Mn_3O_4/金属有机骨架材料活化过一硫酸盐降解水中难降解有机污染物罗丹明B（英文）

锰氧化物是一类环境友好型材料,可以有效活化过一硫酸盐(PMS)降解水中难降解有机污染物.但是锰氧化物在单独使用时容易出现严重的团聚现象,进而降低其对PMS的催化活性,不利于水中污染物的降解.因此,人们通常将锰氧化物负载于多孔的载体材料上.金属有机骨架材料(MOFs)因具有巨大的比表面积和温和的制备条件而广受关注.本文采用温和的溶剂热法首次成功制备了Mn_3O_4与MOF的复合材料Mn_3O_4/ZIF-8,并通过X射线衍射、扫描电镜、透射电镜、X射线光电子能谱和红外光谱等手段对其进行了表征,探究了Mn_3O_4/ZIF-8的形成机理.考察了Mn_3O_4负载量对Mn_3O_4/ZIF-8催化性能的影响,以及Mn_3O_4/ZIF-8投加量、PMS投加量、初始罗丹明B(RhB)浓度和反应温度对RhB去除效果的影响,同时探究了Mn_3O_4/ZIF-8的重复使用性能,分析了RhB的降解途径、去除机理以及最终的降解副产物.结果表明,边长为50-150 nm的片状Mn_3O_4均匀分散在粒径为250 nm的六边形ZIF-8的外表面;当Mn_3O_4负载量为0.5时,所制备的复合材料0.5-Mn/ZIF-120活化PMS对RhB的降解效果最好,反应60 min时RhB降解率可达到99.4%,且Mn的浸出量可以忽略不计.在该体系中,RhB的降解过程符合一级动力学反应方程,其降解速率常数随催化剂和PMS投加量的增加、反应温度的提高和初始RhB浓度的减小而增大.在0.5-Mn/ZIF-120催化剂投加量为0.4 g/L、PMS投加量为0.3 g/L、初始RhB浓度为10 mg/L、初始溶液pH为5.18及室温(23oC)条件下,水中RhB的降解率在40 min时即可达到98%.淬灭实验表明,该体系中HO·起主导作用,而其主要来源于活化PMS所产生的SO_4–·.此外,通过简单的二次水冲洗方式对0.5-Mn/ZIF-120催化剂进行回收使用,在连续5次循环使用后仍然可见较高的催化活性和稳定性,RhB的去除率保持在96%以上,且Mn的浸出百分率始终低于5%.     

