TiO_2-CuPcTs敏化薄膜光电流及可见光光催化性能

以四磺酸酞菁铜(CuPcTs)为敏化剂,玻璃和图案化的氧化铟锡(ITO)分别作为基底,制备了敏化薄膜TiO2-CuPcTs和ITO/TiO2-CuPcTs/ITO敏化器件.以罗丹明B(RhB)的可见光光催化降解为模型反应评价敏化薄膜的光催化性能.敏化薄膜采用UV-vis和Raman技术进行表征,同时利用敏化器件的结构特性,测定其在氮气和纯水体系下的光电流.研究结果表明,TiO2-CuPcTs可以有效地将光谱响应拓宽到可见光区,一级反应速率常数为空白TiO2薄膜的3.7倍.TiO2-CuPcTs薄膜光催化降解RhB的重复性能稳定.与ITO/TiO2/ITO器件相比,敏化器件ITO/TiO2-CuPcTs/ITO具有较高的光电流信号,验证了激发态的CuPcTs能够将电子转移到TiO导带上的敏化机理.     

酞菁敏化混晶TiO2薄膜的低温制备及其对罗丹明B的催化降解

以四磺酸酞菁铜(CuPcTs)为敏化剂,采用溶胶-凝胶法制备了酞菁敏化的TiO2溶胶,经浸渍提拉成膜并室温晾干,制得CuPcTs-TiO2薄膜.采用XRD,UV-Vis和SEM等测试手段对薄膜样品进行了表征,并通过罗丹明B的降解考察了薄膜的可见光催化性能.结果表明,TiO2为锐钛矿-板钛矿-金红石混晶结构,CuPcTs-TiO2薄膜对罗丹明B降解具有较高的光催化活性.CuPcTs敏化能有效提高TiO2的可见光催化活性,但过多的CuPcTs会使催化活性降低.在可见光照射条件下,罗丹明B主要是先脱乙基生成罗丹明,然后再逐步被分解.CuPcTs-TiO2薄膜在经2～3次循环使用后,其光催化活性趋于稳定.CuPcTs可牢固地负载于TiO2薄膜中,从而保证了CuPcTs-TiO2薄膜重复使用的稳定性.     

高比表面积CuPc/TiO2纳米管复合材料的制备及其可见光光催化活性

以P25为前驱体,在碱性条件下采用水热法制备了TiO2纳米管(NT),然后通过浸渍法将敏化剂酞菁铜(CuPc)附着于TiO2NT表面,制得可见光响应的CuPc/TiO2NT复合光催化材料,并对其进行了表征,考察了它在可见光下降解罗丹明B的光催化活性.结果表明,在NaOH碱性条件下水热法制备的TiO2NT具有较大的比表面...     

Ag3PO4光催化耦合微生物燃料电池去除罗丹明B

以硝酸银、磷酸钠为原料,一步沉淀法制备了Ag_3PO_4可见光光催化剂,用硅溶胶将其负载于不锈钢丝网上,经干燥得到光催化电极。以此光催化电极和碳棒分别作为阴极、阳极,在阳极室加入负载生物产电菌的活性炭颗粒,建立光催化耦合微生物燃料电池反应器。以罗丹明B(RhB)为模型污染物,考察了光照、底物浓度、pH值等对污染物去除效率与电池产电性能的影响。结果显示:在100 W卤素灯光照下、外接500Ω电阻、pH=10、微生物量1.5倍,反应4 h可去除92%的(50 mg·L-1、200 m L)RhB;此时电池输出电压和功率密度分别为124 m V、34.9 mW·m-2。5次重复实验表明该负载型光催化电极具有很好的稳定性。     

Ag3PO4光催化耦合微生物燃料电池去除罗丹明B

以硝酸银、磷酸钠为原料,一步沉淀法制备了Ag₃PO₄可见光光催化剂,用硅溶胶将其负载于不锈钢丝网上,经干燥得到光催化电极。以此光催化电极和碳棒分别作为阴极、阳极,在阳极室加入负载生物产电菌的活性炭颗粒,建立光催化耦合微生物燃料电池反应器。以罗丹明B(RhB)为模型污染物,考察了光照、底物浓度、pH值等对污染物去除效率与电池产电性能的影响。结果显示:在100 W卤素灯光照下、外接500Ω电阻、pH=10、微生物量1.5倍,反应4 h可去除92%的(50 mg·L^-1、200 mL)RhB;此时电池输出电压和功率密度分别为124 mV、34.9 mW·m^-2。5次重复实验表明该负载型光催化电极具有很好的稳定性。     

无定形TiO2可见光敏化降解染料污染物

采用一步水解法制备了无定形TiO2(Am-TiO2),并运用X射线衍射、X射线光电子能谱、N2吸附-脱附和紫外-可见漫反射光谱等手段对其进行了表征.结果表明,Am-TiO2具有大的比表面积(216m2/g)和丰富的表面羟基/化学吸附的水.与晶态TiO2相比,Am-TiO2的吸收带边明显蓝移(411nm→378nm),禁...     

