光照下自然水体生物膜产生H2O2及其对十二烷基苯磺酸钠降解的影响

通过模拟实验研究了不同活性的自然水体生物膜在光照条件下生成过氧化氢(H₂O₂)的反应. 并研究了光照对自然水体生物膜体系中十二烷基苯磺酸钠(SDBS)降解的影响, 结合无生物膜H₂O₂溶液中SDBS的降解实验, 验证了H₂O₂对SDBS降解的作用. 结果表明, 具有生物活性的生物膜可以生成H₂O₂, 而无活性和光合作用受到抑制的生物膜则不能生成H₂O₂; 光照条件下, 生物膜体系中SDBS的降解量明显高于无光照条件下的; 光照和Fe²⁺对H₂O₂降解SDBS有促进作用.     

g-C3N4/Fe3O4/BiOI磁性材料的制备及其可见光助芬顿催化性能

采用共沉淀-回流法制成g-C₃N₄/Fe₃O₄/BiOI磁性复合材料作为异相光助芬顿(Fenton)催化剂。运用扫描电镜(SEM)、透射电镜(TEM)、X-射线衍射(XRD)、振动样品磁强计(VSM)和N₂吸附-脱附等手段分别对催化剂的形貌、结构、组成、磁性和比表面积等进行了表征，并以罗丹明B(RhB)为模型污染物考察了材料的可见光催化性能。实验结果表明，当BiOI的负载质量为50%时，在可见光照射下，复合材料具有最好的光催化性能，180 min内对RhB的降解效率可达到99.20%。较高的光催化性能归因于所制备材料对RhB较强的吸附、强烈的可见光响应以及异质结构促进了光生载流子的分离。进一步在光催化体系中加入适量的H₂O₂后，可极大提高三元复合材料可见光助Fenton降解RhB的效率，30 min内即可达到98.44%,这得益于体系中发生Fenton反应产生较多具有强氧化性的羟基自由基，同时光生电子可加速Fe³⁺     

球磨微米硫化零价铁活化双氧水降解有机污染物的研究

报道了机械球磨方法制备的微米硫化零价铁（S-ZVI）可以快速活化H₂O₂降解各类有机污染物.S-ZVI/H₂O₂降解苯酚的单位比表面积反应速率常数是ZVI/H₂O₂的5倍以上,且苯酚的降解不存在初始抑制阶段.探针化合物乙醇的淬灭反应结合电子顺磁共振（EPR）实验证明S-ZVI/H₂O₂体系产生的氧化活性物质为·OH.反应前后S-ZVI颗粒的扫描电子显微镜（SEM）和X射线衍射（XRD）表征结合电化学测试和苯酚降解结果表明S-ZVI中FeS取代ZVI表面的钝化膜（铁氧化物）,加速了电子从Fe⁰传递到H₂O₂,更快地释放Fe²⁺,引发Fenton反应.在这过程中FeS主要作为电子的导体而非Fe²⁺的释放源.     

三维磁性复合材料ZnFe2O4/g-C3N4/rGO@Ag的制备及高效光催化降解罗丹明B的研究

光催化降解有机染料被认为是目前解决染料污染问题的一种理想策略。首先以三聚氰胺、氧化石墨烯(GO)和中空ZnFe₂O₄为前驱体通过热处理来构建3D结构ZnFe₂O₄/g-C₃N₄/rGO骨架;然后将银(Ag)作为助催化剂固定在ZnFe₂O₄/g-C₃N₄/rGO骨架上,制备了3D结构ZnFe₂O₄/g-C₃N₄/rGO@Ag复合光催化剂。并采用傅里叶变换红外(FT-IR)、X射线衍射(XRD)和扫描电子显微镜(SEM)等手段对材料的结构、形貌与化学组成进行了表征。结果表明,ZnFe₂O₄/g-C₃N₄/rGO@Ag复合催化剂在可见光的照射下对罗丹明B (RhB)的降解活性显著增强,在可见光照射下20...     

