析相光度法测定微量铬的研究

研究了Ｃｒ（Ⅲ）－ＤＢＡＶ－ＴｒｉｔｏｎＸ－１００析相显色体系,建立了测定微量铬的析相光度法,在ＰＨ４．５的乙酸－乙酸钠介质中,Ｃｒ（Ⅲ）、ＤＢＡＶ、ＴｒｉｔｏｎＸ－１００加热形成配合物,于９５℃恒温水浴中析相１ｈ,即被ＴｒｉｔｏｎＸ－１００相完全富集,最大吸收峰为５５６ｎｍ,铬含量在０－１０μｇ／５ｍＬ范围内服从比耳定律,用于测定水样中的微量铬,结果令人满意。     

碘蓝分光光度法测定微量铬（Ⅳ）

基于在酸性介质中 ,重铬酸钾与碘化钾、淀粉的显色反应 ,建立了碘蓝分光光度法测定微量铬 ( )的方法。铬 ( )浓度在 0— 0 .6μg/ m L范围内有良好的线性关系 ,方法的相对标准偏差为 1.3% ,表观摩尔吸光系数为 5 .6 3× 10 4 L· mol- 1 · cm- 1 ,检出限为 2 .0× 10 - 3μg/ m L     

水样中总铬测定方法研究

用石墨炉-原子吸收光谱法(GF-AAS)和高锰酸钾-二苯碳酰二肼分光光度法,对环境水中的总铬进行了比较测定.结果表明:两种方法测定总铬的各项指标均在要求范围内,两种方法测定结果的RSD值均≤4.7%,加标回收率在94.5%-110%之间;表明两种方法均可测定水中总铬;但是石墨炉-原子吸收光谱法操作简便快速,更稳定.     

具有U_（qp）（U_3）U_（qp）（U_2）U_（qp）（SO_2）对称

构造了具有Ｕｑｐ（Ｕ３）Ｕｑｐ（Ｕ２）Ｕｑｐ（ＳＯ２）对称的双参数ｑｐ－形变二维相互作用玻色子模型（ＩＢＭ），并给出了其能谱和跃迁矩阵元．结果表明，能谱和跃迁矩阵元极其敏感地依赖于第二个形变参数．     

山东省焦家式金矿区土壤重金属铬高光谱监测研究（英文）

矿区土壤环境问题日益突出,以山东省烟台市焦家式金矿区为典型区,系统采集了85个表层土壤样品进行野外光谱实测,其中35份用于重金属铬含量测定。利用光谱变换技术对原始光谱提取了一阶微分、二阶微分和去包络线三种光谱指标,采用偏最小二乘回归法建立光谱数据与铬含量间的定量关系,将最优预测模型应用于其余50个样本点铬浓度值的获取,最终通过克里金插值实现了对研究区土壤重金属铬的快速监测。结果表明,基于一阶微分数据模型预测精度最高,其次为二阶微分,原始光谱和去包络线数据。研究区铬的含量与金矿的分布情况密切相关,即金矿密集区域铬含量更高,这表明金矿开采对土壤中铬的含量与分布存在一定影响。     

三溴偶氮胂褪色光度法测定土壤及化学试剂中铬（VI）

在 0 .4 8mol/L硝酸介质中 ,Cr( )与三溴偶氮胂 (TBA)发生褪色反应 ,该反应的表观摩尔吸光系数ε516nm=1.0 4× 10 5L· mol-1· cm-1,铬 ( )含量在 0— 1.0× 10 -4 g/L范围内呈良好线性关系。该法用于土样及化学试剂中 Cr( )的测定 ,结果令人满意。     

浊点萃取-石墨炉原子吸收光谱法测定药物胶囊中的痕量铬（Ⅵ）

采用硝基苯胲铵盐（铜铁试剂）、吡咯烷基二硫代甲酸铵（APDC）为络合剂,Triton X-114为表面活性剂的浊点萃取体系分别富集药物胶囊中的痕量Cr（Ⅲ）和总铬,富集后的Cr（Ⅲ）和总铬用石墨炉原子吸收光谱法进行测定.讨论了溶液pH值、表面活性剂浓度、络合剂浓度、平衡温度、平衡时间等对浊点萃取效率的影响.在优化的实验条件下,铬（Ⅵ）的检出限为0.031μg/L,相对标准偏差为1.2％（C=2.0μg/L,n=6）,加标回收率为98.4％-102.1％.应用该法测定药物胶囊中的痕量Cr（Ⅵ）,结果令人满意.     