CuTSPc／SnO2纳米介孔复合材料的合成及其可见光光催化活性

采用无模板水热法,以四磺基酞菁铜(CuTSPc)敏化SnO2制备了CuTSPc/SnO2纳米介孔复合材料,通过X射线衍射、透射电镜、氮气吸附-脱附、紫外-可见光谱和傅里叶变换红外光谱等对复合材料进行了表征,并以罗丹明B (RhB)为目标降解物考察了其低功率(15 W光源)可见光光催化活性及循环使用性. 结果表明, CuTSPc周环的磺基与SnO2表面的锡离子形成双齿螯合, 0.1 mol% (CuTSPc与SnO2物质的量比) CuTSPc/SnO2复合材料的比表面积和平均孔径分别为236 m2/g和2.6 nm, 反应180 min时可见光降解率高达87%, 循环使用率较高(87%±5%).     

超声MnO2联用降解丁基罗丹明B染料

采用超声MnO2体系降解丁基罗丹明B染料,考察了pH值、声强、MnO2投加量等因素对染料降解过程的影响。实验结果表明,溶液pH=3.0,MnO2投加量为1.5g/L,声强=40.7W/cm2,超声辐照10mg/L的罗丹明B溶液48m in,染料的脱色率为98.73%;超声和MnO2的协同效应在酸性条件下较为明显,溶液中产生大量.OH强化了对染料的声化学脱色和降解过程;丁基罗丹明B的超声降解过程以自由基的氧化反应为主,服从动力学一级反应。     

苝染料敏化Pt/TiO2光催化分解水制氢

The photocatalyst (DPPBI/Pt/TiO2)was prepared using N,N’-di(4-pyridyl)-3,4,9,10-perylene tetracarboxylic acid bisimide (DPPBI) sensitized Pt/TiO2 and characterized by infrared spectroscopy(IR), UV-Vis diffuse reflectance spectroscopy (UV-Vis DRS), scanning electron microscopy(SEM), X-ray photoelectron spectroscopy(XPS), and X-ray diffraction (XRD). The results of characterizationshowedthat the crystal form of TiO2was anatase, Ptwas highly dispersed on the surface of TiO2 and DPPBI was adsorbed on the surface of Pt/TiO2 in DPPBI/Pt/TiO2. Hydrogen production from water splitting using photocatalyst (DPPBI/Pt/TiO2) was studied. It has been found that the rate of hydrogen evolution reaches 6.69 滋 mol·h-1·g-1 under visible light irradiation for 8 h with 300 W Xe-lamp cold light source when 250 mL reactive liquid contains 0.8 g·L-1 photocatalyst (0.1%DPPBI/0.4%Pt/TiO2) and 0.2 mol·L-1 KI.     

染料共敏化MoS2光催化产氢性能研究

染料敏化是提升二硫化钼(MoS₂)光催化制氢性能的一种有效手段。相较于单一敏化剂,共敏化可进一步拓展光吸收范围,提高催化剂的光催化效率,但目前尚无共敏化下MoS₂光催化制氢的报道。本文在利用液相法制得MoS₂的基础上,以藻红B钠盐(EB)和罗丹明B(RhB)为共敏化剂,测定了二者共敏化下MoS₂的光催化制氢性能,重点研究了EB和RhB的加入比例和加入顺序对产氢性能的影响。结果发现当少量RhB与EB共存时,产氢性能得到一定程度的提升;EB、RhB分步加入时的性能优于一同加入且RhB先加入时的性能最佳。此外,结合紫外-可见吸收光谱、荧光光谱结果和两种染料分子的结构对染料共敏化提升MoS₂光催化产氢性能的原因进行了初步分析。     

Photocatalytic degradation of rhodamine B by dye-sensitized TiO_2 under visible-light irradiation

Perylene tetracarboxylic diimide (PTCDI),widely used in organic photovoltaic devices,is an n-type semiconductor with strong absorption in the visible-light spectrum.There has been almost no study of the PTCDI-sensitized TiO2 composite used to photocatalytically degrade pollutants.In this study,PTCDIand copper phthalocyanine tetrasulfonic acid (CuPcTs)-sensitized TiO2 composites were prepared using a hydrothermal method.The morphologies and structures of the two composites were characterized by X-ray diffrac...     

