改性凹凸棒石黏土负载纳米铁/钯双金属对4,4′-二溴联苯醚的去除研究

通过分步还原法制备了改性凹凸棒石黏土负载纳米零价铁/钯双金属复合材料(OA-Fe/Pd),并通过X射线衍射(XRD)、透射电镜(TEM)和傅里叶变换红外吸收光谱(FTIR)对其进行表征.以改性凹凸棒石黏土(OA)和改性凹凸棒石黏土负载纳米零价铁材料(OA-Fe)为对照,探讨了OA-Fe/Pd对溶液中4,4′-二溴联苯醚(BDE15)的去除性能,并考察了Pd负载量、材料投加量、BDE15初始浓度、溶剂条件和溶液初始pH对去除BDE15的影响.XRD和TEM表征结果表明纳米零价Fe/Pd双金属颗粒较均匀地分散在OA表面,双金属颗粒粒径小于100 nm.去除动力学实验结果表明OA-Fe/Pd对溶液中BDE15的去除性能显著高于OA和OA-Fe.OA-Fe/Pd对BDE15的去除速率随着Pd负载量和材料投加量的增大而增大,而随着BDE15初始浓度、溶剂中四氢呋喃的比例、溶液初始pH的增大而减小.OA-Fe/Pd对BDE15的去除动力学过程符合准一级动力学方程.OA-Fe/Pd对BDE15的去除机制主要为还原脱溴降解.在适宜的条件下,BDE15可被OA-Fe/Pd完全还原脱溴为联苯醚(DE).     

纳米零价铁去除水体中砷的效能与机理

全球超过一亿人受到高毒性、难处理的砷污染引发的饮用水安全的威胁,解决砷污染问题迫在眉睫而又任重道远。纳米零价铁(nZVI)能高效去除重(类)金属、硝酸盐、磷酸盐、高氯酸盐、卤代物、多环芳烃、偶氮染料和苯酚等污染物,成为广泛应用的工程纳米材料之一,在全球已有近60例的环境原位修复和废水处理工程案例。其独特的纳米级核壳结构和表面性质使其能够通过吸附、还原和沉淀等多种作用高效去砷。本文综述了近年来nZVI及其改性材料去除水中砷的研究进展,探讨了nZVI去除水中As(Ⅲ)和As(Ⅴ)的反应机理,归纳了不同反应条件(初始pH值、反应时间、nZVI投加量、砷初始浓度、共存离子和有机质)对去除效果的影响,总结了nZVI改性材料(多孔材料负载改性nZVI、金属掺杂改性nZVI、表面稳定剂改性nZVI和绿色合成nZVI)对砷的去除效率,展望了纳米零价铁去除砷的发展方向和所面临的挑战。     

应用纳米零价铁富集银的研究

大量研究表明,纳米零价铁（nanoscale Zero-Valent Iron,nZVI）对水中重金属,尤其是金、银等稀贵金属,有良好的分离富集作用.利用纳米零价铁反应器证明了nZVI可从废水中分离低浓度的银离子（Ag⁺）,并生成高含量的“银矿石”.此外,也证明了反应区氧化还原电位能够反映nZVI与Ag⁺的反应速率和分离效率.利用X射线衍射仪、X射线光电子能谱和高分辨透射电子显微镜等手段对反应产物进行表征,证实了Ag⁺可被nZVI还原为单质银,并以纳米颗粒的形式（<10 nm）沉积在nZVI表面.与其他材料（常见吸附/还原材料）相比,nZVI具有效率高,受pH影响小的优点.研究结果表明,nZVI是一种能够高效富集痕量银资源并产生高价值纳米银的材料.     

