一种PAN基偕胺肟螯合纤维对重金属离子的吸附性能

利用有限浴技术对一种PAN基偕胺肟螯合纤维的吸附性能进行了系统研究。结果表明:由于该功能纤维材料含胺肟及多烯多胺双重功能基,因此对Cu2+、Ni2+、Co2+、Hg2+等重金属离子具有很好吸附性能。交联型偕胺肟螯合纤维物理化学性能良好,洗脱再生简便,可望用于湿法冶金及重金属离子工业废水的资源化治理等领域。     

水杨酸型螯合吸附材料对重金属离子的吸附性能

将5-氨基水杨酸接枝到PGMA/SiO2微粒的聚甲基丙烯酸缩水甘油酯(PGMA)大分子链上,成功制备了一种新型螯合吸附材料ASA-PGMA/SiO2。采用静态法研究了ASA-PGMA/SiO2对重金属离子Cu2+、Cd2+、Zn2+、Pb2+的吸附性能,结果表明其对Cu2+、Cd2+、Zn2+、Pb2+具有很强的螯合吸附能力,吸附容量分别可以达到0.42、0.40、0.35、0.31mmol/g。体系的pH对吸附容量影响较大,吸附行为服从Langmuir和Freundlich吸附模型。使用0.1mol/L的盐酸溶液就可实现重金属离子的解吸。通过反复吸附-解吸实验证明ASA-PGMA/SiO2具有良好的重复使用性能。     

螯合纤维的研究：Ⅱ.含偕胺肟基螯合纤维的吸附性能

本文系统地研究了通过枝共聚和偕胺肟化反应制备的以聚乙烯醇缩甲醛（ＰＶＦ）无纺布为基体的含偕胺肟基螯合纤维对碱土，过渡贵重，稀土和放射性金属离子的螯合吸附行为，测定了在不同温度下的吸附速率曲线。并且首次发现这种螯合基团有氧化－还原性性质，能将高价金属离子如Ａｕ＾３＾＋还原成价态，即还原成元素金。     

含偕胺肟基螯合纤维吸附，还原Au^3＋的研究（Ⅰ）：—含偕胺肟基螯合纤维对Au^3＋的吸附行为

研究了含偕胺肟基螯合纤维对Au^3 的吸附特征及影响吸附量的因素，结果表明，含偕胺肟基螯合纤维对Au^3 的吸附是极高，而且将所吸附的Au^3＋还原成单质金；在含Au^3 ,Cu^2 ,Zn^2 和Cr^3 的溶液中，对Au^3 具有相当高的吸附选择性，提高偕胺肟基在螯合纤维中的含量及吸附温度和Au^3 的初始度等均有利于提高吸附量。     

亚氨二乙酸型复合材料IDAA-PGMA/SiO2对重金属及稀土离子的吸附行为与吸附热力学

将甲基丙烯酸缩水甘油酯(GMA)接枝于硅胶微粒表面,制得了接枝微粒PGMA/SiO₂; 使亚氨二乙酸(IDAA)与接枝PGMA的环氧基团发生开环反应, 从而将亚氨二乙酸基团引入接枝微粒表面, 制得了复合螯合微粒材料IDAA-PGMA/SiO₂. 本文研究了IDAA-PGMA/SiO₂对重金属及稀土离子的螯合吸附行为, 深入地研究了吸附机理与吸附热力学. 研究结果表明: 凭借亚氨二乙酸基团与重金属离子之间的静电作用与配位螯合作用的协同, 复合微粒材料IDAA-PGMA/SiO₂对重金属离子可产生强的螯合吸附作用, 尤其对Pb²⁺离子表现出很强的螯合吸附能力, 常温下吸附容量可达0.235 g·g^-1; IDAA-PGMA/SiO₂对重金属离子的吸附过程为一放热过程, 且为焓驱动的过程, 升高温度, 吸附容量降低; 对稀土离子的吸附过程则为熵驱动的过程; 在可抑制金属离子水解的pH范围内, 介质的pH值越高, IDAA-PGMA/SiO₂的螯合吸附能力越强; IDAA-PGMA/SiO₂对重金属离子的吸附容量远高于对稀土离子的吸附容量.     

偕胺肟螯合纤维的合成及对矿液中金的吸附性能研究

螯合离子交换纤维在吸附金属离子时具有选择性高、吸附速度快、易解脱和容易再生等优点[1 4]。本文制备了一偕胺肟螯合纤维,测定了它的机械性能及对模拟金矿液和实际金矿液(水氯法)中金的静、动态吸附性能,考察了共存离子浓度高于实际矿液中浓度几倍至几十倍时对金的吸附选择性。对实际金矿液静态饱和吸附为58 5mg/g,在流速为每分钟1 5个柱床体积的动态实验中,当吸附容量在29 2mg/g以下时,动态吸净率保持在73%以上。1　实验部分1 1　仪器和试剂INSTRON 4465型万能材料试验机(温度为60℃,湿度为60%,拉伸速度为10 00mm/min,计算机采点…     

复合型螯合吸附材料PEI/SiO2对铜离子吸附性能的研究

通过γ-氯丙基三甲氧基硅烷的媒介, 将聚乙烯亚胺(PEI)偶联接枝到硅胶微粒表面, 制备了复合型螯合吸附材料PEI/SiO2;研究了PEI/SiO2对Cu2 的吸附性能. 复合型螯合吸附材料PEI/SiO2对Cu2 具有强的螯合吸附能力;等温吸附数据符合Langmuir方程, 且吸附量随温度升高而增大;pH对吸附量有很大的影响, pH 7时, 吸附量最高.     

