含氮硫多配位基螯合纤维的合成及其性能研究

以腈纶纤维为原料，合成了含氮硫多配位基螯合纤维，讨论了反应时间和反应温度对产物增重的影响，选择了适当的反应条件。通过元素分析和红外光谱，分析了螯合纤维的可能结构，并对合成的螯合纤维进行了基本性能测定。该纤维可用于贵金属元素金、铂的富集与分离。     

用含偕胺肟基螯合纤维吸附、还原Au^3＋的研究（Ⅱ）：—氧化还原过程的初步研究

讨论了含偕胺肟基螯合纤维对Au^3 的还原过程及螯合与还原反应间的关系。结果表明，含偕胺肟基螯合纤维在吸附Au^3 的过程中，功能基螯合Au^3 之后再将其部分还原成单质金，而偕胺肟基则先被氧化成酰氨基进而变成羧基，吸附了Au^3 的纤维经径高温灼烧后合理使可得到海绵金。     

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。     

聚乙烯醇胺肟螯合纤维吸附钯的研究

用动态法研究了聚乙烯醇胺肟（ＰＶＡＡＯ）螯合纤维对钯的吸附。讨论了影响吸附率和回收率的因素，确定了最隹吸附条件。用５％硫脲＋０．５０ｍｏｌ／Ｌ硝酸溶液可以解吸。ＰＶＡＡＯ螯合纤维对钯的饱和吸附容量为４５１．９ｍｇ／ｇ干纤维。     

偕胺肟纤维的合成及对银吸附性能的研究

本文介绍了偕胺肟螯合纤维的制备方法及对银的吸附性能。脱水聚乙烯醇纤维与丙烯睛反应制得氰乙基化纤维。再与盐酸羟胺反应把氰乙基化纤维转化为偕胺肟纤维。该螯合纤维对银的吸附容量达0.3mmol/g。吸附速度也很快。     

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。     

聚丙烯酰胺肟-羧酸螯合纤维对多种微量元素富集性能及机理的研究

近年来,利用巯基及它种螯合基纤维素富集测定多种微量元素的研究报导较多,但将螯合基团接在合成纤维上作为富集剂的报导尚少。我们曾用腈纶为原料合成聚丙烯酰胺肟-羧酸螯合纤维富集测定过数种微量元素。本文较系统地研究了该螯合纤维对30余种微量元素的定量富集酸度、吸附速度、洗脱酸度、饱和吸附量和共存离子的干扰,讨论了螯合纤维的稳定性、耐酸碱性、再生使用和富集机理,并进行了低浓度元素的富集和样品分析。实验表明,该螯合纤维是一种良好的高分子富集剂,它可以定量富集多种微量元素,具     

硫代酰胺基螯合纤维的合成及其吸附性能研究

以腈纶纤维(PAN)为起始原料,分别经水合肼、乙二胺、二乙烯三胺预交联后,以N,N-二甲基甲酰胺(DMF)作溶剂与硫化钠反应,合成了3种携硫代酰胺功能基可达6.8mmol/g·干纤维的螯合功能纤维。利用红外光谱、元素分析、热稳定分析、重量分析等对该螯合纤维的结构、性能等进行了表征;研究了该螯合纤维对Au3 ,Ag ,Pd2 等贵金属离子的吸附性能;考察了温度、pH、硫含量等对纤维吸附Ag 离子的影响。结果表明,纤维对Au3 ,Ag 等贵金属离子具有良好的吸附性能,对Au3 的吸附容量为800mg/g·干纤维;对Ag 离子的吸附容量可达1510mg/g·干纤维,并具有良好的吸附动力学特性,该螯合纤维可用于混合溶液中Ag(I)离子的吸附分离。     

载双硫腙螯合纤维制备及富集重金属离子研究

合成了一种聚苯乙烯基载双硫腙 (DzS) 螯合纤维,研究了该纤维对4种重金属离子的螯合性能,讨论了吸附酸度、吸附时间等对4种重金属吸附性能的影响,选择了适当的反应条件,得出了该螯合纤维对重金属离子吸附量及选择性大小顺序:Pd(Ⅱ)>Cu(Ⅱ)>Co(Ⅱ)>Cd(Ⅱ),指出该纤维与石墨炉原子吸收分光光度测定法结合,可成功地应用于环境检测天然水样中的重金属离子.     

胺肟螯合纤维对汞的吸附性能

本文研究了胺肟螯合纤维吸附汞的条件以及汞的洗脱。测定了汞的吸附容量。给出了汞与一些其它元素的分离因数。实验结果表明胺肟螯合纤维可有效地吸附汞,具有吸附速度快、易洗脱、选择性好等优点,并且螯合纤维可以再生和反复使用。     

化学-X-射线荧光光谱法测定地质样品中的痕量稀土元素

本文采用对氯偶氮氯膦(CPA—PCL)为螯合剂,VS-Ⅱ型强碱性阴离子交换纤维为载体,以先吸着后螯合方式对稀土元素与基体元素进行分离与富集,并经酸溶制备成溶液,采用溶液进样法直接由X射线荧光光谱法(XRFS)测定15个稀土元素。该法具有简便、整合剂用量少、基体效应小的特点,精密度、准确度及检测限均能满足地质样品分析要求,取得满意结果。     