负载零价铁膨胀石墨的合成及对水中NO3-去除的效果与机制

以网络状孔型结构发达的膨胀石墨（EG）为载体,采用化学沉积法制备了负载零价铁（ZVI）的膨胀石墨（EG-ZVI）.利用扫描电子显微镜（SEM）、X射线衍射（XRD）仪及X射线光电子能谱仪（XPS）等对负载及反应前后的EG-ZVI进行表征,探究了EG-ZVI对硝酸根（NO₃^-）的去除效果并对其反应产物及机理进行了分析.结果表明,亚微米级零价铁已负载到EG石墨表面,且分布均匀;与EG相比,EG-ZVI对NO₃^-的去除能力显著提升,其去除率是EG的2.3倍.得益于铁碳原电池效应,EG-ZVI对pH依赖性比零价铁低,即使在pH=9的条件下,NO₃^-去除率依然能达到65%以上,是单独用零价铁处理时的1.83倍;EG-ZVI去除NO₃^-是吸附和还原过程共同作用的结果,符合三级动力学模型,其还原过程由负载在EG表面的零价铁发生腐蚀提供电子,从而还原NO₃^-产生以NH₄⁺-N为主的含氮化合物;EG-ZVI对NO₃^-具有较强的还原吸附作用,并能解决零价铁在反应过程中生成惰性层或金属氢氧化物导致去除效率低的缺陷,使其在含NO₃^-废水的处理中具有较高的应用潜力.     

铁基双金属材料还原降解三溴甲烷的研究

本文制备了Cu/Fe和Pd/Fe两种铁基双金属材料,考察它们对溴仿(CHBr₃)的还原去除效果。结果表明,溴仿的还原去除效果都随双金属材料投加量的增加而增加;溶液中H⁺浓度越高,越有利于还原反应的进行;溶解氧的存在会对还原去除反应产生抑制作用。双金属材料与溴仿的还原去除反应包括直接还原和间接还原两种途径。Pd和Cu通过与零价铁组成原电池结构加快了零价铁在水中的腐蚀速度,从而增强了零价铁对溴仿的直接还原去除效果。Pd与Cu相比,具有更高的氢过电位,氢气更容易在Pd的表面生成,而氢气也可以作为还原剂,取代溴仿分子中的溴原子,完成还原脱卤。因此,Pd/Fe双金属材料对溴仿的还原去除效果要好于Cu/Fe双金属材料。     

NiO/还原氧化石墨烯的溶剂热合成以及作为高循环稳定性超级电容器电极材料的性能表征

通过简单的溶剂热法以及其后续热处理过程,制备了NiO纳米花和NiO/还原氧化石墨烯(rGO)复合物。在NiO/rGO复合物中,rGO作为基底生长NiO,与此同时,NiO则有效的避免了rGO的团聚。采用热重分析(TG)、场发射扫描电子显微镜(FE-SEM)和X射线衍射对样品的成分、形貌和结构进行了表征。NiO/rGO复合物(NiO和rGO的质量比为82.7∶17.3)电极呈现优异的电化学性能。在1 A/g时,初始比电容为514.9 F/g,当材料完全活化后,其比电容高达600 F/g。同时,在电流密度为10 A/g时,相比于1 A/g时的比电容保持率为83.5%。此外,该电极材料具有非常优异的循环稳定性,6000次循环后电容衰减率为7.4%。表明所制备的复合物是一种有应用价值的超级电容器电极材料。     

NiO/rGO的溶剂热合成以及作为高循环稳定性超级电容器电极材料的性能表征

通过简单的溶剂热法以及其后续热处理过程,制备了NiO纳米花和NiO/还原氧化石墨烯（rGO）复合物。 在NiO/rGO复合物中,rGO作为基底生长NiO,与此同时,NiO则有效的避免了rGO的团聚。 采用热重分析(TG)、场发射扫描电子显微镜(FE-SEM)和X射线衍射对样品的成分、形貌和结构进行了表征。 NiO/rGO复合物（NiO和rGO的质量比为82.7∶17.3）电极呈现优异的电化学性能。 在1 A/g时,初始比电容为514.9 F/g,当材料完全活化后,其比电容高达600 F/g。 同时,在电流密度为10 A/g时,相比于1 A/g时的比电容保持率为83.5%。 此外,该电极材料具有非常优异的循环稳定性,6000次循环后电容衰减率为7.4%。 表明所制备的复合物是一种有应用价值的超级电容器电极材料。     

