硫化钠改性活性炭对Pb(Ⅱ)的吸附性能研究

采用质量分数为3%的Na_2S溶液对活性炭浸渍,在600℃以N_2作为保护气对其进行高温处理,研究Na_2S改性活性炭(SAC)吸附Pb(Ⅱ)的动力学和热力学机理,并对吸附Pb(Ⅱ)前后的改性活性炭进行了表征和分析。结果表明,与改性前活性炭相比,SAC的比表面积和总孔容减小,S元素含量显著提高。SAC对Pb(Ⅱ)的吸附效果显著提高,在Pb(Ⅱ)初始浓度为300mg/L时,SAC对Pb(Ⅱ)最大吸附量为122.56mg/g,并且在吸附过程的前80min内可达到总吸附量的95%以上。SAC对Pb(Ⅱ)的吸附过程可用Langmuir模型描述,动力学特性符合拟二级动力学模型。SAC对Pb(Ⅱ)的吸附的热力学参数ΔG在-80~-20k J/mol之间,ΔH0,ΔS0,表明吸附是自发进行的物理吸附与化学吸附共同作用的放热过程。对吸附前后改性活性炭的傅里叶变换红外谱图分析表明,经过Na_2S改性后,活性炭表面引入了砜基,并且砜基强化了改性活性炭对Pb(Ⅱ)的吸附性能。     

生物质基炭膜电吸附去除水中Pb(Ⅱ)的研究

利用二层牛皮为原料,经炭化、硝酸氧化和水蒸气活化制备改性生物质基炭膜。采用比表面积及孔径分析仪、傅里叶红外光谱技术(FT-IR)、Boehm滴定法对生物质基炭膜的物理化学特性进行表征。以生物质基炭膜为电极材料,采用电吸附去除废水中Pb(Ⅱ),分别研究电压、电极板间距、初始Pb(Ⅱ)浓度对吸附效果的影响。结果表明,经硝酸氧化和水蒸气活化后的炭膜,其比表面积、总孔体积及含氧官能团均明显增加。改性后生物质基炭膜电极对Pb(Ⅱ)的去除率是未改性生物质基炭膜电极的3.87倍,在电压3V,Pb(Ⅱ)初始浓度50mg/L,电极板间距25mm电吸附条件下,Pb(Ⅱ)去除率为46.53%,吸附容量为48.08mg/g。该炭膜能够再生和重复利用,但是炭膜稳定性还需进一步改进。电吸附过程符合准一级动力学模型。     

在多孔有机聚合物中构筑广谱性重金属离子吸附活性位

以三维刚性结构的三蝶烯为单体, 通过简单的Friedel-Crafts烷基化反应制备得到高比表面积的三蝶烯基多孔有机聚合物(TPOP), 在TPOP中接枝乙二胺和氯乙酸钠, 构建了广谱重金属离子吸附剂(TPOP-CH₂EDTA). 获得的TPOP-CH₂EDTA具有微孔/介孔结构, 其微孔尺寸为1.6 nm, BET比表面积为634 m²/g, 利于重金属离子传递和配位作用的强化. TPOP-CH₂EDTA对重金属离子具有吸附广谱性, 其对Ag(Ⅰ), Cu(Ⅱ), Ni(Ⅱ), Zn(Ⅱ), Co(Ⅱ), Sn(Ⅳ), Pb(Ⅱ), Cd(Ⅱ), Fe(Ⅲ)和Cr(Ⅲ)等10种重金属离子的去除率均高于98%. 以Pb(Ⅱ)为典型的重金属污染物, 通过Langmuir模型计算得到Pb(Ⅱ)的最大吸附容量高达184.5 mg/g; 具有拟二级吸附动力学特征, 吸附速率快, 动力学常数k₂为0.0173 g·mg^?1·min^?1; 经过5次循环使用后, Pb(Ⅱ)的去除效率仍高达95.8%. TPOP-CH₂EDTA对混合溶液中Pb(Ⅱ)和Cu(Ⅱ)的去除率均高于99%, 且对含有大量无机盐[如Ca(Ⅱ), Mg(Ⅱ), K(Ⅰ)和Na(Ⅰ)离子]和有机化合物的复杂真实水体系, Pb(Ⅱ)和Cu(Ⅱ)的去除效率仍高于90%. 因此, 通过调控多孔有机聚合物微观结构(如比表面积、 孔径和吸附位点密度)而构筑的广谱性重金属吸附材料, 为协同去除复杂水系统中混合重金属离子提供了方案.     