微晶萘固态萃取分离稀土及其在分析中的应用

报道了以微晶萘作吸附载体,固态萃取分离痕量稀土元素的新方法,在ＰＨ５．８－８．６和７．２－８．６时,Ｓｃ＾３＋和Ｙ＾３＋,Ｌａ＾３＋,Ｅｕ＾３＋,Ｙｂ＾３＋,Ｙｂ＾３＋,Ｌｕ＾３＋与８－羟基喹啉形成的金属螯合物,可被微晶萘固态选择萃取。     

Insights into colloid-mediated trace element release at the soil/water interface

Organic or inorganic colloids play a major role in the mobilization of trace elements in soils and waters. Environmental physicochemical parameters (pH, redox potential, temperature, pressure, ionic strength, etc.) are the controlling factors of the colloidal mobilization. This study was dedicated to follow the colloid-mediated mobilization of trace elements through time at the soil/water interface by means of an experimental approach. Soil column experiments were carried out using percolating synthetic solutions. The percolated solutions were ultrafiltrated with various decreasing cutoff thresholds to separate the different colloidal phases in which the dissolved organic carbon and trace element concentrations were measured. The major results which stem from this study are the following: (i) The data can be divided into different groups of organic compounds (microbial metabolites, fulvic acids, humic acids) with regard to their respective aromaticity and molecular weight. (ii) Three groups of elements can be distinguished based on their relationships with the colloidal phases: the first one corresponds to the so-called "truly" dissolved group (Li, B, K, Na, Rb, Si, Mg, Sr, Ca, Mn, Ba, and V). The second one can be considered as an intermediate group (Cu, Cd, Co, and Ni), while the third group gathers Al, Cr, U, Mo, Pb, Ti, Th, Fe, and rare earth elements (REE) carried by the organic colloidal pool. (iii) The data demonstrate that the fulvic acids seem to be a major organic carrier phase for trace elements such as Cu, Cd, Co, and Ni. By contrast, the trace elements belonging to the so-called colloidal pool were mostly mobilized by humic acids containing iron nanoparticles. Lead, Ti, and U were mobilized by iron nanoparticles bound to these humic acids. Thus, humic substances allowed directly or indirectly a colloidal transport of many insoluble trace elements either by binding trace elements or by stabilizing a ferric carrier phase. (iv) Finally, the results demonstrated also that REE were mostly mobilized by humic substances. The REE normalized patterns showed a middle REE downward concavity. Therefore, as previously shown elsewhere humic substances are a major control of REE speciation and REE fractionation patterns as well since the humic substance/metal ratio was the key parameter controlling the REE pattern shape.     

Adsorption and preconcentration of 2,4-dichlorophenoxyacetic acid on a chemically modified silica gel surface

The herbicide 2,4-dichlorophenoxyacetic acid (2,4-D), chemically anchored to a silica gel surface, was used to adsorb and preconcentrate the same herbicide from aqueous solutions at room temperature. From a series of adsorption isotherms adjusted to a modified Langmuir equation, the maximum number of moles adsorbed was calculated as 4.67 x 10(-5) mol g(-1), with the highest retention capacity at pH 5. This modified silica gel was used in a column for preconcentrating trace levels of 2,4-D. The preconcentrated herbicide can be directly eluted with methanol with a recovery efficiency higher than 97%. The concentration factor was 8.33.     

Synthesis and Applications of Poly(Acrylphenylamidrazone-Phenyl-Hydrazide-Acylphenylhydrazine) Chelating Fiber for Preconcentration and Separation of Trae In(III), Zr(IV), Tl(I), V(V), Ga(III) and Ti(IV) from Solution Samples

 An ICP-OES method using a new poly (acrylphenylamidrazone-phenylhydrazide-acylphenylhydrazine) chelating fiber to preconcentrate and separate trace In(III), Zr(IV), Tl(I), V(V), Ga(III) and Ti(IV) ions from solution samples has been established. The new chelating fiber was synthesized using polyacrylonitrile fiber as a starting material and the structure of the chelating fiber was determined by FT infrared spectrometry. The acidity, adsorption rate, re-use, capacity and interference on the adsorption of ions on the chelating fiber as well as the conditions of desorption of these ions from the chelating fiber were investigated by means of inductively coupled plasma optical emission spectrometry (ICP-OES). The results show that the relative standard deviations for the determination of 10 ng/ml In, Tl, Ga and 1 ng/ml Zr, V, Ti were lower than 2.5%. The results obtained for these ions in real solution samples by this method were basically in agreement with the given values with average errors of less than 4%. Received November 29, 2000. Revision May 22, 2001.     

