Ti(IV)与铜离子共掺杂的羟基磷灰石薄膜弱紫外光杀菌研究

采用共沉淀水热合成和离子交换的方法,制备了钛与铜离子共掺杂的羟基磷灰石(Ca10(PO4)6(OH)2:HAP)(HAPTiCu),以大肠杆菌为目标物,研究了不同材料负载的多孔镍网薄膜在弱紫外光下的杀菌活性.结果表明,HAPTiCu在弱紫外光下具有高效杀菌效率,并远远高于HAPTi和P25 TiO2薄膜.这主要是铜离子的抗菌与光催化分解细菌的协同作用的结果.电子自旋共振(ESR)研究表明杀菌反应的主要活性物种是O2-.HAPTiCu薄膜释放的铜离子在光催化杀菌反应过程中,被光催化还原沉积在表面,导致了较低的铜离子溶出,从而保证了材料的稳定性.     

二氧化铅电极的制备、表征及其电催化性能研究

以电沉积法制备了Ti/PbO2和Ti/MnO2/PbO22种电极.采用SEM、XRD和XPS等分析方法表征了电极的形貌、元素组成及元素化学态,并以罗丹明B为目标有机物,考察了所制备电极的析氧极化曲线和电催化活性以及Ti/MnO2/PbO2电极的循环伏安曲线.研究结果表明,Ti/MnO2/PbO2电极的稳定性、使用寿命、析氧电位和电催化活性较Ti/PbO2电极都有所提高,并且罗丹明B在Ti/MnO2/PbO2电极上的反应主要发生在析氧反应区,且反应不可逆.     

Ti/BDD/PbO_2复合电极在化学需氧量测定中的应用

以钛基掺硼金刚石为基体,采用电沉积的方法制备了Ti/BDD/PbO2复合电极,并将其用于化学需氧量（COD）的测定。采用扫描电子显微镜（SEM）和X射线衍射谱图（XRD）表征了电极的微观形貌及结构,采用电化学工作站考察了电极对有机物响应特性。实验结果表明,在1.45 V的低电位条件下,线性范围为0.5～175 mg/L,检测限为0.3 mg/L（S/N=3）。采用Ti/BDD/PbO2复合电极测定法和重铬酸钾标准方法对市政污水、食品废水及印染废水的对比结果表明,2种方法的相对误差小于10%,具有良好的一致性。     

RuO_2-IrO_2/Ti阳极电催化降解偶氮染料甲基橙模拟废水

以自制Ti基Ru O2-Ir O2镀层形稳电极为阳极,采用电催化氧化处理偶氮染料甲基橙模拟废水。以硫酸钠为支持电解质,在自然p H条件下分别考察了电解时间、电极间距、电流密度和电解质浓度等因素对甲基橙去除率的影响,并分析其原因。实验结果表明,在自然p H、电极间距为1.0 cm、电流密度为30.0 m A/cm2、电解质硫酸钠浓度为20.0 g/L、电解1.0h,甲基橙去除率高达90.0%以上。因此,电催化氧化法作为一种高效、简便的染料废水处理技术,具有一定的应用潜力。     

正交法设计Fe、N共掺杂TiO2/Ti液膜可见光光催化处理染料废水

采用溶胶-凝胶法制备了Fe、N共掺杂TiO_2膜电极(Fe,N-TiO_2/Ti),并设计三因素五水平正交试验对电极制备条件进行优化.结果表明,各因素影响主次顺序为:煅烧温度Fe掺杂量N掺杂量;最优制备条件为:煅烧温度550℃,Fe掺杂量0.3%(质量分数),N掺杂量0.3%(质量分数);共掺杂电极光催化活性优于单掺杂和未掺杂电极.紫外-可见漫反射和光电性能测试表明,催化剂有可见光响应;XRD表征结果表明,Fe、N共掺杂细化了晶粒,有效抑制了金红石相的形成,其晶型为锐钛矿型,粒径为11.48 nm.利用Fe,N-TiO_2/Ti与Cu阴极组装成斜置双极液膜反应器,可见光激发光催化降解苋菜红,考察了主要影响因素.结果发现,最佳条件为:初始pH 2.50,废水流量5.1 L·h~(-1),在此条件下处理20mg·L~(-1)苋菜红80 min,脱色率达到91.6%.电极重复使用10次,每次60 min,脱色率下降了12.99%,说明电极稳定性较好.     