Co-Fe/SBA-15与过一硫酸盐联用非均相催化降解水中染料罗丹明B

由于硫酸根自由基(SO4?-)的强氧化性,基于SO4?-的高级氧化技术受到人们的高度关注.采用过渡金属活化过一硫酸盐(PMS)产生SO4?-用以分解有机物,反应体系简单,反应条件温和,且不需要额外的能量供给,因此,成为人们优先选用的方法,其中,采用高效、环境友好的非均相过渡金属催化剂活化PMS处理难降解有机物成为研究热点.本文研究了非均相CoFe/SBA-15-PMS体系对水中难降解染料罗丹明B(RhB)的降解.以SBA-15为载体, Co(NO3)2·6H2O和Fe(NO3)3·9H2O为前驱物,采用一步等体积浸渍法制备了CoFe/SBA-15,通过X射线衍射(XRD)、N2吸附-脱附、扫描电镜(SEM)、能谱(EDS)、透射电镜(TEM)和振动样品磁强计(VSM)等对其进行了表征.考察了焙烧温度、Co与Fe的负载量对CoFe/SBA-15催化性能的影响和该催化剂的重复使用性能,还考察了RhB降解动力学及催化剂CoFe/SBA-15投加量、氧化剂PMS投加量和反应物(RhB和PMS)初始浓度对其性能的影响,探讨了RhB的降解机理.结果表明：对于催化剂CoFe/SBA-15,合成焙烧后在SBA-15上负载的Fe、Co化合物主要是CoFe2O4复合物,它作为催化剂的活性中心负载在SBA-15的孔道内外.制备的焙烧温度对CoFe/SBA-15催化性能几乎无影响,但对Co浸出影响显著.与SBA-15相比,催化剂10Co9.5Fe/SBA-15-700(Co和Fe负载量分别为10 wt%和9.5 wt%,焙烧温度700 oC)的比表面积、孔体积和孔径均减小,分别为506.1 m2/g,0.669 cm3/g和7.4 nm,但仍然保持SBA-15的有序六方介孔结构.该催化剂以棒状体的聚集态存在,聚集体直径大于0.25μm,其磁化强度为8.3 emu/g,因此,可通过外磁铁容易地从水中分离.相比之下,10Co9.5Fe/SBA-15-700具有最佳的催化性能和稳定性,可使RhB的降解率达到96%以上, Co的浸出量小于32.4μg/L.在CoFe/SBA-15和PMS共存下, RhB的降解符合一级动力学方程, RhB降解速率随CoFe/SBA-15和PMS投加量的增加和初始反应物浓度的减小而提高.淬灭实验结果表明,在CoFe/SBA-15, PMS和RhB水溶液体系中,存在的主要活性自由基为SO4?-,它是由CoFe/SBA-15活化PMS产生的,对RhB的降解起决定性的作用. RhB降解过程的UV-vis结果表明, RhB的降解途径主要是蒽环打开, SO4?-优先攻击RhB的有色芳香烃环,然后RhB进一步分解为小分子有机物. CoFe/SBA-15循环使用10次仍能保持高催化活性和稳定性,在每次反应中RhB的降解率均大于84%, Co和Fe的浸出量均分别小于72.1和35μg/L. CoFe/SBA-15作为高效、环境友好的非均相催化剂可有效地活化PMS产生SO4?-降解水中RhB,具有实际应用的潜力.     

Co-Fe/SBA-15与过一硫酸盐联用非均相催化降解水中染料罗丹明B（英文）

由于硫酸根自由基(SO·-4)的强氧化性,基于SO·-4的高级氧化技术受到人们的高度关注.采用过渡金属活化过一硫酸盐(PMS)产生SO·-4用以分解有机物,反应体系简单,反应条件温和,且不需要额外的能量供给,因此,成为人们优先选用的方法,其中,采用高效、环境友好的非均相过渡金属催化剂活化PMS处理难降解有机物成为研究热点.本文研究了非均相CoFe/SBA-15-PMS体系对水中难降解染料罗丹明B(RhB)的降解.以SBA-15为载体,Co(NO3)2·6H2O和Fe(NO3)3·9H2O为前驱物,采用一步等体积浸渍法制备了CoFe/SBA-15,通过X射线衍射(XRD)、N2吸附-脱附、扫描电镜(SEM)、能谱(EDS)、透射电镜(TEM)和振动样品磁强计(VSM)等对其进行了表征.考察了焙烧温度、Co与Fe的负载量对CoFe/SBA-15催化性能的影响和该催化剂的重复使用性能,还考察了RhB降解动力学及催化剂CoF e/SBA-15投加量、氧化剂PMS投加量和反应物(Rh B和PMS)初始浓度对其性能的影响,探讨了Rh B的降解机理.结果表明:对于催化剂CoFe/SBA-15,合成焙烧后在SBA-15上负载的Fe、Co化合物主要是CoFe2O4复合物,它作为催化剂的活性中心负载在SBA-15的孔道内外.制备的焙烧温度对Co Fe/SBA-15催化性能几乎无影响,但对Co浸出影响显著.与SBA-15相比,催化剂10Co9.5Fe/SBA-15-700(Co和Fe负载量分别为10 wt%和9.5 wt%,焙烧温度700 oC)的比表面积、孔体积和孔径均减小,分别为506.1 m2/g,0.669 cm3/g和7.4 nm,但仍然保持SBA-15的有序六方介孔结构.该催化剂以棒状体的聚集态存在,聚集体直径大于0.25μm,其磁化强度为8.3 emu/g,因此,可通过外磁铁容易地从水中分离.相比之下,10Co9.5Fe/SBA-15-700具有最佳的催化性能和稳定性,可使Rh B的降解率达到96%以上,Co的浸出量小于32.4μg/L.在CoFe/SBA-15和PMS共存下,RhB的降解符合一级动力学方程,Rh B降解速率随CoFe/SBA-15和PMS投加量的增加和初始反应物浓度的减小而提高.淬灭实验结果表明,在Co Fe/SBA-15,PMS和RhB水溶液体系中,存在的主要活性自由基为SO·-4,它是由CoFe/SBA-15活化PMS产生的,对RhB的降解起决定性的作用.RhB降解过程的UV-vis结果表明,RhB的降解途径主要是蒽环打开,SO·-4优先攻击RhB的有色芳香烃环,然后RhB进一步分解为小分子有机物.CoF e/SBA-15循环使用10次仍能保持高催化活性和稳定性,在每次反应中RhB的降解率均大于84%,Co和Fe的浸出量均分别小于72.1和35μg/L.CoFe/SBA-15作为高效、环境友好的非均相催化剂可有效地活化PMS产生SO·-4降解水中RhB,具有实际应用的潜力.     

