratio of acid red B was about two times higher than that of rhodamine B for the initial concentration of 10.0 mg/L, addition amount of 1.0 g/L nano-sized ZnO powder, solution acidity of pH 7.0 and 60 min irradiation experimental condition. The difference of the degradation ratios can be illustrated by the difference of chemical forms of acid red B and rhodamine B in aqueous solution and the surface properties of nano-sized ZnO particles. In addition, the researches on the kinetics of sonocatalytic reactions of acid red B and rhodamine B have also been performed and found to the follow pseudo first-order kinetics. All the experiments indicated that the sonocatalytic method in the presence of nano-sized ZnO powder was an advisable choice for the treatments of non- or low-transparent organic wastewaters in future.     

Low frequency sonocatalytic degradation of Azo dye in water using Fe-doped zeolite Y catalyst

Sonocatalytic degradation of acid red B (ARB) dye was investigated using Fe doped zeolite Y catalysts with the assistance of low frequency (20 kHz) ultrasonic irradiation. Low concentration of Fe ions from different precursors was loaded onto the zeolite using wet impregnation method. Catalytic degradation of ARB dye was found to be accelerated by the reaction between Fe (II) and Fe (III) ions and hydrogen peroxide (H₂O₂) generated in situ by the ultrasound-mediated dissociation of water molecules. Fe (II)/Y exhibited higher degradation efficiency at the beginning of the reaction but achieved almost similar degradation at the end of the process. The increase of pH significantly decreased the degradation efficiency of ARB dye and strongly affected the leaching and catalyst stability. The highest efficiency was achieved at an initial pH of 3 with nearly 100% degradation in less than 60 min. Both catalysts showed no significant changes in terms of their mean particle sizes before and after reaction. Finally, Fe (III)/Y showed better performance evaluated based on leaching of Fe and also catalyst reusability. Only minor physical changes occurred during the degradation process for four consecutive runs of reaction.     

无模版剂水热法合成α-FeOOH及其光催化性能

以硝酸铁为原料,通过改变部分原料（NaOH,CH3COONa,H2O2）在无模版剂条件下水热法成功合成出纯相的短棒状、长棒状、颗粒状等形貌的α-FeOOH纳米晶体,并考察了其可见光光催化活性.结果表明：所获的α-FeOOH纳米晶体可用作Fenton催化剂,短棒状α-FeOOH在添加少量的NaF和H2O2条件下,光催化性能显著提高,罗丹明B降解率可由6.8％增加到93.6％.     

三维金属有机骨架/石墨烯水凝胶均相降解纤维素为小分子酸的研究

通过在三维还原氧化石墨烯孔径中原位生长ZIF-8纳米粒子,制备了三维金属有机骨架/石墨烯催化剂.这种ZIF-8/rGO纳米复合材料同时具有介孔和微孔,并且拥有高比表面积和大量催化位点,是生物质转化的理想催化剂.将纤维素溶解于氢氧化钠水溶液中,在水热条件下,使用这种催化剂,纤维素可以被充分降解转化.纤维素转化率可以达到100%,其主要产物是甲酸,产率最高可达93.66%.催化剂还可以被回收,重复使用依然具有很好的催化效果.     

合成Pb(OH)2/rGO催化剂用于催化转化糖为乳酸

Pb²⁺离子可以作为高效的催化剂用于降解糖为乳酸, 但是为了降低暴露Pb²⁺离子于环境中的风险,最好的办法是把铅固定在一个固体催化剂上．报道了一个简单的制备Pb(PbO₂)/石墨烯复合固体催化剂的方法,可以得到石墨烯负载的纳米铅催化剂,铅颗粒的尺寸在2～5 nm．获得的催化剂可以在水中用于降解葡萄糖、果糖甚至纤维素,产物主要为乳酸．对于果糖、乳酸的产率为58.7% (433 K,2.5 MPa N₂);当直接使用纤维素为原料,无额外酸、碱催化剂时,乳酸的产率可以达到31.7%.     

铕掺杂纳米二氧化钛透明光触媒乳液的制备及光催化性能研究

本文采用常温络合—控制水解法,以TiCl_4,有机羧酸,氨水,硝酸铕,D-山梨醇等为主要实验药品,制备了Eu掺杂纳米TiO_2光触媒乳液。以酸性红3R染料为待降解物,分别考察了不同条件下制备的TiO_2光触媒乳液在太阳光模拟器生成光照射下的光催化性能。此外,还考察了Eu掺杂纳米二氧化钛透明光触媒乳液对于不同浓度染料的光催化性能。通过酸性红3R染料的降解实验,研究了影响Eu掺杂纳米二氧化钛透明光触媒乳液光催化活性的因素。通过X射线衍射仪(XRD)、纳米激光粒度分析仪、紫外可见分光光度计(UV-Vis)等对样品进行表征。结果表明:样品的平均粒度为4.1 nm左右,晶型为锐钛矿,样品的吸收光谱可拓宽至可见光区。当Eu掺杂量为0.3%,pH值为6,回流时间是15 min时,制备的Eu掺杂纳米二氧化钛光触媒乳液的光催化性能最佳。该光触媒乳液经太阳光照射1 h之后,对浓度为25 mg/L的酸性红3R模型反应物的降解效率最高,达到97%以上。     

CdS/膨润土复合材料的制备及其光催化性能

以CdCl₂和硫代乙酰胺为反应物,通过湿化学法合成CdS/膨润土复合材料,采用X射线衍射(XRD)、红外光谱(FTIR)以及紫外可见光谱(UV-Vis)等分析技术对其结构及光学性能进行表征。以罗丹明B和亚甲基蓝为目标污染物,考察了CdS/膨润土复合材料对有机染料的降解性能。结果表明:在罗丹明B和亚甲基蓝的初始浓度为20 mg/L 时,光照3 h后,CdS/膨润土对它们的降解率分别为80.6%和88.3%,优于CdS及膨润土原土催化剂。