K_2CO_3活化糖蜜基多孔炭的制备及双电层储能性能

以生物质糖蜜为原料,K_2CO_3为活化剂制备了糖蜜基多孔炭.K_2CO_3的使用改善了传统活化剂KOH对设备腐蚀的问题,避免了传统活化剂ZnCl_2可能引发的致毒性.分析了活化条件对产率的影响.采用扫描电子显微镜(SEM)、X射线衍射(XRD)、N_2吸附-脱附分析(BET)和傅里叶变换红外光谱(FTIR)表征了糖蜜基多孔炭,结果表明其为石墨化层堆结构,表面富含羟基、羧基、酯基或醚基等官能团,具有丰富的孔结构,比表面积可达1219 m~2/g,并证实了800℃为最佳的活化温度.电化学测试结果表明,糖蜜基多孔炭具有优良的双电层储能性能.     

低成本木质素吸附剂对废水中Pb2+吸附性能的研究

首次尝试以马尾松为原料的木质素制备低成本重金属吸附剂,采用N2物理吸附和红外漫反射技术对其结构和表面化学进行了表征,研究了pH值,温度对其吸附水溶液中Pb2 的影响,并与麦草木质素和商业活性炭进行了对比,探讨了它吸附重金属离子的吸附机理以及结构和表面化学对重金属离子吸附的影响。结果表明,马尾松木质素吸附剂对水溶液中Pb2 的吸附机理主要是化学吸附,其表面的功能基有利于吸附水溶液中Pb2 ,尽管商业活性炭的比表面积是马尾松碱木素的200多倍,在相同的实验条件下,所制备的马尾松碱木素对Pb2 的单位比表面积平衡吸附量却是商业活性炭的1000多倍。     

壳聚糖交联不溶性腐殖酸吸附剂的制备及其吸附性能

以壳聚糖和不溶性腐殖酸为原料,采用滴加成球法制备了一种新型重金属离子吸附剂——壳聚糖交联不溶性腐殖酸,对其进行了物理性质测定及FT-IR、SEM等分析。研究了吸附剂对水溶液中Pb(Ⅱ)的吸附特征。吸附等温线分别以Freundlich和Langmuir方程进行拟合,结果显示,吸附的最佳模型为Freundlich吸附模型。利用该方程拟合的数据,由Clausius-Claperyon’s方程计算出的Pb(Ⅱ)吸附焓变值,说明吸附剂对Pb(Ⅱ)的吸附以化学吸附为主。利用吸附剂吸附Pb(Ⅱ)前后的XPS分析了吸附机理,同时考察了温度、p H值及吸附时间对吸附效果的影响。结果表明,随着温度的升高和pH值的增大,吸附剂对Pb(Ⅱ)的吸附量增加,而且吸附更符合准二级动力学模型。     

活性炭吸附及离子交换富集分离-分光光度法测定水中痕量银

建立了用活性炭对水中痕量银进行预富集的新方法。结果表明,pH=1.0时,活性炭能对水中被抗坏血酸还原后的痕量银进行吸附富集,而Cu(Ⅱ)、Fe(Ⅲ)、Co(Ⅱ)、Ni(Ⅱ)、Pb(Ⅱ)、Zn(Ⅱ)、Mn(Ⅱ)、Al(Ⅲ)、Bi(Ⅲ)和Sb(Ⅲ)等常见阳离子不被吸附,用K2S2O8将吸附在活性炭上的单质银氧化解脱后,用Mg(NO3)2辅助置换洗脱,可用分光光度法测定。该法在8～50μg/L银(Ⅰ)范围内加标回收率为93.2～97.1%。同时还研究了活性炭对银的吸附行为,提出了活性炭表面上被氧化的Ag(Ⅰ)和Mg(Ⅱ)有离子交换作用。应用该法测定自来水中痕量银,结果令人满意。     