Ni-N-C单原子催化剂活化过硫酸盐降解苯酚

采用煅烧法制备了以木质素生物炭为载体的单原子催化剂(Ni-N-C-10), 用于高效活化过硫酸盐(PMS)降解苯酚. 利用扫描电子显微镜(SEM)、 透射电子显微镜(TEM)、 经球差校正的高角度环形暗场扫描透射电子显微镜(AC-HAADF-STEM)、 X射线粉末衍射仪(XRD)以及X射线光电子能谱仪(XPS)等对材料进行了表征分析, 证明合成了原子分散的催化剂Ni-N-C-10. 探究了制备过程中双氰胺的投加量和降解实验中催化剂投加量、 PMS投加量、 pH值以及温度对苯酚降解的影响. 结果表明, 在催化剂制备过程中, 加入10倍质量比的双氰胺更有利于实现原子分散. Ni-N-C-10/PMS体系在较低的催化剂和PMS投加量、 以及较宽的pH值范围(3~9)内都能有效活化PMS降解苯酚. 此外, 该体系的稳定性好且应用范围广, 除了能高效降解苯酚外还能快速降解双酚A、 四环素和亚甲基蓝. 电子顺磁共振检测和自由基淬灭实验结果表明, Ni-N-C-10/PMS体系降解苯酚为SO₄^?-、 ·OH和¹O₂ 3种主要活性物种共同作用的结果, 其中¹O₂起主导作用. 反应前后Ni-N-C-10催化剂的XPS分析结果表明, 催化降解苯酚的效率与Ni位点呈正相关.     

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%.     

凹凸棒石负载锰氧化物低温选择性催化还原催化剂的表征及对氨的吸脱附

 以非均相沉淀法制备了凹凸棒石 (PG) 载体上负载锰氧化物催化剂 Mn/PG, 并用于低温选择性催化还原法 (SCR) 脱硝反应. 采用 X 射线衍射、透射电子显微镜和 H2-程序升温还原方法对催化剂进行了表征; 通过 NH3 吸脱附实验考察了催化剂的锰负载量和煅烧温度对 NH3 吸附和脱附量及吸附位的影响. 结果表明, 锰氧化物高度分散于 PG 晶体表面, 其存在状态取决于催化剂煅烧温度. 煅烧温度低于 550 oC, 锰氧化物为 Mn2O3 和 Mn3O4, 煅烧温度为 550 oC 时, 锰氧化物为 Mn3O4. NH3 主要吸附在 PG 载体上, 锰氧化物的担载基本不影响催化剂吸附 NH3 的能力, 但促进了吸附 NH3 的活化, 这是催化剂 SCR 活性显著增加的直接原因.     

TiO2/膨润土光催化降解有机污染物

用溶胶-凝胶法制备了一系列TiO2/膨润土光催化剂(不同负载量和不同焙烧温度), 以罗丹明B(RhB)为模型化合物, 通过测定染料吸光度和体系化学需氧量(COD)变化, 来研究它们在紫外光照射下降解有机污染物的性能. 评价结果表明, 负载量为50%和焙烧温度为400 ℃的催化剂Ti400样品降解RhB活性较好, 虽然其矿化活性略小于P25(光照4 h P25的COD变化为99.7%, 400 ℃焙烧的TiO2/膨润土催化剂Ti400的COD变化为97.0%), 但是TiO2/膨润土催化剂更易于回收再利用. 用Ti400做催化剂降解RhB, 连续循环使用7次, 其催化活性基本不变. 用XRD、BET和紫外可见漫反射(UV-Vis DRS)等方法对这些催化剂进行了表征. 表征结果表明催化剂比表面积大有利于催化活性的提高.     