聚丙烯胺肟螯合纤维的合成及其对铜（Ⅱ）离子的吸附

利用预辐照接枝法合成了聚丙烯胺肟螯合纤维，研究了影响接枝率，胺肟基团含量及离子吸附的因素，该纤维对铜的离子的吸附容量达０．６７ｍｍｏｌ／ｇ干纤维。     

螯合纤维的研究.Ⅰ.含偕胺肟基螯合纤维的制备

本文系统地研究了以聚乙烯醇缩甲醛(PVF)无纺布为基体,通过化学引发丙烯腈(AN)在PVF上的接枝共聚反应制备反应性纤维时各种因素如用KMnO_4引发剂预氧化PVF时其溶液的浓度、预氧化温度、时间、接枝共聚反应温度、时间、单体浓度、反应介质的酸度等对接枝率和接枝效率的影响,同时还研究了反应性纤维进行偕胺肟化反应时影响其反应程度的各种因素,如反应介质、温度、时间等的影响。     

Synthesis of thiol chelating resins and their adsorption properties toward heavy metal ions

A series of chelating resins, derived from a macroreticular styrene-divinylbenzene (2%) copolymer beads grafted with various poly(ethylene glycols) HO? (? CH₂? CH₂? O? )_n? H(n = 0, 4, 9, 13) and containing thiol groups as chelating functions, have been synthesized in a three-step reaction sequence. The structure of the functionalized resins was confirmed by IR spectrophotometry, elemental analysis, and differential scanning calorimetry. The complexation behavior of these thiol resins was investigated towards Hg(II), Cu(II), and Pb(II) ions in aqueous solution by a batch equilibration technique. The influence of pH on adsorption capacity was also examined. The adsorption values for metal ions' intake followed the order Hg(II) > Cu(II) > Pb(II). The affinity of these polymers towards Hg(II) ions was so high that the total mercury level in the liquid decreased from 20 ppm to below 10 ppb after 2 h of treatment. Polymers can be regenerated by washing with a solution of hydrochloric acid (6N) and 10% by weight of an aqueous solution of thiourea. © 1994 John Wiley & Sons, Inc.     

Dynamic adsorption and desorption of heavy metal ions on poly(acrylaminophosphonic-carboxyl-hydrazide) chelating fiber

The dynamic adsorption and desorption properties, including the effect of pH value and flow rate on the adsorption, eluent acidity and volume, eluting velocity and re-use, of Cu(II), Pb(II), Zn(II), Cd(II), Mn(II), Ni(II), Co(II) and Hg(II) ions on the column loaded with poly(acrylaminophosphonic-carboxyl-hydrazide) chelating fiber were investigated. The recovery of Mn(II), Co(II), Cd(II), Ni(II) and Zn(II) ions in the presence of Na, K, Ca and Mg ions was examined. The preconcentration of trace amounts of Mn(II), Co(II), Cd(II), Ni(II) and Zn(II) ions from model solution samples was carried out with satisfactory results. The amount of the metal ions detected after preconcentration and recovery by this technique was basically in agreement with the added amount. The method is rapid, precise and simple. Received: 15 October 1997 / Revised: 17 March 1998 / Accepted: 20 March 1998     

Dynamic adsorption and desorption of heavy metal ions on poly(acrylaminophosphonic-carboxyl-hydrazide) chelating fiber

The dynamic adsorption and desorption properties, including the effect of pH value and flow rate on the adsorption, eluent acidity and volume, eluting velocity and re-use, of Cu(II), Pb(II), Zn(II), Cd(II), Mn(II), Ni(II), Co(II) and Hg(II) ions on the column loaded with poly(acrylaminophosphonic-carboxyl-hydrazide) chelating fiber were investigated. The recovery of Mn(II), Co(II), Cd(II), Ni(II) and Zn(II) ions in the presence of Na, K, Ca and Mg ions was examined. The preconcentration of trace amounts of Mn(II), Co(II), Cd(II), Ni(II) and Zn(II) ions from model solution samples was carried out with satisfactory results. The amount of the metal ions detected after preconcentration and recovery by this technique was basically in agreement with the added amount. The method is rapid, precise and simple. Received: 15 October 1997 / Revised: 17 March 1998 / Accepted: 20 March 1998     

Concentration of heavy metal ions in water using thermoresponsive chelating polymer

Thermoresponsive polymers, poly(N-isopropylacrylamide) (PNIPAAm), having chelating functionalities were synthesized. PNIPAAm-imidazole (-Im) was precipitated and formed a gum-like aggregate in the neutral pH region at 50 °C, while PNIPAAm-carboxylic acid (---COOH) and PNIPAAm-iminodiacetic acid (-IDA) remained soluble even at pH 7. An addition of a paired ion, dodecyltrimethylammonium ion, was effective for inducing the precipitation of those polymers. PNIPAAm-Im was useful for collecting copper(II), nickel(II), cobalt(II), and lead(II), but was ineffective for cadmium(II) recovery. In contrast, PNIPAAm-COOH collected cadmium(II), while insufficiently recovered cobalt(II) and nickel(II). PNIPAAm-IDA was the best choice for collecting all metal ions in neutral pH's. After 20-folds concentration, the metal ions in river and seawater were successfully determined by graphite furnace atomic absorption spectrometry (GFAAS).     