Cr_（75）（Fe_（0．67）Mn_（0．33））_（25）合金加外磁场穆斯

利用加外场穆斯堡尔效应对Ｃｒ７５（Ｆｅ０．６７Ｍｎ０．３３）２５合金的磁性进行了研究．结果表明该合金不是磁单相的．在温度约２７５Ｋ时合金中开始形成反铁磁相，其共存于一顺磁相．在１３３Ｋ下，该顾磁相转变成铁磁相，共存于反铁磁相二铁磁、反铁磁交换相互作用的竟争导至合金在２８Ｋ下重入自旋玻璃态．     

Determination of Cr(III) and Cr(VI) in water by wavelength‐dispersive X‐ray fluorescence spectrometry after preconcentration with an ion‐exchange resin disk

A rapid and simple method using an ion‐exchange resin disk combined with wavelength‐dispersive X‐ray fluorescence (WDXRF) spectrometry was developed for the determination of Cr(III) and Cr(VI) in water. A 100‐ml water sample was first adjusted to pH 3 with nitric acid and then passed through an anion‐exchange resin disk placed on top of a cation‐exchange resin disk at a flow rate of 1 ml min^?1 to separate Cr(III) and Cr(VI). Anionic Cr(VI) was preconcentrated on the upper anion‐exchange resin disk, whereas cationic Cr(III) was preconcentrated on the lower cation‐exchange resin disk. Each ion‐exchange resin disk was dried at 100 °C for 30 min in an electric oven and coated with a commercially available laminate film. The specimens were measured using a WDXRF spectrometer. The calibration curves of Cr(III) and Cr(VI) showed good linearity in the range 1–10 µg. The detection limits corresponding to three times the standard deviation (n = 5) of blank values were 0.17 µg for Cr(III) and 0.16 µg for Cr(VI). If a 1‐l water sample is used, these limits would be 0.17 and 0.16 µg l^?1, respectively. A spike test for 50 µg l^?1 Cr(III) and Cr(VI) in tap water and river water showed quantitative recoveries (94–114%), although this was not observed for mineral drinking water owing to the overlap of V Kβ with Cr Kα. The recovery after overlap correction was satisfactory (115%). Copyright © 2011 John Wiley & Sons, Ltd.     

用三正辛胺-苯萃取分离体系-原子吸收光谱对铬作形态分析

研究了痕量铬形态分析的三正辛胺(TOA)-苯萃取分离体系-原子吸收光谱法。用三正辛胺(TOA)和苯在H₂SO₄介质中把水相中的Cr(Ⅵ)萃入到有机相而Cr(Ⅲ)留在水相中,使两种形态的Cr分离到两相中后对有机相的Cr(Ⅵ)和水相的Cr(Ⅲ)进行AAS测定,可求得Cr(Ⅵ)和Cr(Ⅲ)的含量,该方法对实际水样加标回收率分别在95.0%～102% 和94.8%～103%之间,相对标准偏差分别为2.9%和2.6% ,体系对Cr(Ⅵ)有富集作用,对Cr(Ⅵ)和Cr(Ⅲ)的检出限分别为6.6 μg·L-1和0.20 mg·L-1,TOA对Cr(Ⅵ)的最佳萃取量为4.6 mg·mL-1,该法简单、快速、准确。     