铕掺杂TiO2的制备及其可见光光催化性能研究

采用溶胶-凝胶法制备了不同铕(Eu)掺杂量的TiO₂纳米颗粒(Eu-TiO₂),利用透射电镜(TEM),X射线光电子能谱(XPS),X射线衍射(XRD)及紫外可见漫反射(UV-Vis DRS)等方法对Eu-TiO₂进行了物理特性的初步表征.结果表明:与未掺杂纳米TiO₂比较,Eu-TiO₂禁带宽度变窄,具有可见光光催化活性.在可见光下(λ≥420 nm)照射下,以光催化降解染料罗丹明B(Rhodamine B,RhB)为目标反应,探讨了Eu-TiO₂不同制备条件对RhB降解光催化活性的影响,优化得到制备高活性Eu-TiO₂最佳pH为3、掺杂比例(n_Eu/n_Ti)为0.05%、煅烧温度为500 ℃.研究了可见光照射下Eu-TiO₂降解RhB和无色有机小分子水杨酸(SA)光催化反应条件及降解特性,RhB的12 h深度氧化矿化率为60.2%,SA的8 h降解率达到100%.通过跟踪测定可见光下Eu-TiO₂光催化反应过程中氧化物种的变化,研究了可见光激发Eu-TiO₂光催化反应机理,表明其光催化反应主要涉及羟基自由基(·OH)历程.     

BiOBr/g-C3N4 S型异质结无H2O2光-自芬顿高效催化降解RhB

通过焙烧-超声混合法成功地制备了BiOBr/g-C₃N₄S型异质结复合光催化剂。采用多种表征手段对样品物理属性进行了表征,包括X射线多晶粉末衍射仪(XRD)、扫描电子显微镜(SEM)、X射线光电子能谱(XPS)、紫外可见漫反射光谱(UV-Vis DRS)。研究了所制备样品有/无Fe³⁺的光-自芬顿催化/光催化降解罗丹明B(RhB)性能。通过捕获实验确定了光催化反应中的主要活性物种,提出了光-自芬顿反应的降解机理。研究结果表明,BiOBr/g-C₃N₄S型异质结能原位生成H₂O₂,添加Fe³⁺后,H₂O₂被原位活化成活性物种且光生电流和载流子分离效率获得显著提高。该光-自芬顿过程能高效降解RhB,其反应速率常数为0.208 min^-1,约为无Fe³⁺光催化反应速率常数的5.3倍,在光-自芬顿循环使用过程中表现出良好的稳定性。Fe...     

磁性AgBr/Ag3PO4/ZnFe2O4复合催化剂的制备及光催化性能

水热法结合原位沉淀法成功制备新型磁性溴化银/磷酸银/铁酸锌(AgBr/Ag₃PO₄/ZnFe₂O₄)复合催化剂,并通过X射线衍射、能量色散X射线、场发射扫描电子显微镜、透射电子显微镜和紫外-可见漫反射光谱对其晶相结构、组成、形貌及吸光性能进行了表征。在可见光照射下,所制备的AgBr/Ag₃PO₄/ZnFe₂O₄复合催化剂光催化降解罗丹明B (RhB)的活性优于Ag3PO4/ZnFe₂O₄、AgBr/ZnFe₂O₄和P25 TiO₂。在酸性和碱性溶液中,AgBr/Ag₃PO₄/ZnFe₂O₄光催化剂呈现出优良光催化性能。在AgBr/Ag₃PO₄/ZnFe₂O₄体系中,光催化降解RhB的速率随着反应体系温度的升高而增大,由阿伦尼乌斯方程计算获得反应体系活化能为31.9 kJ·mol^-1。AgBr/Ag₃PO₄/ZnFe₂O₄复合材料优异的可见光催化活性归因于光生电荷的有效分离,所产生的超氧自由基和空穴是RhB降解的主要活性物种。     

过硫酸盐增强花状MnCo2O4可见光降解性能

为了充分利用光降解技术与过硫酸盐氧化技术耦合的优势，成功制备了具有3D中空结构的花状MnCo₂O₄催化剂(HF-MnCo₂O₄)。在可见光照射下，HF-MnCo₂O₄能够有效地活化过硫酸钾(PS)。将PS引入光催化体系(HF-MnCo₂O₄/PS/Vis)，可以降低光生e^-/h⁺对的复合机率，同时也增加该体系的活性物种数量。以亚甲基蓝(MB)为目标物，考察了HF-MnCo₂O₄/PS/Vis耦合体系的光催化性能。得益于MnCo₂O₄独特的分级结构及MnCo₂O₄和PS之间协同效应，HF-MnCo₂O₄/PS/Vis耦合体系对MB展现出较好的降解去除能力，可见光照射50 min对MB的去除率达到96...     

