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1.
用共沉淀法将强吸附性的膨胀石墨与光催化活性优良的锌铁氧体磁粉复合,制备出锌铁氧体/膨胀石墨复合物(ZF/EG)。用现代分析测试技术表征了样品的组成、微观结构,并研究了去污性能。结果表明,实验制备的碳磁复合物不仅保持了EG原有的特殊结构和优良吸附性能,且具有可观的ZF负载率和光催化活性;腐殖酸的去除率与样品中EG和ZF的质量比(mZF/mEG)、吸附时间和溶液的p H值等因素有关。紫外光照射90 min后,0.1 g mEG/mZF=1的ZF/EG复合物对腐殖酸(溶液浓度为15 mg·L~(-1),体积100 m L,p H=7)的去除率达95%,该复合物4次重复使用后,对腐殖酸的去除率仅下降了4%,是一类具有潜在应用前景的绿色环保的高效废水处理剂。  相似文献   

2.
用化学共沉淀法和原位乳液聚合法分别制备了镍锌铁氧体(NixZn1-xFe2O4)、Ni0.7Zn0.3Fe2O4/膨胀石墨(NZF/EG)二元复合物及其聚苯胺(PANI)包覆的三元复合物(NZF/EG/PANI)。用现代测试技术表征了样品的组成、结构、形貌和电磁性能。结果表明,NZF粒子较好地嵌入到EG的层间,PANI对NZF/EG的包覆效果良好;三元复合物的磁性能随磁性组分含量的减小而减弱,而电导率与EG和PANI的导电性及其相对含量相关联;复合物的电磁损耗性能优良,其中三元复合物优于二元复合物。含PANI 70wt%的NZF/EG/PANI三元复合物,制样厚度分别为1.5、2.0和2.5 mm时,其反射损耗峰值(有效带宽)分别为-19.99 dB(5.82 GHz),-20.33 dB (4.08 GHz)和-25.28 dB(3.67 GHz),具有优良的电磁波吸收效果。  相似文献   

3.
采用共沉淀法制备性能优异的层状材料锌铬水滑石(ZnxCr-LDHs, x=2, 3, 4), 并探究各种因素对吸附酸性红14(AR14)的影响。XRD、ICP、FTIR及BET表征结果表明:合成的ZnxCr-LDHs晶型良好且稳定, 具备介孔结构。实验结果表明:最佳吸附剂为Zn3Cr-LDHs, 比表面积为101 m2·g-1, 对AR14的最大吸附容量为484.63 mg·g-1。同时, 降低溶液pH值和提高溶液温度均可促进AR14的吸附。该吸附过程分别符合准二级动力学模型和Freundlich等温吸附模型。结合Materials Studio 5.5软件模拟, 推测该吸附机理主要以表面吸附为主, -SO3-基团是反应点。  相似文献   

4.
采用共沉淀法制备性能优异的层状材料锌铬水滑石(ZnxCr-LDHs, x=2, 3, 4), 并探究各种因素对吸附酸性红14(AR14)的影响。XRD、ICP、FTIR及BET表征结果表明:合成的ZnxCr-LDHs晶型良好且稳定, 具备介孔结构。实验结果表明:最佳吸附剂为Zn3Cr-LDHs, 比表面积为101 m2·g-1, 对AR14的最大吸附容量为484.63 mg·g-1。同时, 降低溶液pH值和提高溶液温度均可促进AR14的吸附。该吸附过程分别符合准二级动力学模型和Freundlich等温吸附模型。结合Materials Studio 5.5软件模拟, 推测该吸附机理主要以表面吸附为主, -SO3-基团是反应点。  相似文献   

5.
以结晶氯化铝(AlCl3·6H2O)作为铝源,十二烷基苯磺酸钠(SDBS)为模板剂,采用水热法在硅藻土盘上制备了束状纳米结构γ-AlOOH/Al2O3复合吸附剂。采用XRD、SEM、TEM、TG/DSC、N2吸脱附等对样品进行了表征。研究了样品对133Cs+及Pb2+的吸附能力。研究表明,样品γ-AlOOH/硅藻土、γ-Al2O3/硅藻土,对Cs+及Pb2+均具有良好的吸附性能,两者对Cs+的去除率分别为98.9%和99.6%;对Pb2+的最大吸附量分别为357.1、416.7 mg·g-1。两种样品对Pb2+的吸附均符合Langmuir吸附模型。  相似文献   