纳米TiO2预分离/富集FAAS法同时测定Cr(Ⅲ)和Cr(Ⅵ)的研究

纳米材料是近年来受到广泛重视的一种新兴功能材料,具有一系列新异的物理化学特性和一些优于传统材料的特殊性能.其中一点是随着粒径的减小,表面原子数迅速增大,表面原子周围缺少相邻的原子,具有不饱和性,易与其他原子相结合而稳定下来,因而具有很大的化学活性.纳米材料对许多金属离子具有很强的吸附能力,是痕量元素分析较为理想的分离富集材料.文章利用火焰原子吸收法(FAAS)研究了纳米TiO2(金红石型)对Cr(Ⅵ)/Cr(Ⅲ)的吸附性能,并应用于水样中铬的形态分析.吸附体系中pH对Cr(Ⅵ)和Cr(Ⅲ)的吸附有很大影响,当pH＞6时,纳米TiO2对Cr(Ⅲ)的吸附率大于90%,而对Cr(Ⅵ)基本不吸附,从而达到二者的分离.pH 6.5微酸性条件下,纳米TiO2吸附Cr(Ⅲ),然后以2mol.L-1HCl洗脱,得到Cr(Ⅲ)的含量,剩余水溶液中测定Cr(Ⅵ)含量.该法测定Cr(Ⅵ)和Cr(Ⅲ)的检出限分别为57和41 ng·mL-1,RSD分别为2.6%和3.4%(2.0μg·mL-1Cr,n=6),Cr(Ⅵ)和Cr(Ⅲ)的线性范围分别为0～9.0和0.1～10μg·mL-1.该法选择性好,大多数共存离子不干扰测定.该法简便快速,用于工业废水、地表水中铬的形态分析,结果较满意.     

弱碱性阴离子交换树脂富集ICP-AES测定环境水体中Cr(Ⅵ)和有机态Cr(Ⅲ)的研究

选用331弱碱性阴离子交换树脂,对微污染水体中的Cr(Ⅵ)和有机态Cr(Ⅲ)进行了分离富集作用研究,考察了酸度、富集时间、洗脱液类型、洗脱液浓度及溶液中共存离子对分离富集过程的影响。研究表明,分别用1.0 mol·L-1 HCl和2.0 mol·L-1 NH₄NO₃＋0.5 mol·L-1 NH₃·H₂O可以很好分步洗脱有机态Cr(Ⅲ)和Cr(Ⅵ),利用ICP-AES测定, 该方法对Cr(Ⅲ)和Cr(Ⅵ)的检出限分别为1.1和 1.4 μg·L-1,相应的相对标准偏差RSD(n＝6)平均值分别为3.8％和5.6％。该方法适用于自来水、地下水、地表水及生活污水中痕量Cr(Ⅵ)和有机态Cr(Ⅲ)的分离富集及测定。     

吸光度比值-导数光谱法同时测定铜(Ⅱ)和铬(Ⅲ)的研究

提出了运用吸光度比值-导数光谱法同时测定Cr(Ⅲ)与Cu(Ⅱ)含量的新方法。在pH 5.7的HAc-NaAc的缓冲溶液中,Cr3+,Cu2+与铬天青S(CAS)和溴化十六烷基三甲胺(CTMAB)可分别形成蓝色三元络合物。其摩尔吸光系数分别为2.52×105 L·mol-1·cm-1和1.01×105 L·mol-1·cm-1。Cu2+和Cr3+的浓度分别在0.08～1.2 μg·mL-1和0.05～0.52 μg·mL-1范围内符合比尔定律,其检测限分别为0.014和0.013 μg·mL-1。此方法应用于环境水中Cr(Ⅲ),Cu(Ⅱ)的同时测定,取得了满意的结果。     

ICP-AES法同时测定陶瓷制品铅、镉、铬、钴的溶出量

采用ICP AES法同时测定陶瓷制品铅、镉、铬和钴的溶出量 ,并对 4 %醋酸溶液中仪器入射功率的影响、分析谱线的选择和背景校正及共存元素的干扰等因素进行详细的研究。方法检出限 :铅 6 8μg·L-1;镉 0 18μg·L-1;铬 0 6 1μg·L-1;钴 1 0 μg·L-1。加标回收率为 98%～ 10 4 % ,相对标准偏差为 0 2 7%～1 2 4 %。该法简便快速 ,具有良好的精密度和准确度 ,适用于进出口陶瓷制品的日常检验     

FTIR和XPS对沸石合成特性及Cr(Ⅲ)去除机制的谱学表征

以粉煤灰为原料,采用优化的水热晶化法合成沸石,使用XRD,SEM和ζ电位分析沸石产品的组成特性,借助FTIR和XPS等揭示废水中Cr(Ⅲ)的去除机制。合成产品主要为NaP1型沸石,在pH值8～12区间内,ζ电位由-8.72mV降到-24.46mV。准二级方程和Langmuir等温线对试验的拟合效果更好,理论饱和吸附量为33.557 0mg.g-1。FTIR图谱表明—OH和Si—O类官能团在反应过程中有重要贡献。XPS全谱发现:结合能576.45eV为Cr(2p3/2)的特征峰,揭示了吸附过程的有效性。吸附Cr(Ⅲ)后,沸石中Si—Si和Si—O对应的结合能增加了0.25和0.60eV,含Si官能团可能与Cr(Ⅲ)发生了配位反应。O(1s)的结合能在反应后变得更低。这些证据表明:沸石对Cr(Ⅲ)的去除过程是物理吸附和化学吸附共同作用的结果。     