Ag和Pd及其离子对TiO2光催化分解CH3CHO的影响

当用能量大于其禁带宽度的光照射通有氧气的TiO₂悬浮液时,在TiO₂微粒表面会产生反应活性很高的空穴和O₂^-、H₂O₂等多种活性氧.在上一篇文章中^[1]我们已报道了在通氧气和紫外光照的条件下,向TiO₂悬浮液中加入少量Ag⁺或Pd²⁺,将会大幅度提高体系中H₂O₂的生成量.另外,蔡汝雄等人也曾通过向TiO₂悬浮液中加入SOD的方法来提高其中H₂O₂的生成量^[2],而且证明了H₂O₂生成量的增多有助于杀死子宫癌细胞^[3].另一方面,利用TiO₂光催化来分解处理工业废水中的有机物已多见报道^[4～7].因此,为考察H₂O₂含量的增加是否有助于TiO₂催化分解有机物,我们以CH₃CHO为氧化对象,测定了经Ag和Pd表面修饰以及直接向悬浮体系添加Ag⁺或Pd²⁺离子前后,TiO₂光催化氧化分解CH₃CHO效率的变化,并对氮气和氧气气氛的实验结果进行了测定和比较.     

异相Fenton光催化对有毒有机污染物的降解

以蒙脱石-K10(Montmorillonite K10)作为Fe3 的载体制备异相Fenton催化剂(Mot-Fe),并用此催化剂在可见光(λ>420 nm)照射下研究其降解染料罗丹明B(Rhoda-mine B,RhB)和2,4-二氯苯酚(2,4-Dichlorophenol,DCP)。研究表明,选定的Mot-Fe/H2O2体系能有效地降解RhB,反应300 min脱色完全,总有机碳(TOC)去除率达85.2%,反应过程中主要涉及到.OH自由基的产生和参与。可见光照射下,对DCP/Mot-Fe/H2O2体系,TOC的去除率达到51.6%。催化剂具有比较好的稳定性,能够重复使用。     

A novel approach for the oxidative degradation of organic pollutants in aqueous solutions mediated by iron tetrasulfophthalocyanine under visible light radiation

An efficient approach has been developed to decompose toxic organic pollutants. The photodegradation of Rhodamine B (RhB), salicylic acid, and Orange II was examined in the presence of iron tetrasulfophthalocyanine ([Fe(PcS)]) and H(2)O(2) under visible irradiation. It was found that under visible light irradiation, organic pollutants in the [Fe(PcS)]/H(2)O(2) system can be rapidly degraded, but the concentration of [Fe(PcS)] remains nearly unchanged, and this indicates that [Fe(PcS)] has a good catalytic character. EPR results and other experimental results suggest that the light-activated reaction process involves the formation and reaction of HO(.) radicals. On the basis of the experimental results, a possible reaction mechanism for the degradation of organic pollutants under visible light illumination in the aqueous [Fe(PcS)]/H(2)O(2) solutions is proposed.     

Keggin型铜取代磷钨杂多阴离子可见光催化降解罗丹明B

以Keggin型铜取代杂多阴离子PW11O39Cu(Ⅱ)(H2O)5-[PW11Cu]为可见光催化剂,有机染料罗丹明B(RhB)为模型污染物,研究了在可见光照射下PW11Cu对RhB的可见光催化降解作用,提出了PW11Cu可见光催化作用的反应机理,同时考察了RhB初始浓度、PW11Cu初始浓度和溶液pH值对RhB光催化降解速率的影响。 实验结果表明,含有15.6 μmol/L PW11Cu+10 μmol/L RhB的水溶液在可见光照射下反应80 min,RhB的降解率达100%,总有机碳去除率约33%。 RhB的可见光催化降解服从准一级动力学方程,在RhB初始浓度为20、30和40 μmol/L的情况下,其表观一级速率常数分别为3.1×10-2、2.0×10-2和1.5×10-2 min-1。     

Oxidative decomposition of rhodamine B dye in the presence of VO2+ and/or Pt(IV) under visible light irradiation: N-deethylation, chromophore cleavage, and mineralization