6.
采用共沉淀法制备了3种不同含铁量的氧化铁改性蛭石(Verm-Fex,x=5,10,20),研究了纯蛭石(Verm)和Verm-Fex的表面性质及吸附氟的特性。与样品Verm比较,3种Verm-Fex中Verm的d(002)层间距略有升高;Verm-Fex的孔体积、表面积、表面分形度均随含铁量的增加而升高,其中微孔体积和外表面积的增加幅度更明显。4种样品的等电点(IEP)也随含铁量的增加而明显升高;初始pH=5.0时,它们的表面ζ电位分别为-16.4,-6.1,10.5和28.4 mV。4种样品对氟的等温吸附数据用单吸附位Langmuir模型拟合(R2=0.973~0.995)时,Verm的R2最高;双吸附位Langmuir模型可很好地描述3种Verm-Fex样品的等温吸附过程(R2=0.991~0.998);Freundlich模型对4种样品吸附数据的拟合度较差(R2=0.835~0.937),但R2随样品含铁量的增加而略微升高。初始pH=5.0时,Verm和Verm-Fex(x=5,10,20)对氟的最大吸附容量(qmax)分别为3.18,6.76,9.27和12.43 mg·g-1。可见,Verm-Fex(尤其含铁量较高的产物)对表生环境中氟的吸附固定性能明显高于Verm。  相似文献   

7.
采用共沉淀法制备了3种聚合羟基铁改性蒙脱石(Mt-Fex,x=1,2,3),对比研究了纯蒙脱石(Mt)和Mt-Fexx=1,2,3)的表面性质及吸附Se(Ⅵ)的特性。结果表明,Mt样品的d(001)层间距为1.296nm,在Mt-Fex中升高至1.430nm以上;与Mt样品比较,Mt-Fex的孔体积、表面积、表面分形度均随含铁量的增加而升高,其中微孔体积和微孔表面积的变化尤为明显;Mt样品的等电点(IEP)低于3,而Mt-Fe3的IEP升高至6.8;初始pH=5.0时,Mt和Mt-Fexx=1,2,3)的表面ζ电位分别为-33.5,-11.7,9.9和33.2mV。单吸附位Langmuir模型能够很好地拟合Mt样品对Se(Ⅵ)的等温吸附数据(R2=0.993),4种样品吸附数据的单吸附位Langmuir拟合判断系数(R2)随样品含铁量的增加而降低;3种Mt-Fex样品的吸附数据更适合用双吸附位Langmuir模型拟合(R2=0.993~0.997);Freundlich模型对4种样品的吸附数据拟合度较低(R2=0.849~0.970),其判断系数(R2)随样品含铁量的增加而升高。初始pH=5.0时,Mt和Mt-Fexx=1,2,3)对Se(Ⅵ)的吸附容量分别为4.23,7.83,10.38和14.34mg·g-1。可见,聚合羟基铁含量较高的Mt-Fex样品对土-水体系中Se(Ⅵ)的固定能力明显高于Mt。  相似文献   

8.
采用共沉淀法制备了3种不同含铁量的氧化铁改性蛭石(Verm-Fex,x=5,10,20),研究了纯蛭石(Verm)和Verm-Fex的表面性质及吸附氟的特性。与样品Verm比较,3种Verm-Fex中Verm的d(002)层间距略有升高;Verm-Fex的孔体积、表面积、表面分形度均随含铁量的增加而升高,其中微孔体积和外表面积的增加幅度更明显。4种样品的等电点(IEP)也随含铁量的增加而明显升高;初始pH=5.0时,它们的表面ζ电位分别为-16.4,-6.1,10.5和28.4 mV。4种样品对氟的等温吸附数据用单吸附位Langmuir模型拟合(R2=0.973~0.995)时,Verm的R2最高;双吸附位Langmuir模型可很好地描述3种Verm-Fex样品的等温吸附过程(R2=0.991~0.998);Freundlich模型对4种样品吸附数据的拟合度较差(R2=0.835~0.937),但R2随样品含铁量的增加而略微升高。初始pH=5.0时,Verm和Verm-Fexx=5,10,20)对氟的最大吸附容量(qmax)分别为3.18,6.76,9.27和12.43 mg·g-1。可见,Verm-Fex(尤其含铁量较高的产物)对表生环境中氟的吸附固定性能明显高于Verm。  相似文献   