纳米银/二维石墨相氮化碳/还原氧化石墨烯复合材料的制备及其光催化降解抗生素

为优化石墨相氮化碳(g-C₃N₄)光催化剂的结构,改善其对污染物的降解性能,本文以三聚氰胺为前驱体,通过高温煅烧和热氧化剥离制备了二维石墨相氮化碳(2D-C₃N₄),并用光还原法一步合成纳米银/二维石墨相氮化碳/还原氧化石墨烯(Ag/2D-C₃N₄/rGO)复合光催化剂。通过X射线粉末衍射(XRD)、扫描电子显微镜(SEM)、透射电子显微镜(TEM)、紫外-可见漫反射光谱(UV-Vis DRS)、光致发光光谱(PL)、X射线光电子能谱(XPS)、氮气吸附脱附等温曲线(BET)等对材料进行表征。 以头孢曲松钠为目标污染物,探究pH值、催化剂用量、头孢曲松钠初始浓度等因素对催化剂的吸附、降解性能的影响,并探究降解反应机理。 当pH=6.0,催化剂用量为0.3 g/L,头孢曲松钠初始浓度为10.0 mg/L时,复合材料对头孢曲松钠的降解率可达到89.1%。 催化剂的稳定性较强,具有实际应用价值,可用于处理含头孢类抗生素的废水。     

水中菲的类Fenton氧化降解及动力学研究

采用类Fenton氧化法对水溶液中的菲进行深度处理,研究纳米零价铁(n ZVI)投加量、H2O2投加量、溶液p H值和温度四个主要因素对菲去除效果的影响。结果表明在纳米零价铁(n ZVI)投加量为1.0 g/L、H2O2为10 mmol/L、p H为3.0、温度30℃的优化条件下,菲的初始投加量(浓度)为50 mg/L在60 min内菲的去除率达到100%。此外类Fenton氧化降解菲符合伪一级降解动力学模型,且菲的投加量(浓度)越高,降解速率越快,进一步说明类Fenton氧化技术对菲降解有很好的效果。     

AuNPs@POMs/rGO复合材料的制备及光催化性能

以Keggin型多金属氧酸盐(多酸,POMs)为光催化还原剂、稳定剂和包覆剂,在光照下一步合成AuNPs@POMs/rGO复合纳米材料。采用透射电镜(TEM)、X射线衍射(XRD)和紫外-可见吸收光谱(UV-vis)等对所制得的材料进行了结构表征和性能测试。以光催化降解甲基橙为模型反应研究了AuNPs@POMs/rGO纳米复合材料的光催化活性。透射电子镜结果显示Au纳米微粒均匀的负载在rGO薄层上,无聚集和团聚现象。实验探究了pH、温度、催化剂投放量以及甲基橙初始浓度对光催化降解过程的影响。光催化降解结果表明:当溶液处于室温,pH=8.0,催化剂投放量为0.15 g·L~(-1),甲基橙溶液初始浓度为25.0 mg·L~(-1)时,效果达到最佳,降解率为94.5%。     

Removal of uranium from aqueous solution using montmorillonite-supported nanoscale zero-valent iron