Properties and applications of polyacrylacylisothiourea chelating fiber for preconcentration and separation of trace titanium, vanadium and bismuth

An ICP-OES method using a new poly-acrylacylisothiourea chelating fiber to preconcentrate and separate trace Ti(IV), V(V) and Bi(III) ions from solution samples is established. The results show that 5–25 ng/ml of Ti or V and 50–250 ng/ml of Bi ions in 200–1000 ml of solution can be enriched quantitatively by 0.05 g of the fiber at pH 3 with recoveries over 97%. These ions can be desorbed quantitatively with 10 ml of 4M HC1O₄. 100- to 1000-fold excesses of Fe(III), Al(III), Ca(II), Mg(II), Cu(II), Ni(II) and Mn(II) ions cause little interference. The chelating fiber stored for about 2 years can still be used repeatedly for preconcentration and separation of trace Ti, V and Bi ions from solution with above 95% recovery. The RSDs for enrichment and determination of 5 ng/ml of Ti or V and 50 ng/ml of Bi are in the range 2.5–2.8%. The recoveries of added standard in real waste waters and mineral samples are between 96 and 100%, and the concentration found for each ion in the mineral sample was in good agreement with that measured by ETAAS.     

Preconcentration and determination of trace elements with 2,6-diacetylpyridine functionalized Amberlite XAD-4 by flow injection and atomic spectroscopy

An on-line flow injection method for the direct determination of trace elements in environmental samples is described. A mini-column packed with 2,6-diacetylpyridine functionalized Amberlite XAD-4 was used to preconcentrate and separate 8 trace metals (Cd, Co, Cu, Mn, Ni, Pb, U and Zn) from water and extracts from solid samples. The metals were eluted with 0.1 M HNO(3) directly to the detection system (either inductively coupled plasma-mass spectrometry (ICP-MS) or flame atomic absorption spectrometry (FAAS)). As well as demonstrating that the resin could be used to preconcentrate ultra-trace analytes from natural waters, it was also shown to work well at a pH of 5.5. Therefore, after treatment of sample digests with sodium fluoride, samples that contain extremely large concentrations of iron may be analysed for trace analytes without the excess iron overloading the capacity of the resin. To this end, the analytes Cd, Co, Cu and Ni were preconcentrated from acid extracts of certified soil/sediment samples and then eluted with nitric acid to be determined on-line. Limits of detection (3sigma) of Cd = 0.33 microg l(-1), Co = 0.094 microg l(-1), Cu = 0.34 microg l(-1), Mn = 0.32 microg l(-1), Ni = 0.30 microg l(-1), Pb = 0.43 microg l(-1), U = 0.067 microg l(-1) and Zn = 0.20 microg l(-1) for the FI-ICP-MS system and Cd = 22 microg l(-1), Co = 60 microg l(-1), Cu = 10 microg l(-1) and Ni = 4.8 microg l(-1) for the FI-FAAS system were obtained. Analysis of certified reference materials showed good agreement with the certified values using the two methods.     

Separation and preconcentration of ultratrace lead in biological organisms and its determination by graphite furnace atomic absorption spectrometry

A biological organism (chitosan) was utilized to preconcentrate lead ions from tap water. This preconcentration was achieved by mixing 0.8 ml of chitosan slurry with 10-50 ml of lead-containing solution and subsequently separating by centrifugation. The chitosan paste was then dissolved in 1 ml of 0.2% nitric acid and analysed by graphite furnace atomic absorption spectrometry. The extraction efficiency can approach 100% in the pH range 4-10. The amount of chitosan used was not critical. The effect of some impurities was also investigated. If six samples were prepared simultaneously, the time needed to preconcentrate each sample was less than 3 min. Two different modes of standard addition (the standard lead solutions being added before and after preconcentration) were used for analysis of tap water samples, and the results obtained by the two modes were found to be quite consistent.     

Applicability of capillary electrophoresis to the analysis of trace rare earth elements in geological samples.

This study developed a methodology to analyze trace rare earth elements (REEs) in geological materials by capillary electrophoresis (CE). Changed from dilute HNO3 into a water medium by heating, REE ions are detectable at approximately 2 ng mL(-1). In the presence of coexisting elements from geological samples, REE separations were carried out. After sample fusion with Na2O2 and interference separation with ammonium pyrrolidinedithiocarbamate chelate, REE analytes were coprecipitated with Mg(OH)2 at pH 8.5, and then prepared into a water medium for CE determination. Using the standard addition method, this protocol was validated by analyses with better than 5% precision. This method was applied to geological materials; the REE results are in consistence with their certified values. With electrokinetic injection, internal standard (IS) selected among lanthanides is a prerequisite of high-quality REE data. An approach was proposed to derive the IS content for further correcting its contribution from unknown samples.     

微晶萘固相萃取分离富集及ICP—AES测定Cu,Mn的研究

报道以微晶萘作吸附载体的固相萃取分离及ＩＣＰ－ＡＥＳ测定Ｃｕ，Ｍｎ的新方法，详细研究了溶液酸度，试剂浓度，萘用量及共存离子对待测物回收率的影响，考查了加入适量的Ｃｏ＾２＋，对富集痕量Ｃｕ＾２＋Ｍｎ＾２＋辅助作用，本法用于生物样品马尾藻及小牛肝中Ｃｕ，Ｍｎ的测定，分析结果与标准值吻合。