9.
以结晶氯化铝(AlCl3·6H2O)作为铝源,十二烷基苯磺酸钠(SDBS)为模板剂,采用水热法在硅藻土盘上制备了束状纳米结构γ-AlOOH/Al2O3复合吸附剂。采用XRD、SEM、TEM、TG/DSC、N2吸脱附等对样品进行了表征。研究了样品对133Cs+及Pb2+的吸附能力。研究表明,样品γ-AlOOH/硅藻土、γ-Al2O3/硅藻土对Cs+及Pb2+均具有良好的吸附性能,两者对Cs+的去除率分别为98.9%和99.6%;对Pb2+的最大吸附量分别为357.1、416.7mg·g-1。两种样品对Pb2+的吸附均符合Langmuir吸附模型。  相似文献   

10.
采用改进的水热法成功合成了单分散的纯相锶铁氧体纳米片。借助DLS、XRD、FTIR、SEM、EDS和VSM等分析测试手段对SrFe12O19铁氧体粉体的粒度、结构、形貌和磁性能进行表征。研究结果表明,在240℃保温5 h,物质的量之比nFe3+/nSr2+(RF/S)和nOH-/nNO3-(RO/N)分别为5和2时,所得产物为单分散的纯相六角SrFe12O19铁氧体纳米片。随着RF/SRO/N的变化,合成样品中有少量SrCO3和Fe2O3杂相存在,这主要与反应条件和离子比例有关。磁性能测试结果显示,所得纯相的六角SrF12O19铁氧体纳米片具有优异的磁性能,其饱和磁化强度和矫顽力分别达到60.91 emu·g-1和94.83 kA·m-1,使其在医疗、催化和生物等高技术领域具有潜在的应用。  相似文献   

11.
ZnTi_xFe_(2–x)O_4 and ZnTi_(0.6)Fe_(1.4)O_4/Carbon nanotubes(ZT_(0.6)F_(1.4)/CNTs) composites were prepared by chemical co-precipitation method. The composition, microstructure, magnetic property, adsorption and photocatalytic activity of the prepared samples were characterized by means of modern analytical techniques. The results indicated that ZT_(0.6)F_(1.4)/CNTs composites not only held the original special structure and excellent adsorption properties of CNTs, but also had suitable magnetic property and excellent photocatalytic activity. The removal rate of the samples on Rhodamine B(RhB) depended on the adsorption of CNTs and the photocatalytic degradation of ZT_(0.6)F_(1.4) in the composites. The maximum adsorption amount(q_m) of ZT_(0.6)F_(1.4)/CNTs with the mass ratios of ZT_(0.6)F_(1.4) to CNTs(mZ/C)=1 was up to 17.153 mg g~(–1) for RhB, its adsorption behavior was in accord with Langmuir model, and its photocatalytic degradation activity on RhB had a positive correlation with the content of ZT_(0.6)F_(1.4) in the sample. The experimental results indicate that the total removal rate of composite with mZ/C=1 on RhB was more than 95% and the composite had good decontamination capability on industrial dye wastewater. In addition, the samples can be recovered conveniently, activated easily and had good performance for recycling.  相似文献   

12.
用浸渍法制备了镍铁氧体/碳纳米管(NF/MWNTs)复合材料。用XRD、SEM、TEM、VSM、UV-Vis等表征了样品的组成、结构、形貌、磁性能和吸附性能。结果表明,制备的NF/MWNTs复合材料保留了碳纳米管优良的吸附性能,且具有良好的镍铁氧体负载率和优异的磁性能。质量比(mNF/mMWNTs)为1的NF/MWNTs复合物对亚甲基蓝溶液的最大吸附容量为18.87mg·g-1,其吸附行为符合Langmuir和Freundlich模型。NF/MWNTs复合材料对亚甲基蓝溶液的脱色率与溶液温度和pH值呈正相关性。此外,NF/MWNTs复合材料回收容易,活化处理简便,可重复使用。  相似文献   

13.
用浸渍法制备了镍铁氧体/碳纳米管(NF/MWNTs)复合材料。用XRD、SEM、TEM、VSM、UV-Vis等表征了样品的组成、结构、形貌、磁性能和吸附性能。结果表明,制备的NF/MWNTs复合材料保留了碳纳米管优良的吸附性能,且具有良好的镍铁氧体负载率和优异的磁性能。质量比(mNF/mMWNTs)为1的NF/MWNTs复合材料对亚甲基蓝溶液的最大吸附容量为18.87 mg·g-1,其吸附行为符合Langmuir和Freundlich模型。NF/MWNTs复合材料对亚甲基蓝溶液的脱色率与溶液温度和pH值呈正相关性。此外,NF/MWNTs复合材料回收容易,活化处理简便,可重复使用。  相似文献   

