专利文摘

一种利用含锂废液生产氯化锂的方法，一种用冶金渣制备聚硅硫酸铁铝的方法，负载型纳米二氧化钛的弥散光纤光催化反应器，乙烯碱洗废液再生处理工艺，一种复合活性炭脱硫剂的制备方法     

低浓度有机废气纳米TiO2光催化处理技术

对常用有机废气净化技术进行了比较分析,以活性炭过滤网的强吸附性复合TiO2光催化剂研究为主,分析了纳米TiO2光催化处理低浓度有机废气的反应原理,叙述了几种常见负载型TiO2光催化剂的制备方法,影响TiO2光催化效率的因数及提高TiO2光催化剂的催化性能方式.     

铁律铁腕保安全

不久前，一个触目惊心的新名词，赫然出现在不少媒体上，它就是“公共安全危机”。对于“安全”一词，人们并不陌生，它曾让国家和人民群众在不断深刻认识它的过程中，付出了十分惨重的代价。     

ZVI/EDDS/Air体系降解水中2,4-二氯酚的研究

建立零价铁(ZVI)、乙二胺二琥珀酸(EDDS)和曝气三者组成的类Fenton(ZVI/EDDS/Air)处理体系,考察了初始EDDS浓度、铁粉投加量、曝气速率、2,4-二氯酚(2,4-DCP)浓度、初始pH以及反应温度等对水溶液中2,4-DCP降解的影响.结果表明,该体系能有效降解2,4-DCP,并且其降解规律符合准一级动力学方程.在2,4-DCP质量浓度100 mg·L-1、EDDS浓度0.80 mmol.L-1、铁粉投加量20 g·L-1、曝气速率为2 L.(min.L)-1的最佳实验条件下室温反应1 h,2,4-DCP的降解率达到99%.ZVI/EDDS/Air体系对氯酚的降解较ZVI/EDTA/Air体系具有环境友好、反应条件温和,而且对2,4-DCP的降解效果好等优点.     

催化湿式氧化法降解水中的β-萘酚

采用催化湿式氧化法降解β-萘酚,制备了一系列MnOx/nano-TiO2催化剂,对其制备条件、反应条件及催化剂的稳定性进行了研究,同时对催化剂进行了X射线衍射(XRD)、X射线光电子能谱(XPS)及程序升温还原(TPR)等表征.结果表明,Mn负载量过高时,高分散的MnO2和Mn2O3聚集形成相应的晶相,导致了β-萘酚COD去除率的降低;焙烧温度过高时,可能是因为形成较多活性较差的Mn2O3,MnO2和Mn2O3之间的电子传递作用被削弱,造成COD去除率的降低;催化剂使用6次后COD去除率略微降低可能是和对应的衍射峰峰强度下降有关.当Mn负载量(质量分数)为4%、焙烧温度为450℃时所制备的MnOx/nano-TiO2催化剂活性较好,其在反应温度为110℃、反应总压力为0.5 MPa的条件下催化β-萘酚降解时COD去除率可达96.4%.该催化剂重复使用6次后β-萘酚COD去除率仍可达92.4%.采用原子吸收光谱(AAS)分别测定50、80、110及150℃时反应后溶液中Mn的溶出量,均低于9.3 mg·L-1,催化剂稳定性较好.根据文献对β-萘酚的降解路径进行了推测.     

基于零价铁的双金属体系对六氯苯还原脱氯研究

利用Ag、Pb和Cu作为催化金属与微米级铁粉制成不同的双金属体系还原脱氯六氯苯(hexachlorobenzene,HCB),探讨不同催化金属种类、不同双金属添加量以及不同离子强度3种因素对HCB脱氯效率的影响,并剖析双金属催化条件下HCB的脱氯规律.结果表明,微米级铁粉对HCB几乎无还原脱氯效果,添加Ag、Pb和Cu对HCB均具有良好的催化脱氯能力,当Ag/Fe、Pb/Fe和Cu/Fe的最佳比例分别为0.2%、0.5%和1%时,反应2 h后HCB的脱氯率分别达到93.5%、88.5%和49.6%;同时,由于催化金属均匀附着在零价铁表面可以形成更多的微型原电池,故增加双金属投加量可有效提高HCB脱氯速率,0.1 g Pb/Fe对HCB脱氯率为38.3%,而0.8 g Pb/Fe对HCB脱氯率可达到88.6%;另外,离子强度增大对HCB的脱氯也有一定促进作用,在Na2SO4浓度分别为0、0.05和0.5 mol·L-1的3个反应器中,反应2 h后HCB脱氯率分别达到93.5%、98.0%和98.9%.     