改性生物炭催化过硫酸氢钾降解染料废水中罗丹明6G的研究

通过煅烧-浸渍法制备了铁酸锰和钴共改性生物碳(Co/MnFe_2O_4/Biochar,CMB),采用扫描电镜(SEM)、X射线能谱仪(EDS)、X射线衍射仪(XRD)、傅里叶红外光谱仪(FTIR)和N_2吸脱附等温仪(BET)对CMB进行形貌观察和结构表征,并用其催化过硫酸氢钾(PMS)降解染料罗丹明6G(Rh 6G),研究了CMB投加量、PMS投加量、溶液初始pH值、水中常见物质(如Cl~-、HCO_3~-、H_2PO_4~-、HA)对CMB/PMS体系降解Rh 6G的影响。实验结果表明,随着CMB和PMS投加量的增大,Rh 6G降解效率也随之增高。在溶液初始pH在5-9范围内,Rh 6G的降解率可达98%以上。Cl~-、HCO_3~-、H_2PO_4~-、HA对CMB催化PMS降解Rh 6G影响微弱。自由基猝灭反应实验结果证明SO_4·~-、~1O_2和O_2~-·对Rh 6G的降解起主要作用。重复利用实验表明,CMB经过五次循环使用后,降解率仍可达76.7%。     

钴催化过一硫酸氢盐降解水中有机污染物:机理及应用研究

钴/过一硫酸氢盐(Co/PMS)是为了克服Fenton技术的诸多缺陷而基于类Fenton思路(过氧化物+过渡金属)建立起来的一种高级氧化技术。该体系具有Co用量少(μg/L数量级),产生的SO₄^-·氧化还原电位高,能够在广泛的pH范围(2-9)降解有机污染物,反应后不产生污泥等优点,在环境污染治理领域具有广阔的应用前景。本文从自由基链式反应、溶液pH、阴离子效应、光照条件、反应气氛及固液两相交换六个方面分析了Co/PMS体系降解水中有机污染物的机理,并在此基础上综述了Co/PMS (黑暗条件)、UV/Co/PMS、Vis/Co/PMS三类均相Co/PMS体系以及Co氧化物催化、Co负载催化两类非均相Co/PMS体系降解水中有机污染物的国内外研究进展,并就存在的问题提出了展望。     

超声-光催化降解水中有机污染物

超声-光催化是一项近年发展起来的废水处理的新型高级氧化技术。该技术利用超声的空化效应、自由基效应以及机械效应强化光催化的催化效能,实现超声和光催化对水中有机污染物的协同降解。本文从水中有机污染物的超声-光催化降解机理、降解动力学、影响因素（光催化剂类型和投加量、超声频率和强度、溶液pH值、温度、反应物初始浓度、溶解性气体和离子强度）和反应器类型（悬浮型、固定床型）4个方面介绍了相关研究进展,提出了目前存在的主要问题,并展望了超声-光催化降解水中有机污染物的发展方向。     

Heterometallic Cr-Mn complexes containing cyanide and oxalate bridges

Three heterometallic Cr-Mn compounds, {Mn(mu-ox)0.5(H2O) [Cr(phen)(CN)4]}n.n H2O.2n CH3OH, (1), {Mn(mu-ox)0.5(H2O)[Cr(bpy)(CN)4]}n.2n H2O x n CH3OH, (2), and {Mn(mu-ox)0.5(bpy)[Cr(bpy)(CN)4]}n, (3) (ox = oxalate), containing cyanide and oxalate bridges based on building blocks [Cr(L)(CN)4]- (L = phen and 2,2'-bipyridine) have been prepared. A new approach was first employed to synthesize ox-bridged compounds via facile oxidation-hydrolysis reactions of diaminomaleonitrile. X-ray crystallography revealed that the structures of 1 and 2 are similar, where cyano-bridged corrugated ladderlike chains are further connected through bis-bidentate oxalato bridges to unique two-dimensional layered structures. Of note is that the introduction of 2,2'-bipyridine led to an interesting cluster-based chainlike compound (3) with cyano-bridged squares [Mn2Cr2] extended by ox bridges. Magnetic studies show antiferromagnetic (AF) interaction between cyano-bridged Cr(III)-Mn(II) and ox-bridged Mn(II)-Mn(II) ions, with the result that 1 and 2 exhibit AF ordering with spin-flop behaviors below 18 and 19 K, respectively.     