In order to make clear the roles of dissolved O2 in the photocatalytic decomposition of organic pollutants and to discriminate different degradation pathways (N-deethylation, chromophore cleavage, and mineralization) during the degradation of dye, the photodegradation of rhodamine B (RhB) has been investigated using vanadate and/or platinum species as electron acceptors in the presence or absence of O2 under visible light irradiation. It was found that with VO2+ as electron acceptor, RhB underwent efficient N-deethylation under visible light irradiation and O2 was found to slow down this process significantly. Little mineralization has been observed in the presence and absence of O2 in VO2+ systems. By contrast, Pt(IV) resulted in the cleavage of conjugated chromophore structure (bleaching) of RhB dye under the otherwise identical conditions. In this case, the presence of O2 did not affect the bleaching rate of the dye, but enhanced greatly the mineralization. Both cleavage of conjugated chromophore structure and N-deethylation occurred simultaneously upon the coaction of VO2+ and Pt(IV) under visible light irradiation. The mineralization yield of the combined system was evidently higher than the expected summation of separate ones. TOC, XPS, and ESR results indicate that in the VO2+ and Pt(IV) combined system VO2+ not only oxidized RhB leading to deethylation but also oxidized the reduced Pt(II) to regenerate Pt(IV) leading to the further cleavage of chromophore structure of RhB, which behaved quite different from the separate ones. A mechanism was also proposed to interpret the different pathways for the oxidative photodecomposition of RhB under visible irradiation.     

季膦-磷钨酸室温离子液体的合成及光催化降解罗丹明B

以不同摩尔比的磷钨酸与烷基取代季膦盐为原料合成了一系列磷钨酸类离子液体,并使用DSC和IR对系列离子液体进行了表征。 结果表明,[P(C14H29)(C6H13)3]-磷钨酸系列离子液体为室温离子液体,磷钨酸根保留了Keggin结构。 进一步研究了在可见光照射下,以所制备的磷钨酸季膦盐离子液体为催化剂催化降解罗丹明B染液。 以脱色率和COD来表征染料的降解效果,分别探讨了离子液体中阳离子碳链长度、催化剂用量、光照时间和罗丹明B的初始浓度等因素对光降解罗丹明B的影响。 结果表明,其中[P(C14H29)(C6H13)3]3-PW12O40离子液体的催化效果最好,在催化剂用量为0.3 g时,3 h内50 mL 8.35×10-5 mol/L罗丹明B的降解率可达到95%以上,催化剂重复使用5次后,脱色率仍可达到97%以上。     

可见光照射下SiW12O40^4-／Resin光催化剂活化H2O2降解染料的研究

将杂多酸（SiW12O40^4-）负载到阴离子交换树脂上，得到SiW12O40^4-／Resin（SWR）固相光催化剂，在可见光的照射下，可以有效地活化H2O2降解染料．以罗丹明B（RhodamineB，RhB）为模型化合物，研究了不同条件下RhB的降解动力学，以及降解过程中其UV—vis光谱及体系的总有机碳（Total Organic Carbon，TOC）变化情况，结果表明RhB的共轭芳环结构被破坏，矿化率为24．2％．其它染料如孔雀绿（Malacllite Green，MG）和吖啶橙（Acridine Orange，AO）等也可以被降解和矿化．催化剂的循环实验表明SWR固相光催化剂易于分离，并且具有良好的稳定性，可以重复利用．     

Degradation of organic pollutants by visible light synergistic electro-Fenton oxidation process

Visible light irradiation combined with homogeneous iron and/or hydrogen peroxide to degrade organic dye rhodamine B (RhB) and small molecular compound 2,4-dichlorophenol (2,4-DCP) in a home-made bottle reactor was assessed. The concen-tration of oxidize species, Fe3+ and Fe2+ were determined during the degradation process. The results demonstrated that visible light irradiation combined with electro-Fenton improved the degradation efficiency. Moreover, both RhB and 2,4-DCP were mineralized during visible light synergistic electro-Fenton oxidation process. 95.0% TOC (total organic carbon) removal rate of RhB occurred after 90 min and 96.7% of COD (chemical oxygen demand) removal rate after 65 min of irradiation. 91.3% TOC removal rate of 2,4-DCP occurred after 16 h of irradiation and 99.9% COD removal rate occurred after 12 h of illumination. The degradation and oxidation process was dominated by the hydroxyl radical ( · OH) generated in the system. Both the impressed electricity and dye sensitization by visible light facilitated the conversion between Fe3+ and Fe 2+ , thus, improving Fenton reaction efficiency.     