Graphene-supported nanoscale zero-valent iron：Removal of phosphorus from aqueous solution and mechanistic study

Excess phosphorus from non-point pollution sources is one of the key factors causing eutrophication in many lakes in China,so finding a cost-effective method to remove phosphorus from non-point pollution sources is very important for the health of the aqueous environment. Graphene was selected to support nanoscale zero-valent iron(nZVI)for phosphorus removal from synthetic rainwater runoff in this article. Compared with nZVI supported on other porous materials,graphene-supported nZVI(G-nZVI) could remove phosphorus more efficiently. The amount of nZVI in G-nZVI was an important factor in the removal of phosphorus by G-nZVI,and G-nZVI with 20 wt.% nZVI(20% G-nZVI)could remove phosphorus most efficiently. The nZVI was very stable and could disperse very well on graphene,as characterized by transmission electron microscopy(TEM) and scanning electron microscopy(SEM). X-ray photoelectron spectroscopy(XPS),Fourier Transform infrared spectroscopy(FT-IR) and Raman spectroscopy were used to elucidate the reaction process,and the results indicated that Fe-O-P was formed after phosphorus was adsorbed by G-nZVI. The results obtained from X-ray diffraction(XRD) indicated that the reaction product between nZVI supported on graphene and phosphorus was Fe3(PO4)2·8H2O(Vivianite). It was confirmed that the specific reaction mechanism for the removal of phosphorus with nZVI or G-nZVI was mainly due to chemical reaction between nZVI and phosphorus.     

Combination of heterogeneous Fenton-like reaction and photocatalysis using Co-TiO2 nanocatalyst for activation of KHSO5 with visible light irradiation at ambient conditions

A novel coupled system using Co–Ti O2 was successfully designed which combined two different heterogeneous advanced oxidation processes, sulfate radical based Fenton-like reaction（SR-Fenton） and visible light photocatalysis（Vis-Photo）, for degradation of organic contaminants. The synergistic effect of SR-Fenton and Vis-Photo was observed through comparative tests of 50 mg/L Rhodamine B（Rh B） degradation and TOC removal. The Rhodamine B degradation rate and TOC removal were 100% and 68.1% using the SR-Fenton/Vis-Photo combined process under ambient conditions, respectively. Moreover, based on XRD, XPS and UV-DRS characterization, it can be deduced that tricobalt tetroxide located on the surface of the catalyst is the SR-Fenton active site, and cobalt ion implanted in the Ti O2 lattice is the reason for the visible light photocatalytic activity of Co–Ti O2. Finally, the effects of the calcination temperature and cobalt concentration on the synergistic performance were also investigated and a possible mechanism for the synergistic system was proposed. This coupled system exhibited excellent catalytic stability and reusability,and almost no dissolution of Co2＋was found.     

Heterogeneous Fenton-like degradation of 4-chlorophenol using iron/ordered mesoporous carbon catalyst

Ordered mesoporous carbon supported iron catalysts(Fe/OMC) were prepared by the incipient wetness impregnation method and investigated in Fenton-like degradation of 4-chlorophenol(4CP) in this work. XRD and TEM characterization showed that the iron oxides were well dispersed on the OMC support and grew bigger with the increasing calcination temperature. The catalyst prepared with a lower calcination temperature showed higher decomposition efficiency towards 4CP and H2O2, but more metals were leached. The effect of different operational parameters such as initial pH, H2O2 dosage, and reaction temperature on the catalytic activity was evaluated. The results showed that 96.1% of 4CP and 47.4% of TOC was removed after 270 min at 30°C, initial pH of 3 and 6.6 mmol/L H2O2. 88% of 4CP removal efficiency was retained after three successive runs, indicating Fe/OMC a stable catalyst for Fenton reaction. 4CP was degraded predominately by the attack of hydroxyl radical formed on the catalyst surface and in the bulk solution due to iron leaching. Based on the degradation intermediates detected by high performance liquid chromatography, possible oxidation pathways were proposed during the 4CP degradation.     

Synthesis of carbon-coated magnetic nanocomposite (Fe3O4@C) and its application for sulfonamide antibiotics removal from water

The occurrence of antibiotics in the environment has recently raised serious concerns regarding their potential threat to human health and aquatic ecosystem. A new magnetic nanocomposite, Fe304@C （Fe304 coated with carbon）, was synthesized, characterized, and then applied to remove five commonly-used sulfonamides （SAs） from water. Due to its combinational merits of the outer functionalized carbon shell and the inner magnetite core, Fe3O4@C exhibited a high adsorption affinity for selected SAs and a fast magnetic separability. The adsorption kinetics of SAs on Fe304 @ C could be expressed by the pseudo second-order model. The adsorption isotherms were fitted well with the Dual-mode model, revealing that the adsorption process consisted of an initial partitioning stage and a subsequent hole-filling stage. Solution pH exerted a strong impact on the adsorption process with the maximum removal efficiencies （74% to 96%） obtained at pH 4.8 for all selected SAs. Electrostatic force and hydrogen bonding were two major driving forces for adsorption, and electron-donor-acceptor interactions may also make a certain contribution. Because the synthesized Fe304@C showed comprehensive advantages of high adsorptivity, fast magnetic separability, and prominent reusability, it has potential applications in water treatment.