Visible light-driven BiOI/ZIF-8 heterostructure and photocatalytic adsorption synergistic degradation of BPA

A novel binary photocatalytic composite (BiOI/ZIF-8) was successfully constructed by solvothermal method. Its crystal morphology, chemical state of the elements and electrochemical properties were characterized by X-ray diffraction, Fourier transform infrared spectroscopy, transmission electron microscopy, scanning electron microscopy, X-ray photoelectron spectroscopy and photoluminescence analysis. Appropriate ZIF-8 doping enhanced the separation and utilization of photogenerated electrons, promoted the capture of contaminants and rapidly produces active species, thereby accelerating the photocatalytic degradation of contaminants. Degradation experiments on BPA showed that the photocatalytic property of BiOI/ZIF-8 (0.5) was significantly improved compared with the parent material. BiOI/ZIF-8 (0.5) showed the highest reaction rate constant (0.06061 min^?1), 9.2 times that of BiOI (0.00659 min^?1) and 23.3 times that of ZIF-8 (0.0026 min^?1). In addition, five cycle tests showed that BiOI/ZIF-8 was highly efficient in recycling and stability. Through capture experiments, superoxide free radicals ·OH, h^? and ·O₂^? play an important role in degrading BPA, among which superoxide free radicals h⁺ play a major role.

     

NaF浸泡处理对BiOBr光催化降解有机染料罗丹明B的影响

以五水硝酸铋(Bi(NO_3)_3·5H_2O)和溴代十六烷基吡啶(CPB)为原料,通过水热法合成溴氧化铋(BiOBr)光催化剂,并在pH=3.3的条件下分别用0.01 mol/L、0.1 mol/L、0.3 mol/L NaF溶液对其进行浸泡氟化处理得新催化剂BiOBr-F_(0.01)、BiOBr-F_(0.1)和BiOBr-F_(0.3).运用XRD(X-射线衍射)、SEM(扫描电镜)、UV-Vis DRS(紫外-可见漫反射光谱)、XPS(X-射线光电子能谱)、FL(荧光光谱)等技术对催化剂的物理结构及性质进行表征并研究了其在可见光(λ≥420 nm)下对有机染料罗丹明B(Rhodamine B,RhB)的催化降解活性.结果表明,随着NaF浓度增加,催化剂的结构及性质均发生一定程度的改变.氟化使得BiOBr对RhB的矿化能力减弱;但BiOBr-F_(0.1)使RhB褪色加快.RhB在降解过程中涉及到超氧自由基(O_2~(·-))、羟基自由基(·OH)及空穴(h~+)氧化,矿化率减小归因于活性物种产量降低,BiOBr-F_(0.1)使褪色加速则是加快了RhB的脱烷基过程,使最大吸收峰快速蓝移.     

Preparation and characterization of ZIF-8 and ZIF-67 incorporated poly(vinylidene fluoride) membranes for pervaporative separation of methanol/water mixtures