Efficient photocatalytic properties of a dinuclear iron complex with bis[2-hydroxybenzaldehyde]hydrazonate ligand

A novel photooxidative system for degrading toxic organic pollutants is reported. A new complex of Fe2L3(L = bis[2-hydroxybenzaldehyde]hydrazone) synthesized can efficiently activate hydrogen peroxide (H2O2) to oxidize and mineralize the target complexes rhodamine B (RhB) and methyl orange (MO) in aqueous media under ambient temperature and normal pressure and with visible light irradiation.     

铬取代杂多阴离子PW11O39Cr（Ⅲ）（H2O）4-可见光催化降解罗丹明B

为了利用太阳光能去除水体有机染料污染物,以Keggin型铬取代杂多阴离子PW11O39Cr(III)(H2O)4-(PW11Cr)为光催化剂, 详细研究在可见光照射下PW11Cr对水体有机染料污染物罗丹明B(RhB)的光催化降解作用, 考察RhB和PW11Cr初始浓度以及溶液pH对RhB可见光催化降解速率的影响, 并通过可见吸收光谱和荧光发射光谱研究水溶液中PW11Cr和RhB的相互作用, 提出PW11Cr光催化作用的机理. 实验结果表明,含有50 μTTmol·L-1 PW11Cr和10 μTTmol·L-1 RhB的水溶液在200 W可见光下照射120 min, RhB的降解率达到100%,总有机碳去除率约32%. 在PW11Cr浓度较大和pH<3.5的酸性条件下, PW11Cr与RhB之间易发生络合, 导致RhB光降解速率变慢,而PW11Cr浓度为50 μTTmol·L-1和溶液接近中性条件下, RhB的光降解速率较快.     

Photooxidative degradation of dye pollutants accumulated in self-assembled natural polyelectrolyte microshells under visible radiation

A novel route to facilitate the degradation of dye pollutants, a class of well-known recalcitrant organic pollutants, is reported. This new approach is based on a natural polyelectrolyte microshell that was preformed by the alternate adsorption of the anionic alginate sodium (ALG) and the cationic chitosan (CHI) onto weakly cross-linked melamine formaldehyde (MF) colloidal particles, and the subsequent sacrifice of MF templates in 0.1 M HCl. The as-prepared microshells could accumulate rhodamine B (RhB) and fluorescein (Flu) efficiently in water under ordinary conditions by means of a simple mixing process. The photodegradation of the accumulated RhB and Flu was examined in the presence of Fe3+ and H2O2 under visible radiation. The accumulated RhB and Flu are rapidly degraded and the assembled shells maintain their intact spherical shape throughout the photoreaction process. Results of recycling degradation experiments and the photochemical behavior of the shells, as demonstrated by confocal laser scanning microscopy (CLSM), UV-visible spectroscopy, and scanning force microscopy (SFM), further suggest that the constructed shells may be used as environmentally friendly microcontainers for the elimination of dyes in wastewater.     

新颖的PW11O39Fe(Ⅲ)(H2O)4-/H2O2类光-Fenton体系光催化降解苯胺

将Keggin型铁取代杂多阴离子PW11O39Fe(Ⅲ)(H2O)4-[PW11Fe(Ⅲ)(H2O)]构成的类光-芬顿体系用于水体生物难降解有机污染物苯胺(ArNH2)的降解。 研究了在紫外光照射和H2O2存在下,PW11Fe(Ⅲ)(H2O)对ArNH2降解的均相光催化作用。 考察了ArNH2、H2O2和PW11Fe(Ⅲ)(H2O)浓度对光催化降解反应速率的影响。 实验结果表明,0.1 mmol/L PW11Fe(Ⅲ)(H2O)+0.2 mmol/L H2O2+0.1 mmol/L ArNH2的中性溶液在300 W汞灯照射下反应60 min,ArNH2的降解率达100%,总有机碳(TOC)去除约52%。 同时讨论了PW11Fe(Ⅲ)(H2O)光催化H2O2产生羟基自由基的分子机制,并比较了酸性和中性条件下苯胺的光催化降解效果。