炭化玉米秸秆对水中Pb(Ⅱ)的去除行为研究

以炭化玉米秸秆(CCS)为吸附剂去除水中Pb(Ⅱ),研究反应过程的动力学特性和等温线方程,考察溶液pH值和反应温度对Pb(Ⅱ)去除的影响,分析CCS的解吸行为。结果表明:吸附过程更好地符合准二级动力学方程和Langmuir等温线方程,拟合系数R2分别为0.9972和0.9959;由Langmuir方程计算可知,CCS对Pb(Ⅱ)的理论最大吸附量qm为30.3030mg/g。反应过程自发、吸热,反应后体系自由度略有增加。Pb(Ⅱ)去除的最适pH值为6,对于浓度为40mg/L、体积为100mL的Pb(Ⅱ)溶液,使用0.1g CCS能去除水中63.53%的Pb(Ⅱ)。反应温度对Pb(Ⅱ)去除效果的影响很小。蒸馏水和HCl都能实现Pb(Ⅱ)的有效解吸,再生后的CCS对Pb(Ⅱ)仍能取得15.69mg/g的二次吸附量。     

磁性氧化石墨烯/MIL-101(Cr)表面金属离子印迹聚合物制备及其对Cu(Ⅱ)和Pb(Ⅱ)选择性吸附

本文以磁性氧化石墨烯/MIL-101(Cr)复合材料为载体,以Cu(Ⅱ)和Pb(Ⅱ)模板,多巴胺(DA)为功能单体,采用表面印迹技术成功制备一种对Cu(Ⅱ)和Pb(Ⅱ)具有高选择吸附性能的磁性离子印迹聚合物。 采用傅里叶变换红外光谱、扫描电子显微镜和振动样品磁强计等技术对该磁性离子印迹聚合物的形貌、粒径大小和磁性能进行表征。 详细探讨了该磁性离子印迹聚合物对Cu(Ⅱ)和Pb(Ⅱ)的吸附动力学、等温吸附性能及吸附选择性,结果表明该磁性离子印迹聚合物对Cu(Ⅱ)和Pb(Ⅱ)最大吸附量分别为144.92和322.58 mg/g。 优化了磁固相萃取条件,该磁性离子印迹聚合物成功用于水样中微量Cu(Ⅱ)和Pb(Ⅱ)的分离和检测,Cu(Ⅱ)和Pb(Ⅱ)的回收率分别为81.99%~89.91%和81.24%~95.15%。     

硫酸体系中P507浸渍树脂吸附Cd(Ⅱ)的研究

选用2-乙基已基膦酸单(2-乙基已基)酯(P507)为萃取剂,HZ818大孔树脂为载体,以干法浸渍技术制备了P507浸渍树脂.研究了吸附平衡时间、溶液pH和树脂用量对硫酸体系中该浸渍树脂吸附Cd(Ⅱ)的影响.静态吸附实验表明,吸附过程符合准二级动力学模型.采用0.5mol/L的盐酸溶液可将吸附在树脂上的Cd(Ⅱ)洗脱下来.     

Preparation of Ag-MnFe2O4-bentonite Magnetic Composite for Pb(Ⅱ)/Cd(Ⅱ) Adsorption Removal and Bacterial Inactivation in Wastewater

An Ag-MnFe₂O₄-bentonite composite was synthesized by a chemical co-precipitation method and used for adsorption removal of Pb(Ⅱ), Cd(Ⅱ) and disinfection. The result of X-ray diffraction indicate that the diffraction peaks of MnFe₂O₄ and Ag can be perfectly indexed to the cubic spinel MnFe₂O₄(JCPDS No.88-1965) and metallic Ag(JCPDS No.41-1402), respectively. The results of scanning electron microscopy and energy dispersive X-ray spectroscopy manifest the deposition of MnFe₂O₄ and Ag on the bentonite surface and the presence of Mn, Fe and Ag. The result of X-ray photoelectron spectroscopy displayed that the composition of Ag-MnFe₂O₄-bentonite was Mn(Ⅱ), Fe(ⅡI) and metallic Ag. The analysis of Brunauer-Emmett-Teller showed that the specific surface area of Ag-MnFe₂O₄-bentonite was the largest compared with that of bentonite, MnFe₂O₄ and MnFe₂O₄-bentonite. Thermodynamic studies revealed that the adsorption of Pb(Ⅱ) and Cd(Ⅱ) ions was spontaneous and endothermic. Langmuir model showed an adsorption capacity of 129.87 mg/g for Pb(Ⅱ) and 48.31 mg/g for Cd(Ⅱ) ions. The adsorption kinetics of Pb(Ⅱ) and Cd(Ⅱ) ions onto Ag-MnFe₂O₄-bentonite can be best described by a pseudo-second-order model. The adsorption rate constant of the pseudo-second-order model was 0.0019 g·mg^-1·min^-1 for Pb(Ⅱ) and 0.0065 g·mg^-1·min^-1 for Cd(Ⅱ) ions. In addition to the adsorption experiment, the antibacterial properties of Ag-MnFe₂O₄-bentonite were studied through plate count method. Gram-negative(G-) bacteria Escherichia coli and Gram-positive(G+) bacteria Lactobacillus plantarum were used to test the antibacterial properties. The results showed that the composite demonstrated excellent antibacterial activity. Thus, Ag-MnFe₂O₄-bentonite can be employed as an adsorbent as well as an antimicrobial agent.     