Metal–organic frameworks (MOFs) are made up of metal centers and organic binders with larger surface area and distinct pore structures. Particularly significant advancement in MOF membranes has been achieved in three different directions: preparation of MOF membranes with larger surface area, improving the membrane performance by surface modification, and its usage with added features. However, its significance has not been completely known and concluded yet. MOF membranes are used in a variety of membrane-based separation like gas permeation, nanofiltration, pervaporation, membrane distillation, etc. This research aims to synthesize MOFs (ZIF-8 and ZIF-67) and MOF membranes (ZIF-8/PVDF and ZIF-67/PVDF) and used them in the pervaporative separation of the methanol/water mixture. MOFs and MOF membranes were characterized by Fourier transform infrared spectroscopy, scanning electron microscopy, X-ray diffraction, and thermogravimetry analysis. Methanol/water mixtures were be used to study the performance of the prepared membranes. A study on the process parameters such as temperature (40, 45, 50, and 55°C), feed pressure (4, 8, 12, and 16 psi), and feed composition (10%, 20%, 30%, and 40% of water) was carried out to examine the effect of each process parameters for pure membrane. In contrast, Taguchi screening design was used to screen the most influential process variable. The optimized conditions based on Taguchi screening method were 55°C, 12 psi, and 40 %vol of water in feed. The obtained total flux of 425 L/m²h was observed for M3 membrane. As feed temperature increased, the total flux of all three membranes was increased.     

亚微米级Cu0/Fe3O4复合物多相催化过一硫酸盐降解有机污染物

过一硫酸盐催化活化技术因其可产生强氧化性活性氧化物种,可快速氧化降解并矿化有机污染物的优异性能而备受关注.本文成功制备了亚微米级Cu0/Fe3O4复合物,发现其能多相催化过一硫酸盐产生单线态氧降解有机污染物.首先,以CuCl2·2H2O,FeCl2·4H2O和FeCl3·6H2O为铜源和铁源,水合肼为还原剂,采用水热法在180oC反应24 h制备了亚微米级磁性Cu0/Fe3O4复合物.表征结果显示,所制材料为Cu0和Fe3O4的复合物,颗粒大小约为220 nm;单一相Cu0和Fe3O4晶体粒径分别为33.8和106.2 nm,而Cu0/Fe3O4复合物中Cu0和Fe3O4晶体粒径分别减为20.8和31.9 nm.这表明Cu0和Fe3O4复合降低了Cu0和Fe3O4晶体粒径,有利于Cu0和Fe3O4的分散.BET测试结果表明,Cu0/Fe3O4复合物比表面积为4.6 m2/g,与Cu0颗粒的(4.2 m2/g)相当,但远小于Fe3O4的(15.6 m2/g).制备的Cu0/Fe3O4复合物可有效催化过一硫酸盐产生单线态氧降解罗丹明B、亚甲基蓝、金橙II、苯酚和对氯酚.当Cu0/Fe3O4复合物的用量为0.1 g/L,过一硫酸盐浓度为0.5 mmol/L和初始pH为7时,Cu0/Fe3O4复合物可在30 min内完全降解20μmol/L的罗丹明B、亚甲基蓝、金橙II以及0.1 mmol/L的苯酚和对氯酚.对比试验显示,在相同条件下,Cu0和Fe3O4颗粒分别可以降解28%和20%的罗丹明B.这表明Cu0/Fe3O4复合物中的Cu0和Fe3O4晶体在催化过一硫酸盐降解污染物的反应中具有协同作用,这主要来源于Cu0/Fe3O4复合物中Cu0和Fe3O4的晶体粒径变小和更好的分散.采用分光光度法测定了降解反应液中铜和铁离子的溶出量.当Cu0/Fe3O4复合物的用量为0.1 g/L,过一硫酸盐浓度为0.5 mmol/L和初始pH为7时,反应60 min后,降解液中铜和铁离子的浓度分别为0.22和0.1 mg/L,仅占复合物中总铜和总铁量的1.1%和0.2%,表明Cu0/Fe3O4复合物具有较强的化学稳定性.所制Cu0/Fe3O4复合物具有超顺磁性,借助磁场实现快速分离回收,可循环利用五次,表明其优越的催化稳定性.通过加入乙醇和叠氮化钠,考察了Cu0/Fe3O4复合物催化活化过一硫酸盐体系中的活性氧化物种.发现100 mmol/L乙醇的加入对污染物的降解无明显影响,而加入同等量的叠氮化钠可完全抑制污染物的降解,表明Cu0/Fe3O4复合物催化活化过一硫酸盐产生的主要活性氧物种为单线态氧.采用电子顺磁共振谱进一步证实了单线态氧的生成.基于以上研究,Cu0/Fe3O4复合物催化活化过一硫酸盐的机理为Cu0/Fe3O4作为一个电子媒介加速过一硫酸盐和污染物之间的电子转移,从而导致污染物被快速降解.该反应机理不同于常见的金属催化过一硫酸盐产生硫酸根和羟自由基的反应机理.我们推测,电导性优良的Cu0在此催化反应中起着关键性作用.本催化方法可作为一种绿色的氧化技术用于环境污染物的氧化降解处理.     