络合吸附伏安法同时测定多种重金属离子

在络合剂亚硝基苯胲 乙醇 乙酸铵体系中,Cr(Ⅵ)、Cd2 、Cu2 、Pb2 、Ni2 等离子都能在汞电极上产生灵敏的阴极络合吸附波,其二次导数伏安峰电流均与离子质量浓度有良好的线性关系,可用于这些离子的定量检测,测定线性范围为Cr(Ⅵ)0.0017～0.67μg mL、Cd2 0.0017～0.117μg mL、Cu2 0.0083～5 8μg mL、Pb2 0.083～1.25μg mL、Ni2 0.17～150μg mL,RSD分别为5.7%、1 3%、1.4%、2 5%和1.6%。方法为工业废水、地表水及生活用水等样品中重金属离子的同时测定提供了可靠、灵敏的检测方法。     

Cellulose/chitosan composites prepared in ethylene diamine/potassium thiocyanate for adsorption of heavy metal ions

Cellulose/chitosan composites were successfully prepared in a new and basic-based solvent system, ethylene diamine/potassium thiocyanate (EDA/KSCN), by dissolving cellulose and chitosan in 70/30 (w/w) EDA/KSCN at ?19 °C, and then coagulating in methanol. Wide angle X-ray diffraction studies revealed that the EDA/KSCN solvent system is capable of disrupting the hydrogen bonds in both cellulose and chitosan and increase the amorphous regions. Stability tests proved that the composites are stable in acidic aqueous solution due to the hydrogen bonds formed between cellulose and chitosan. This is the first time to dissolve chitosan in a basic-based solvent system and prepare cellulose/chitosan composites in a straightforward way. The adsorption of heavy metal ions (Cu²⁺, Cd²⁺, and Pb²⁺) onto the cellulose/chitosan composites was investigated. The adsorption capacity is highly dependent on pH and the maximum metal uptake was obtained at pH 5.0. Increasing initial metal concentration enhanced the diffusion of metal ions to the composite surface and therefore the metal removal efficiency. Higher percentage of chitosan in the composites also led to higher metal adsorption. The results indicated that the prepared cellulose/chitosan (1:1) composite can adsorb 0.53 mmol/g Cu²⁺, 0.28 mmol/g Cd²⁺ and 0.16 mmol/g Pb²⁺ ions at pH 5.0. The Freundlich model and the pseudo-second-order model were in good agreement with the adsorption isotherms and kinetics, respectively. X-ray photoelectron spectroscopy studies indicated that the binding of heavy metal ions is attributed to the nitrogen atoms of amino groups in chitosan. The composites can be reused for metal removal.     

Study of the adsorption behavior of heavy metal ions on nanometer-size titanium dioxide with ICP-AES

A new method using nanoparticle TiO2 as solid-phase extractant coupled with ICP-AES was proposed for simultaneous determination of trace elements. The adsorption behavior of nanometer TiO2 towards Cu, Cr, Mn and Ni was investigated by ICP-AES, and the adsorption pH curves, adsorption isotherms and adsorption capacities were obtained. It was found that the adsorption rates of the metal ions studied were more than 90% in pH 8.0-9.0, and 2.0 mol L-1 HCl was sufficient for complete elution. Nanometer TiO2 possesses a significant capacity for the sorption of the metal ions studied which is higher than the capacity of silica, the commonly used extractant. The method has been applied to the analysis of some environmental samples with satisfactory results.     

Investigation of adsorption purification of the effluences containing heavy metal ions

Kinetics of adsorption purification of effluences containing heavy metal ions and adsorption of the metal ions under dynamic conditions using various adsorbents, including the products from industrial wastes are studied.     

Progress and challenges in molecularly imprinted polymers for adsorption of heavy metal ions from wastewater

Molecularly imprinted polymers (MIPs), prepared by the interaction forces such as forming covalent or non-covalent bonds by crosslinkers and initiators, are new types of specific recognition polymers with particular cavities. This is an ideal class of materials for wastewater treatment because of the particular holes left by the elution process. This review discusses the development process, classification, synthesis principles, systems, and polymerization methods of MIPs. At the same time, the adsorption mechanism of Copper (Cu), Mercury (Hg), Chromium (Cr), Silver (Ag), and Lead (Pb) in the MIPs technique are studied. Finally, some suggestions and prospects for the future development of MIPs are also put forward.