Synthesis,Characterization and Applications of Schiff Base Chemosensor for Determination of Cr(III) Ions

The development of a highly sensitive, selective, and efficient sensor for the determination and detection of Cr(III) ions remains a great challenge. Recently, some fluorescent chemosensors have been developed for the recognition of Cr(III) ions. But, the main drawbacks of the reported fluorescent chemosensors are the lack of selectivity and interference of anions and other trivalent cations. Herein, we designed and synthesized a novel thiazole-based fluorescent and colorimetric Schiff base chemosensor SB2 for the detection of Cr(III) ion by chemodosimetric approach. Using different analytical techniques including UV–vis, ¹³C-NMR, ¹H-NMR, and FT-IR analysis the chemosensor SB2 was structurally characterized. The fully characterized chemosensor SB2 was used for the spectrofluorimetric and colorimetric detection of Cr(III) ions. Interestingly, chemosensor SB2 upon interaction with various metal cations including Ni²⁺, Na⁺, Cd²⁺, Ag⁺, Mn²⁺, K⁺, Zn²⁺, Cu²⁺, Hg²⁺, Co²⁺, Pb²⁺, Mg²⁺, Sn²⁺, Al³⁺ and Cr³⁺ displays highly selective and sensitive fluorescent (turn-on) and colorimetric (yellow to colorless) response toward Cr(III) ions. The fluorescence and UV–vis techniques confirmed the selective hydrolysis of azomethine group (-C?=?N-) of Schiff base chemosensor SB2 by Cr(III) ions. As a result, the fluorescence enhancement was observed that is corresponding to 2-hydroxy-1-nepthaldehyde (fluorophore). The chemosensor SB2 exhibits high interference performance towards Cr(III) ions over other metal cations in a wide pH range. Mover, the quite low detection limit was calculated to be 0.027 µg ml-1 (0.5 µM) (3σ/slop), lower than the maximum tolerable limits of Cr(III ions (10 µM) in drinking water permitted by the United States Environmental Protection Agency (EPA). These results show that chemosensor SB2 has great potential to detect selectively Cr(III) ions in the agricultural, environmental and biological analysis system.

Graphical Abstract

     

流动注射在线分离富集-火焰原子吸收光谱法测定环境水样中Cr(Ⅲ)和Cr(Ⅵ)的形态

采用单阀阴离子和阳离子交换树脂微柱并联 ,两柱交替采样逆向洗脱流动注射在线分离富集环境水样中Cr(Ⅲ )和Cr(Ⅵ ) ,分别用 15 %HNO3和 8%NH4 NO3洗脱 ,火焰原子吸收光谱法直接检测。富集 1min时Cr(Ⅲ )和Cr(Ⅵ )的特征浓度分别为 :1 5 0 μg·L- 1 和 1 39μg·L- 1 ,Cr(Ⅲ )和Cr(Ⅵ )检出限 (3σ)分别为 1 0 3μg·L- 1 和 0 5 4 μg·L- 1 ;相对标准偏差 (10 μg·L- 1 )分别为 :3 4 1%和 1 80 % ,分析样品加标回收率在 93 5 %～ 10 7 5 %之间。     

ELS study on chemisorbed state of CO on Cr(110)

The chemisorbed state of CO on a Cr(110) surface has been investigated at 300 K by electron energy loss spectroscopy (ELS) with the in-situ combined supplementary techniques. The ELS spectrum of the Cr(110) surface after CO adsorption is characterized by the peaks at 2, 4.4, 6–7, 9, 11, 14.5, 19 and 23 eV, and is found to be practically the same as that of the oxygen covered surface. The C-KLL Auger spectra obtained in the range 0.1–900 L CO agree with those of metal carbides. These results are considered to indicate that CO is dissociatively chemisorbed on the Cr(110) surface throughout the whole exposure region examined. The average sticking probability of CO on Cr(110) is 0.7 at below 0.5 L, and the maximum work function increase at 1 L is ~0.1 eV. The adsorbed state of O atoms produced from dissociative adsorption of CO is also discussed.