Insights into the mechanism of O₂ formation and release from the Mn₄O₄L₆ "cubane" cluster

To probe photoinduced water oxidation catalyzed by the Mn?O?L? cubane clusters, we have computationally studied the mechanism and controlling factors of the O? formation from the [Mn?O?L?] catalyst, 6. It was demonstrated that dissociation of an L = H?PO?? ligand from 6 facilitates the direct O-O bond formation that proceeds with a 28.3 (33.4) kcal/mol rate-determining energy barrier at the transition state TS1. This step (the O-O single bond formation) of the reaction is a two-electron oxidation/reduction process, during which two oxo ligands are transformed into to μ2:η2-O?2? unit, and two ("distal") Mn centers are reduced from the 4+ to the 3+ oxidation state. Next two-electron oxidation/reduction occurs by "dancing" of the resulted O?2? fragment between the Mn1 and Mn2/Mn(2')-centers, keeping its strong coordination to the Mn(1')-center. As a result of this four-electron oxidation/reduction process Mn centers of the Mn?-core of I transform from {Mn1(III)-Mn(1')(III)-Mn2(IV)-Mn(2')(IV)} to {Mn1(II)-Mn(1')(II)-Mn2(III)-Mn(2')(III)} in IV. In other words, upon O? formation in cationic complex [Mn?O?L?](+), I, all four Mn-centers are reduced by one electron each. The overall reaction I → TS1 → II → III → TS2 → IV → TS3 → V → VI + O? is found to be exothermic by 15.4 (10.5) kcal/mol. We analyze the lowest spin states and geometries of all reactants, intermediates, transition states, and products of the targeted reaction.     

高可见光催化降解污染物和产氢活性的Z型N-掺杂K4Nb6O17/g-C3N4异质结

随着人口增长和全球工业化进程加快,人们饱受环境污染和能源短缺问题的困扰.半导体光催化技术作为一种高效、可持续、环境友好、有潜力的新技术,在环境净化和能源开发方面有着广阔的应用前景.到目前为止,人们已开发出多种半导体光催化剂,并广泛应用于污染物降解、氢气制备和二氧化碳还原等领域.其中,化合物K4Nb6O17具有典型的层状结构、合适的电子能带结构、结构易改性以及良好的电荷传输性能等特点,在光催化领域得到了广泛研究.然而,单纯K4Nb6O17仍存在光响应范围窄、光生载流子复合率高等问题,限制了K4Nb6O17的进一步应用.因此,需要对K4Nb6O17进行改性,拓宽其光吸收范围,提高其光生载流子分离效率,从而提高其光催化活性.本研究通过简单焙烧法制备Z型N-掺杂K4Nb6O17/g-C3N4(KCN)异质结光催化剂,其中石墨相氮化碳(g-C3N4)在复合材料中质量比约为50%.层状K4Nb6O17层板的电子结构通过N掺杂进行调控,拓宽其光响应范围,使其具有可见光响应;同时,形成的g-C3N4位于N-掺杂K4Nb6O17的外层以及内层空间,在这两种组分之间形成异质结,有利于提高光生载流子的分离效率.荧光光谱、时间分辨荧光光谱和光电化学测试表明,N掺杂和异质结的形成有利于增强光生电子-空穴对的传输和分离效率.通过在可见光照射下降解罗丹明B(RhB)和产氢来评估材料的光催化性能.相比g-C3N4(8.24μmol/h)和Me-K4Nb6O17(~1.30μmol/h),KCN复合材料光催化产氢效率(~16.91μmol/h)得到了极大提高,并显示出极好的光催化产氢稳定性能.对于光催化降解RhB体系,KCN复合材料也显示出较好的光催化活性和稳定性,并能很好地将RhB矿化.鉴于KCN复合材料具有较小的比表面积(9.9 m^2/g)且无孔结构,认为比表面积对光催化活性影响较小.因此,与单组分相比,KCN复合材料光催化产氢和RhB降解活性都得到了极大提高,活性的增强主要归功于N掺杂和异质结形成的协同效应,其中N掺杂可以拓宽光捕获能力,异质结形成可提高电荷载流子的分离效率.电子自旋共振(ESR)谱表明,在KCN降解RhB体系中,超氧自由基(·O2^?)、羟基自由基(·OH)和空穴(h^+)作为主要活性物质都参与了反应.结合实验结果可以推测KCN复合材料满足了Z型光催化体系,该体系具有高效的光生载流子分离效率和较高的氧化还原能力.     