Pb (II) removal from aqueous media by EDTA-modified mesoporous silica SBA-15

An organic-inorganic hybrid mesoporous silica material was synthesized by two-step post-grafting method of SBA-15 with 3-aminopropyltrimethoxy-silane (APTES) and thionyl dichloride (SOCl(2)) activated ethylenediaminetetraacetic acid (EDTA) in sequence and measured by means of Fourier transform infrared spectroscopy (FT-IR), X-ray diffraction (XRD), elemental analysis (EA), transmission electron microscopy (TEM), nitrogen (N(2)) adsorption-desorption analysis and back titration. The material was found having the beneficial properties of mesoporous silica SBA-15 and EDTA. Adsorption potential of the material for Pb (II) removal from aqueous solution was investigated by varying experimental conditions such as pH, contact time and initial metal concentration. The removal efficiency of Pb(2+) was high under studied experimental conditions. The adsorption equilibrium could be reached within 20min and the kinetic data were fitted well by pseudo-second-order and intraparticle diffusion model. The adsorbent exhibited a favorable performance and its maximum adsorption capacity calculated by the Langmuir model was 273.2mgg(-1). Recycling experiments showed the adsorbent could be regenerated by acid treatment without altering its properties. The chemical states of the elements involved in the adsorption were analyzed by X-ray photoelectron spectroscopy (XPS). The results demonstrated that the adsorption mechanism of the material involved Na Pb ion-exchange and carboxyl group dominated surface complexation.     

Adsorbents based on carbon microfibers and carbon nanofibers for the removal of phenol and lead from water

This paper describes the production, characteristics, and efficacy of carbon microfibers and carbon nanofibers for the removal of phenol and Pb(2+) from water by adsorption. The first adsorbent produced in the current investigation contained the ammonia (NH(3)) functionalized micron-sized activated carbon fibers (ACF). Alternatively, the second adsorbent consisted of a multiscale web of ACF/CNF, which was prepared by growing carbon nanofibers (CNFs) on activated ACFs via catalytic chemical vapor deposition (CVD) and sonication, which was conducted to remove catalytic particles from the CNF tips and open the pores of the CNFs. The two adsorbents prepared in the present study, ACF and ACF/CNF, were characterized by several analytical techniques, including SEM-EDX and FT-IR. Moreover, the chemical composition, BET surface area, and pore-size distribution of the materials were determined. The hierarchal web of carbon microfibers and nanofibers displayed a greater adsorption capacity for Pb(2+) than ACF. Interestingly, the adsorption capacity of ammonia (NH(3)) functionalized ACFs for phenol was somewhat larger than that of the multiscale ACF/CNF web. Difference in the adsorption capacity of the adsorbents was attributed to differences in the size of the solutes and their reactivity towards ACF and ACF/CNF. The results indicated that ACF-based materials were efficient adsorbents for the removal of inorganic and organic solutes from wastewater.     

Preparation and characterization of activated carbon from <Emphasis Type="Italic">Amygdalus Scoparia</Emphasis> shell by chemical activation and its application for removal of lead from aqueous solutions

Two series of activated carbon have been prepared by chemical activation of Amygdalus Scoparia shell with phosphoric acid or zinc chloride for the removal of Pb(II) ions from aqueous solutions. Several methods were employed to characterize the active carbon produced. The surface area was calculated using the standard Brunauer-Emmet-Teller method. The microstructures of the resultant activated carbon were observed by scanning electron microscopy. The chemical composition of the surface resultant activated carbon was determined by Fourier transform infrared spectroscopy. In the batch tests, the effect of pH, initial concentration, and contact time on the adsorption were studied. The data were fitted with Langmuir and Freundlich equations to describe the equilibrium isotherms. The maximum adsorption capacity of Pb(II) on the resultant activated carbon was 36.63 mg g⁻¹ with H₃PO₄ and 28.74 mg g⁻¹ with ZnCl₂. To regenerate the spent adsorbents, desorption experiments were performed using 0.25 mol L⁻¹ HCl. Here we propose that the activated carbon produced from Amygdalus Scoparia shell is an alternative low-cost adsorbent for Pb(II) adsorption.     