Montmorillonite-supported nanoscale zero-valent iron (M-nZVI) was synthesized by sodium borohydride reduction and characterized by X-ray diffraction, X-ray photoelectron spectroscopy, and field emission scanning electron microscopy (FE-SEM). The interaction of uranium with M-nZVI was studied using batch technique under different experimental conditions such as pH, ionic strength, initial U(VI) concentration, solid-to-liquid ration (m/V), and temperature. The presence of montmorillonite decreased the aggregation while increased the specific surface area (SSA) of the iron nanoparticles. The SSA for as-synthesized M-nZVI was 91.42 m²/g, higher than 26.60 and 10.23 m²/g for nZVI and montmorillonite, respectively. The removal efficiency of U(VI) using M-nZVI was significantly affected by the pH of the aqueous solution, whereas it was slightly affected by ionic strength and temperature. The isoelectric point of M-nZVI was at pH 5.6; however the results indicated that the optimum removal efficiency of U(VI) using M-nZVI was achieved at a pH range 3.0–5.0. The experiments with aqueous solution containing 100 μg/L of U(VI) showed that the removal efficiency of the as-synthesized M-nZVI was about 978 μg/g at pH 3.0. These results show that M-nZVI has a potential as a novel material for removing U(VI) from aqueous solution.     

Preparation and characterization of palladium/polypyrrole-reduced graphene oxide/foamed nickel composite electrode and its electrochemical dechlorination of triclosan

In this study, a new composite electrode of palladium (Pd) nanoparticles dispersed on polypyrrole-reduced graphene oxide (PPy-rGO) loaded on foam-nickel was achieved by galvanostatic method. Characterization of structures, morphology and crystallinity of the synthesized materials were investigated by scanning electron microscopes (SEM), transmission electron microscope (TEM), X-ray photoelectron spectroscopy (XPS), X-ray diffraction (XRD), Raman spectroscopy and electrochemical impedance spectroscopy (EIS). The results of XPS and XRD demonstrated Pd showed primarily as Pd0. From SEM and TEM results, we had seen that Pd nanoparticles were dispersible well on the composite electrode. Raman spectroscopy was used to show the state of graphene oxide and further demonstrated that PPy and rGO had existed of on the foam Ni matrix. The data of EIS also suggested the charge transfer of the new composite electrode decreased compared to Pd/PPy/foam-Ni and PPy/foam-Ni composite electrodes. The effect of the electropolymerization potential on Pd/PPy-rGO/foam-Ni electrode for removing triclosan (TCS) was examined. It was found that the removal efficiency of TCS on the composite electrode could reach 100% at electropolymerization potential of 0.7 V and reaction time of 100 min.     

Highly active nanoscale zero-valent iron (nZVI)-Fe3O4 nanocomposites for the removal of chromium(VI) from aqueous solutions

For the first time, nanoscale zero-valent iron (nZVI)-Fe(3)O(4) nanocomposites, prepared by an in situ reduction method, are employed for chromium(VI) removal in aqueous environment. 96.4% Cr(VI) could be removed by these novel materials within 2h under pH of 8.0 and initial Cr concentration of 20 mg L(-1), compared with 48.8% by bare nFe(3)O(4) and 18.8% by bare nZVI. Effects of several factors, including mass composition of nZVI-Fe(3)O(4) nanocomposites, initial pH and Cr(VI) concentration, were evaluated. The optimal ratio of nFe(3)O(4) to nZVI mass lies at 12:1 with a fixed nZVI concentration of 0.05 g L(-1). Low pH and initial Cr(VI) concentration could increase both the Cr(VI) removal efficiency and reaction rate. Corresponding reaction kinetics fitted well with the pseudo second-order adsorption model. Free energy change (ΔG) of this reaction was calculated to be -4.6 kJ mol(-1) by thermodynamic study, which confirmed its spontaneous and endothermic characteristic. The experimental data could be well described by the Langmuir and Freundlich model, and the maximum capacity (q(max)) obtained from the Langmuir model was 100 and 29.43 mg g(-1) at pH 3.0 and 8.0, respectively. The reaction mechanism was discussed in terms of the mutual benefit brought by the electron transfer from Fe(0) to Fe(3)O(4).     