光诱导聚合制备聚噻吩/二氧化钛复合粒子的结构及光催化性能

通过光诱导噻吩在TiO2的氯仿悬浮液中聚合反应,制备了聚噻吩/二氧化钛(PTh/TiO2)复合粒子,并采用比表面积分析仪、扫描电子显微镜、粒径分析仪、X射线光电子能谱、紫外-可见漫反射光谱和红外光谱对复合粒子进行了表征.结果表明,PTh/TiO2复合粒子上的聚噻吩骨架中S原子与TiO2粒子间存在强相互作用,该复合粒子对...     

Mercury oxide as an efficient photocatalyst for degradation of rhodamine B dye under visible-light irradiation

In this work, a new visible-light-responsive photocatalyst, mercury oxide (HgO) was successfully developed. Its activity is significantly higher than that of the highly efficient photocatalyst, Ag₃PO₄ in degradation of rhodamine B (RhB) dye under irradiation of visible light. The HgO photocatalyst can be reused for at least three cycles without obvious loss of its activity in the degradation experiments. It was found that the RhB degradation rate is significantly influenced by the dye solution pH. The ultrahigh photocatalytic activity of HgO is attributed to its strong oxidization-ablility of the photogenerated holes, and high separation-possibility of the photogenerated carriers.     

Visible light induced photocatalytic reaction of rhodamine B dye via 12-tungstosilicic acid in water

Using 12-tungstosilicic acid (SiW124-) as the catalyst, rhodamine B (RhB) dye in an aerated aqueous solution can undergo an effective photocatalytic stepwise N-deethylation process under visible light irradiation, and dioxygen is reduced to hydrogen peroxide by the reducedSiW12 4-. This provides the potential for moving polyoxometalate-based photocatalytic processes from the near-UV into the visible region of the spectrum.     

A new Cu~(2+)-induced color reaction of a rhodamine derivative N-(3-carboxy)acryloyl rhodamine B hydrazide

A new rhodamine derivative,N-(3-carboxy)acryloyl rhodamine B hydrazide(CARB),has been synthesized,and its unusual spectroscopic reaction with Cu2+ has been investigated.The derivative exhibits a rapid and reversible non-fluorescent absorption upon coordination to Cu2+,which is a rather unusual phenomenon for rhodamine B derivatives.Stoichiometric measurements using the Job's method and the molar ratio method reveal that one CARB molecule combines two Cu2+ ions,and the two Cu2+ ions play different roles:one ...     

Fe(III)参与TiO_2光催化降解X3B的反应机理研究

三价铁离子对TiO2 光催化降解X3B活性艳红染料具有明显的促进作用 .但是 ,当Fe(III)全部转化为Fe(II)离子以后 ,X3B的降解不再加快 .研究表明 ,Fe(III)捕获表面光生电子是导致X3B降解速率增加的主要原因 ,而Fe(III)光解产生羟基自由基使降解X3B的贡献则相对较小 .由于体系缺乏Fe(III) /Fe(II)循环 ,(Photo) Fenton反应参与X3B降解过程的可能性极小 .X3B和Fe(III)竞争吸附催化剂表面 ,促进了光生电子 -空穴对的分离和转移 .Fe(II)吸附相当微弱 ,这可能是导致Fe(II)难以被表面空穴或其它活性物质重新氧化的原因之一     

Synthesis and characterisation of mesoporous hybrid silica-polyoxometalate aerogels for photocatalytic degradation of rhodamine B and methylene blue

ABSTRACT

Mesoporous silica aerogel/polyoxometalate hybrids were successfully synthesised under mild conditions, and were investigated towards photocatalytic degradation of Rhodamine B and Methylene Blue dye models in aqueous media under ultraviolet irradiation. The materials were characterised, in the solid state, by various tools such as FTIR, TGA, and powder XRD, in order to gather information about their chemical and structural properties. Moreover, UV-Vis, AAS, BET, SEM, and EDX techniques were used to confirm the polyoxometalates’ loading and their distribution onto the silica aerogels’ surface. The most important analytical technique was the Nitrogen adsorption-desorption, which revealed a significant increase in the specific surface area and pore volume of the hybrid catalysts after immobilisation. The synthesised hybrid catalysts, TEOS/PW₁₂ and TEOS/SiW₁₂, have shown efficient photocatalytic activity towards Methylene Blue and Rhodamine B degradation within 120 min under ultraviolet illumination, thus reaching a degradation percentage of 81–98% and 55–90%, respectively. UV-Vis analysis was employed to scrutinise the formation of intermediate species and revealed that the photocatalytic degradation process proceeded to completion within a surprisingly short time of ~5 min.