ZIF-8吸附剂上CH4/N2的吸附分离性能与热力学性质

将沸石咪唑酯骨架结构材料应用于抽放煤层甲烷的浓缩净化研究。以三乙胺(TEA)为导向剂,ZnSO₄为金属离子源,水为溶剂,采用水热合成法进行了ZIF-8吸附剂的制备。采用XRD、物理吸附、动态吸附分离和反相气相色谱(IGC)等方法对ZIF-8的物理结构、化学稳定性、吸附分离性能和热力学性质进行了研究。结果表明,ZIF-8具有良好的化学稳定性,能够在强酸、强碱和强极性的溶剂中保持结构的稳定性;在298 K时,ZIF-8对CH₄/N₂的分离因子达到3.4,与活性炭相当,但CH₄、N₂在ZIF-8上的吸附热比在活性炭上低20%左右。     

离子印迹法制备对铜离子(Ⅱ)选择性吸附的碳基材料

通过钨离子印记方法,合成了对铜离子有高选择性吸附性能的碳基材料。 在四乙烯五胺(TEPA)、钨酸铵和葡萄糖摩尔比为1:1:5条件下,经水热法合成的碳基吸附材料能有效地吸附铜离子,对铜离子吸附的最佳pH=5。 在Cd²⁺、Co²⁺、Cu²⁺、Ni²⁺和Zn²⁺摩尔浓度相近体系中,离子印记碳基吸附材料对铜离子的吸附率高达97.2%,而对Cd²⁺、Co²⁺、Ni²⁺、Zn²⁺吸附率分别为20.1%、9.63%、20.3%、13.3%,表明这种离子印记碳基吸附材料对Cu²⁺具有非常优异的选择吸附能力。     

Adsorption of Pb(II) and Ni(II) From Aqueous Solution by a High-Capacity Industrial Sewage Sludge-Based Adsorbent

In the present study, adsorption of Ni(II) and Pb(II) from aqueous solution was investigated using activated carbon synthesized with industrial wastewater sludge. The synthesized adsorbent was analyzed using nitrogen adsorption–desorption and Fourier transfer infrared (FTIR) techniques. Batch adsorption mode was used to evaluate the effect of solution pH, contact time, adsorbent dose, initial metal ion concentration, and temperature on the adsorption capacity of the synthesized adsorbent. The kinetic data were analyzed using different kinetic models. The pseudo-second-order equation gave the best fit to the experimental data for both metal ions. The equilibrium isotherm data were analyzed using the Langmuir, Freundlich, and Dubinin–Radushkevich (D–R) isotherm models. The results showed that the data obtained for the Ni(II) and Pb(II) adsorption are in good agreement with the Langmuir model. The Langmuir mono-layer maximum adsorption capacities for Ni(II) and Pb(II) ions were estimated to be 74.06 and 88.76 mg g^?1 at 25°C, respectively. In addition, the thermodynamic studies proved that the adsorption process of both metals could be considered endothermic.     

磁性纳米粒子富集-电感耦合等离子体发射光谱法测定食具中铬、镍、镉、铅、砷的迁移量

采用氩电弧等离子体法制备磁性碳包铁纳米粒子,考察了其对水溶液中Cr,Ni,Cd,Pb和As的富集能力,建立电感耦合等离子体原子发射光谱同时测定食具中Cr,Ni,Cd,Pb和As迁移量的分析方法。研究了纳米粒子表面经H2O2处理后,pH值、吸附时间、吸附剂用量等因素对各元素富集效率的影响。结果表明,H2O2表面处理可有效提高纳米粒子对待检元素的吸附率。在pH 8.0～9.5范围内,选用30 mg碳包铁纳米粒子定量富集,振荡3 min后,Cr,Ni,Cd,Pb和As均可被磁性碳包铁纳米粒子定量富集,酸性溶液(pH 1～2)可洗脱吸附离子。采用本方法测定了实际样品,各元素回收率在87%～106%之间。