14.
In this paper, the capture of radiocadmium (Cd(II)) by adsorption onto the titanate nanotube/iron oxide (TNT/IOM) magnetic composite as a function of contact time, pH, ionic strength, foreign cation and anion ions, humic acid (HA) and fulvic acid (FA) was studied using batch technique. The results indicated that the adsorption of Cd(II) onto the TNT/IOM magnetic composite was dependent on ionic strength at pH <9.0, but was independent of ionic strength at pH >9.0. Outer-sphere surface complexation were the main mechanism of Cd(II) adsorption onto the TNT/IOM magnetic composite at low pH values, whereas the adsorption was mainly dominated via inner-sphere surface complexation at high pH values. The adsorption of Cd(II) onto the TNT/IOM magnetic composite was dependent on foreign cation and anion ions at low pH values, but was independent of foreign cation and anion ions at high pH values. A positive effect of HA/FA on Cd(II) adsorption onto the TNT/IOM magnetic composite was found at low pH values, while a negative effect was observed at high pH values. From the results of Cd(II) removal by the TNT/IOM magnetic composite, the optimum reaction conditions can be obtained for the maximum removal of Cd(II) from water. It is clear that the best pH values of the system to remove Cd(II) from solution by using the TNT/IOM magnetic composite are 7.0–8.0. Considering the low cost and effective disposal of Cd(II)-contaminated wastewaters, the best condition for Cd(II) capture by the TNT/IOM magnetic composite is at room temperature and solid content of 0.5 g L?1. These results are quite important for estimating and optimizing the removal of Cd(II) and related metal ions by the TNT-based magnetic composite.  相似文献   

15.
In this study, the removal of nitrate using ZnO, MgO, and CeO2 nanoparticles (NPs) modified by humic acid from water was tested. Nanoparticles were modified by humic acid using the microwave-assisted technique and then modified ZnO (Zn–H), modified MgO (Mg–H), and modified CeO2 (Ce–H) were characterized through SEM, EDX, FTIR, and XRD analysis. Several important parameters influencing the removal of nitrate such as contact time, pH, adsorbent dosage and temperature were explored systematically by batch experiments. Isotherm studies were set up with the following optimum conditions: pH?=?5, adsorbent concentration of 1 g L?1, 180 min and 25 °C. The results revealed that the adsorption were best fitted to pseudo-second order and simple Elovich kinetics models. Langmuir, Freundlich and linear adsorption models were fitted to describe adsorption isotherms and constants. The isotherm analysis indicated that the adsorption data can be represented by both Freundlich and linear isotherm models. The maximum adsorption capacity (qm) was obtained at 55.1, 74.2 and 75.8 mg g?1 for Zn–H, Ce–H, and Mg–H, respectively. The thermodynamic parameters such as free energy, enthalpy and entropy of adsorption were obtained. From the thermodynamic parameters, it is suggested that the adsorption of nitrate on modified NPs (MNPs) followed the exothermic and spontaneous processes. The obtained results showed that the MNPs were efficient adsorbents for removing nitrate from aqueous media.  相似文献   

16.
通过γ-氯丙基三甲氧基硅烷的偶联, 将聚乙烯亚胺(PEI)偶合接枝在硅胶微粒表面, 制得了对脲酸有强吸附性能的复合型医用吸附材料PEI/SiO2. 静态吸附实验结果表明, 凭借强烈的氢键相互作用, 硅胶表面的聚胺大分子PEI对脲酸的互变异构体三羟基嘌呤具有很强的吸附能力, 等温吸附满足Freundlich吸附方程, 饱和吸附量可达84.9 mg/g; 介质的pH值对吸附作用有很大的影响, 在中性溶液中(pH=6~7), 复合吸附材料PEI/SiO2对脲酸具有强吸附能力, 而在酸性与碱性溶液中吸附能力都较弱; 温度对吸附性能也有影响, 升高温度吸附量增大.  相似文献   