Removal of Chromium(VI) from Groundwater Using Oil Shale Ash Supported Nanoscaled Zero-valent Iron

Oil shale ash(OSA) supported nanoscaled zero-valent iron(OSA-nZVI) was used as a rapid and efficient reductant for Cr(VI) reduction. The optimal mass ratio of nZVI to OSA and the optimal dosage were explored. The effects of initial pH, reaction temperature, initial Cr(VI) concentration, and common cations and anions in groundwater on Cr(VI) reduction were determined in batch experiments. The results show that the optimum initial pH is 5.0. The reaction temperature has a positive effect on Cr(VI) reduction while the real groundwater has a negative effect. Additionally, 84.22% Cr(VI) was still reduced by 3 g/L OSA-nZVI(1:2)(mass ratio of OSA to Fe⁰ was 1:2) within 120 min for 50 mg/L Cr(VI) under conditions of 10℃ and unadjusted pH.     

Ni3(HCOO)6/还原氧化石墨烯复合电极材料的制备及电容性能

以氧化石墨烯(GO)为前驱体, Ni(NO₃)₂·6H₂O为镍源, 甲酸为配体, N,N-二甲基甲酰胺为溶剂, 通过一步溶剂热法制备了Ni₃(HCOO)₆/rGO复合电极材料. 研究结果表明, 通过金属镍离子和配体在氧化石墨烯表面超分子自组装成核, 形成了“三明治”式的夹心复合结构; 不同的GO浓度对复合材料的物相结构、 晶体尺寸大小、 形貌及电化学性能有很大的影响; 当GO的浓度为8 mg/mL时, 在100 ℃下反应24 h得到的Ni₃(HCOO)₆/rGO复合材料在电解液为1 mol/L KOH, 5 mV/s下比电容高达940 F/g, 经过500次充放电循环后电容的保持率为96.28%.     

Fe3O4@SiO2@TiO2-Co/rGO磁性光催化剂的合成及其光催化活性研究

采用溶胶-凝胶法和水热法（HTM）合成了Fe₃O₄@SiO₂@TiO₂-Co/rGO复合纳米粒子（磁性光催化剂）,通过X射线衍射、扫描电子显微镜及其能量分散光谱和UV-vis漫反射光谱对产物进行了表征分析.研究了Co掺杂量、溶液pH值、亚甲基蓝（MB）溶液初始浓度以及干扰离子（例如Cl^-、SO₄^2-、CO₃^2-）等因素对MB降解的影响,并对磁性光催化剂的可重复使用性进行了分析.正常实验条件下（pH=7,[MB]=10 mg/L,磁性光催化剂用量=0.1 g/50 mL）,150 min内MB最大去除率达到98.24%.干扰离子影响MB降解次序为CO₃^2- < Cl^- < SO₄^2-,磁性光催化剂重复使用7次MB光降解率仅下降7.07%,新型磁性光催化剂具有良好的MB降解性能和较高的重复使用性能.     

羟基氧化铁/膨胀石墨复合材料的制备及除砷机制

以膨胀石墨为载体材料,采用改进后的综合法制备的羟基氧化铁（FeOOH）为改性材料,在酸性及超声波振荡的条件下对膨胀石墨进行表面接枝,制得羟基氧化铁/膨胀石墨复合材料,并对材料进行扫描电子显微镜（SEM）、X射线衍射（XRD）、傅里叶变换红外光谱（FTIR）和X射线光电子能谱（XPS）表征,随后测试了其除砷性能,并探讨了反应机理.实验结果表明,复合材料中羟基氧化铁通过氢键与化学键均匀负载在了膨胀石墨表面,为亚微米级球状;使用0.5 g复合材料处理50 mL浓度为0.5 mg/L的模拟含砷废水,90 min后去除率可达到99%,且经过处理可以使废水中的砷浓度达到饮用标准;载铁量越高,材料的除砷性能越好,当载铁量达到55%时,使用0.5 g复合材料处理50 mL浓度为2.0 mg/L的模拟含砷废水,1 h后去除率达到72.6%,是普通膨胀石墨的3倍;该除砷过程由解离的羟基氧化铁与砷在复合材料附近完成,符合二级动力学方程和Temkin等温吸附模型.