Heterojunction of BiPO4/BiOBr photocatalysts for Rhodamine B dye degradation under visible LED light irradiation

BiOBr synthesized by alcoholysis precipitation is used in the preparation of BiPO₄/BiOBr composites by adding H₃PO₄. Pristine BiOBr and a series of BiPO₄/BiOBr composites have been successfully synthesized using an entirely room-temperature production process. X-ray powder diffraction, scanning electron microscopy, High-resolution transmission electron microscopy, X-ray photoelectron spectroscopy, UV–vis absorption spectroscopy were used to investigated the bulk structure, surface morphology, element composition and optical properties of the samples. The degradation effect of different proportions of BiPO₄/BiOBr composites, BiOBr and BiPO₄ on Rhodamine B (RhB) was evaluated under visible LED light irradiation. Compared to pure BiOBr and BiPO₄, the as-synthesized BiPO₄/BiOBr composites showed enhanced performance, with 30% BiPO₄/BiOBr composite showing the best performance, as it could degrade 95.66% of RhB (100 ml, 15 mg/L) within 120 min. The enhanced photocatalytic activity of BiPO₄/BiOBr was attributed to the heterojunction formation between BiOBr and BiPO₄ and efficient charge separation.     

Substituent effects on core structures and heterogeneous catalytic activities of Mn(III)(μ-O)2Mn(IV) dimers with 2,2':6',2″-terpyridine derivative ligands for water oxidation

[(OH(2))(R-terpy)Mn(μ-O)(2)Mn(R-terpy)(OH(2)) ](3+) (R-terpy = 4'-substituted 2,2':6',2″-terpyridine, R = butoxy (BuO), propoxy (PrO), ethoxy (EtO), methoxy (MeO), methyl (Me), methylthio (MeS), chloro (Cl)) have been synthesized as a functional oxygen-evolving complex (OEC) model and characterized by UV-vis and IR spectroscopic, X-ray crystallographic, magnetometric, and electrochemical techniques. The UV-vis spectra of derivatives in water were hardly influenced by the 4'-substituent variation. X-ray crystallographic data showed that Mn centers in the Mn(III)(μ-O)(2)Mn(IV) cores for derivatives with R = H, MeS, Me, EtO, and BuO are crystallographically indistinguishable, whereas the derivatives with R = MeO and PrO gave the significantly distinguishable Mn centers in the cores. The indistinguishable Mn centers could be caused by rapid electron exchange between the Mn centers to result in the delocalized Mn(μ-O)(2)Mn core. The exchange integral values (J = -196 to -178 cm(-1)) for delocalized cores were lower than that (J = -163 to -161 cm(-1)) for localized cores, though the Mn···Mn distances are nearly the same (2.707-2.750 ?). The half wave potential (E(1/2)) of a Mn(III)-Mn(IV)/Mn(IV)-Mn(IV) pair of the derivatives decreased with an increase of the electron-donating ability of the substituted groups for the delocalized core, but it deviated from the correlation for the localized cores. The catalytic activities of the derivatives on mica for heterogeneous water oxidation were remarkably changed by the substituted groups. The second order rate constant (k(2)/mol(-1) s(-1)) for O(2) evolution was indicated to be correlated to E(1/2) of a Mn(III)-Mn(IV)/Mn(IV)-Mn(IV) pair; k(2) increased by a factor of 29 as E(1/2) increased by 28 mV.