17.
The photocatalytic degradation of natural organic matter (NOM) would be an attractive option in the treatment of drinking water. The performance of a submerged photocatalytic membrane reactor (PMR) was investigated with regard to the removal of NOM and the control of membrane fouling. In particular, this work focused on the adsorption and desorption of humic acids (HA) and lake water NOM at the surface of TiO2 photocatalyts and ferrihydrite (FH) adsorbents in the PMR for water treatment. The addition of FH particles with a large sorption capacity helped remove the NOM released from TiO2 particles, but FH suspended in water affected the photocatalysis of lake water NOM with a low specific UV absorbance (SUVA) value. To prevent the UV light being scattered by FH without any photocatalytic activity, FH particles were attached to a submerged microfiltration (MF) membrane, which contributed to a greater removal of NOM during long-term PMR operation. The further removal of NOM from aqueous solution was achieved due to the synergistic effect of TiO2 photocatalysis and FH adsorption in PMR while minimizing the influence of photoinduced desorption of NOM. No significant membrane fouling occurred when the submerged PMR was operated even at high flux levels (>25 L/m2 h), as long as photocatalytic decomposition took place.  相似文献   

18.
Advanced oxidation processes (AOPs) counting heterogeneous photocatalysis has confirmed as one of the preeminent method for waste water remediation. In the present work, we have successfully fabricated novel visible-light-driven nitrogen-doped graphene (NG) supported magnetic ZnO/ZnFe2O4 (ZnO/ZF/NG) and ZnO/CoFe2O4 (ZnO/CF/NG) nanocomposites. ZnO synthesized via direct precipitation method. Hydrothermal method was used for the preparation of nitrogen-doped graphene supported magnetic ZnO/ZF (ZnO/ZnFe2O4) and ZnO/CF (ZnO/CoFe2O4) nanocomposites. The procured materials were scrutinized by assorted characterizations to acquire information on their chemical composition, crystalline structure and photosensitive properties. The absorption and photocatalytic performance of photocatalysts were studied via UV–Visible spectra. Photodegradation performance of the synthesized nanocomposites was estimated toward mineralization of methyl orange (MO) and malachite green (MG) dyes in aqueous solution. The high surface area of ZnO/ZF/NG and ZnO/CF/NG was suitable for adsorptive removal of MO and MG dyes. The photodegradation performance of heterojunction photocatalysts was superior to bare photocatalyst in 140 min under visible-light irradiation. Spectrophotometer, GC–MS (Gas chromatography–mass spectrometry) elucidation was carried out to expose the possible intermediates formed. Both ZnO/ZF/NG and ZnO/CF/NG were rapidly isolated from the aqueous phase by applying an external magnetic field in 20 sec and 2 min, respectively. The photocatalytic performance and stability of ZnO/ZF/NG and ZnO/CF/NG nanocomposites were confirmed by conducting 10 consecutive regeneration cycles. Owing to recyclability of ZnO/ZF/NG and ZnO/CF/NG, these heterogeneous nanocomposites might be used as cost-effective for treatment of discarded water. The observations endorse that the synthesized ternary heterogeneous nanocomposites facilitates wastewater decontamination using photocatalytic technology.  相似文献   

19.
The objective of this study was to evaluate the performance of a photocatalysis/H2O2/metal membrane hybrid system in the degradation of humic acid. A metal membrane of nominal pore size 0.5 μm was used in the experiment for separation of TiO2 particles. Hydrogen peroxide was tested as an oxidant. The efficiency of removal of CODCr and color increased rapidly for initial hydrogen peroxide concentrations up to 50 mg L−1. The efficiency of removal of CODCr and color by 50 mg L−1 initial hydrogen peroxide concentration was approximately 95 and 98%, respectively. However, addition of hydrogen peroxide over 50 mg L−1 inhibited the efficiency of the system. Addition of hydrogen peroxide to a UV/TiO2 system enhanced efficiency of removal of CODCr and color compared with no addition of hydrogen peroxide. This may be ascribed to capture electrons ejected from TiO2 and to the production of OH radicals. Application of the metal membrane in the UV/TiO2/H2O2 system enhanced the efficiency of removal of CODCr and color because of adsorption by the metal membrane surface and the production of OH radicals. By application of a metal membrane with a nominal pore size of 0.5 μm, TiO2 particles were effectively separated from the treated water by metal membrane rejection. The photocatalytic metal membrane had much less resistance than the humic acid, TiO2, and humic acid/TiO2 because of the degradation of humic acid by the photocatalytic reaction.  相似文献   

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