Exceptional responders in conservation

Conservation operates within complex systems with incomplete knowledge of the system and the interventions utilized. This frequently results in the inability to find generally applicable methods to alleviate threats to Earth's vanishing wildlife. One approach used in medicine and the social sciences has been to develop a deeper understanding of positive outliers. Where such outliers share similar characteristics, they may be considered exceptional responders. We devised a 4‐step framework for identifying exceptional responders in conservation: identification of the study system, identification of the response structure, identification of the threshold for exceptionalism, and identification of commonalities among outliers. Evaluation of exceptional responders provides additional information that is often ignored in randomized controlled trials and before–after control‐intervention experiments. Interrogating the contextual factors that contribute to an exceptional outcome allow exceptional responders to become valuable pieces of information leading to unexpected discoveries and novel hypotheses.     

Ti/SnO2-Sb2O5/PbO2电极的制备及降解不同污染物性能研究

采用溶胶凝胶法和电沉积法分别制备了Ti/SnO2-Sb2O5/PbO2电极的中间层和表面活性层,并通过XRD和SEM对电极的中间层和表面活性层进行了相关表征.结果表明,制得的电极表面为β型PbO2,表面形貌均匀致密.同时,采用线性伏安扫描和交流阻抗测试对电极的电化学性能进行了测试.结果表明,电解液中污染物的存在可提高电极的析氧电位,中间层的制备可以有效提高电极的催化性能.另外,通过测定电极对苯酚、靛蓝胭脂红、甲基橙3种不同类型污染物的去除率、COD去除率,研究了该电极对不同类型有机物的降解规律.结果表明,在相同条件下该电极对靛蓝胭脂红的去除速率较高且所需电压最低,降解1 h时靛蓝胭脂红去除率即达100%,甲基橙降解3 h时其COD去除率高达55%.     

Biodegradation of benzo[a]pyrene in soil by Mucor sp. SF06 and Bacillus sp. SB02 co-immobilized on vermiculite

Two indigenous microorganisms, Bacillus sp. SB02 and Mucor sp. SF06, capable of degrading polycyclic aromatic hydrocarbons （PAHs） were co-immobilized on vermiculite by physical adsorption and used to degrade benzo[a] pyrene （BaP）. The characteristics of BaP degradation by both free and co-immobilized microorganism were then investigated and compared. The removal rate using the immobilized bacterial-fungal mixed consortium was higher than that of the freely mobile mixed consortium. 95.3% of BaP was degraded using the co-immobilized system within 42 d, which was remarkably higher than the removal rate of that by the free strains. The optimal amount of inoculated co-immobilized system for BaP degradation was 2%. The immobilized bacterial-fungal mixed consortium also showed better water stability than the free strains. Kinetics of BaP biodegradation by co-immobilized SF06 and SB02 were also studied. The results demonstrated that BaP degradation could be well described by a zero-order reaction rate equation when the initial BaP concentration was in the range of 10--200 mg/kg. The scanning electronic microscope （SEM） analysis showed that the co-immobilized microstructure was suitable for the growth of SF06 and SB02. The mass transmission process of co-immobilized system in soil is discussed. The results demonstrate the potential for employing the bacterial-fungal mixed consortium, co-immobilized on vermiculite, for in situ bioremediation of BaP.     

Effect of Sb dopant amount on the structure and electrocatalytic capability of Ti/Sb-SnO2 electrodes in the oxidation of 4-chlorophenol

Ti/Sb-SnO_2 anodes were prepared by thermal decomposition to examine the influence',of the amount of Sb dopant on the structure and electrocatalytic capability of the electrodes in the oxidation of 4-chlorophenol.The physicochemical properties of the Sb-SnO_2 coating were markedly influenced by different amounts of Sb dopant.The electrodes,which contained 5% Sb dopant in the coating, presented a much more homogenous surface and much smaller mud-cracks,compared with Ti/Sb-SnO_2 electrodes containing 10% or 15% Sb dopant,which exibited larger mud cracks and pores on the surface.However,the main microstructure remained unchanged with the addition of the Sb dopant.No new crystal phase was observed by X-ray diffraction(XRD).The electrochemical oxidation of 4-chlorophenol on the Ti/SnO_2 electrode with 5% Sb dopant was inclined to electrochemical combustion;while for those containing more Sb dopant,intermediate species were accumulated.The electrodes with 5% Sb dopant showed the highest efficiency in the bulk electrolysis of 4-chlorophenol at a current density of 20 mA/cm~2 for 180 min;and the removal rates of 4-chlorophenol and COD were 51.0% and 48.9%,respectively.     

电催化氧化法处理生活污水研究

研究制作了3种金属氧化物修饰电极:Ti/SnO2-Sb2O3、Ti/RuO2-IrO2、Ti/SnO2-Sb2O3-MnO2/PbO2,用这3种电极电解葡萄糖溶液,筛选出了处理效果最好的电极——Ti/SnO2-Sb2O3-MnO2/PbO2电极。通过Ti/SnO2-Sb2O3-MnO2/PbO2电极电解葡萄糖溶液实验,研究了电解时间、电流密度、电解质浓度等因素对电解效果的影响。