不同复合体系对含钛高炉渣光催化还原Cr(VI)的影响

采用煅烧的硫酸盐掺杂的含钛高炉渣(sulfate-modified titanium-bearing blast furnace slag, STBBFS)作为光催化剂, 研究了Cr(VI)-柠檬酸[Cr(VI)-CA]复合体系和Cr(VI)-柠檬酸-硝酸铁[Cr(VI)-CA-FN]复合体系对 STBBFS催化剂光催化活性的影响. 结果表明: 酸性条件下, 不同复合体系对STBBFS催化剂光催化活性的促进作用按Cr(VI)-CA-FN复合体系＞Cr(VI)-CA复合体系＞Cr(VI)单一体系增强. Cr(VI)-CA复合体系在pH＝2.5, 反应50 min后STBBFS催化剂光催化活性为0.426 mg•min―1•g―1时将溶液中的Cr(VI)全部还原; 而Cr(VI)-CA-FN复合体系在pH＝2.5, 反应16 min后STBBFS催化剂光催化活性为1.2425 mg•min―1•g―1时将溶液中的Cr(VI)全部还原. 两种复合体系中, Cr(VI)离子的光催化还原过程都遵循L-H动力学规律, 虽然加入CA和FN后, 降低了吸附对光催化还原Cr(VI)的影响, 但是Cr(VI)吸附至催化剂表面仍然是整个反应过程的关键.     

杂多酸存在下X3B染料光降解和Cr(VI)光还原的协同反应机理

以H3PW12O40(PW)和H4SiW12O40(SiW)杂多酸(POM)为催化剂, 波长大于320 nm的高压氙灯为光源, 研究了混合水溶液中活性艳红染料X3B的光致降解和重铬酸根(Cr(VI))的光致还原. 结果表明, POM-X3B-Cr(VI)三元体系的反应效率高于POM-X3B、POM-Cr(VI)和X3B-Cr(VI)二元体系的反应效率, PW的光活性高于SiW, 且X3B光降解和Cr(VI)光还原之间存在明显的协同作用. 通过考察各组分起始浓度以及N2、O2、H2O2和乙醇的影响, 实验发现, 激发态POM*与H2O反应产生POM-和·OH是反应的决速步骤. X3B光降解和Cr(VI)光还原分别主要通过·OH 和POM-进行, 而X3B和Cr(VI)之间光化学反应的贡献较小. 在二元和三元体系中POM浓度对反应速率表现出不同的影响, 表明激发态POM*与H2O之间的反应具有可逆性.     

不同复合体系对含钛高炉渣光催化还原Cr(VI)影响

采用煅烧的硫酸盐掺杂的含钛高炉渣(sulfate-modified titanium-bearing blast furnace slag,STBBFS)作为光催化剂,研究了Cr(VI)-柠檬酸[Cr(VI)-CA]复合体系和Cr(VI)-柠檬酸-硝酸铁[Cr(VI)-CA-FN]复合体系对STBBFS催化剂光催化活性的影响.结果表明:酸性条件下,不同复合体系对STBBFS催化剂光催化活性的促进作用按Cr(VI)-CA-FN复合体系>Cr(VI)-CA复合体系>Cr(VI)单一体系增强.Cr(VI)-CA复合体系在pH=2.5,反应50 min后STBBFS催化剂光催化活性为0.426 mg·min-1·g-1时将溶液中的Cr(VI)全部还原;而Cr(VI)-CA-FN复合体系在pH=2.5,反应16 min后STBBFS催化剂光催化活性为1.2425 mg·min-1·g-1时将溶液中的Cr(VI)全部还原.两种复合体系中,Cr(VI)离子的光催化还原过程都遵循L-H动力学规律,虽然加入CA和FN后,降低了吸附对光催化还原Cr(VI)的影响,但是Cr(VI)吸附至催化剂表面仍然是整个反应过程的关键.     

In This Issue

<正>封面:李可心等报道了在Cr(VI)/4-CP复合污染系统中多孔g-C_3N_4的协同光催化效应.与单组份光催化系统相比,在Cr(VI)/4-CP复合污染系统中Cr(VI)的还原效率和4-CP的降解效率同时提高.这种协同光催化效应可归因于多孔g-C_3N_4的电子转移作用加速了Cr_2O_7~(2–)和4-CP之间的氧化还原反应.见本期第1804–1811页.     

盐酸副玫瑰苯胺褪色光度法测定铬(Ⅵ)

研究了显色剂盐酸副玫瑰苯胺与Cr2O72 -的褪色反应.发现在H2SO4介质中盐酸副玫瑰苯胺与Cr(Ⅵ)反应具有高灵敏的褪色现象.据此建立了测定Cr(Ⅵ)的光度法.当Cr(Ⅵ)质量浓度为0.01～2.0 mg/L时,盐酸副玫瑰苯胺的吸光度与Cr(Ⅵ)浓度符合朗伯-比耳定律,摩尔吸光系数为5.9×105 L·mol-1·...     

氨基功能化纳米Fe3O4磁性高分子吸附剂对废水中Cr(VI)的吸附研究

采用分散聚合法通过共聚、开环反应, 对纳米Fe3O4进行表面功能化修饰, 得到富含NH2官能团的纳米磁性高分子复合材料. 通过透射电镜(TEM)、振动样品磁强计(VSM)、热重差热分析(TGA)、X射线衍射(XRD)、红外光谱(IR)等对其进行表征, 着重研究了其作为吸附剂对Cr(VI)的吸附性能. 结果表明: 该吸附剂对Cr(VI)的吸附能在10 min内达到平衡; 废水溶液pH值能显著影响吸附剂对Cr(VI)的吸附效果, pH为2.5时效果最佳. 废水中Cr(VI)的初始浓度、吸附时间、温度等因素对吸附效果均有不同程度的影响. 结合相应pH值下Cr(VI)的形态分布, 探讨了这种新型材料对Cr(VI)的吸附机理. 结果表明: 其吸附机理及吸附容量与废水中Cr(VI)的离子形式有关; 吸附过程以离子交换与静电引力为主. 等温吸附数据符合Langmuir模型, T＝308 K, pH＝2.5, V＝40 mL时, 吸附剂的饱和吸附容量qm＝25.58 mg/g. 吸附为吸热过程, 焓变ΔH＝8.64 kJ/mol.     

TiO2纳米管半波脉冲直流电光电催化还原Cr（Ⅵ）

报道了在半波脉冲直流电(h-DC)作为电压驱动下,以阳极氧化法制备的TiO2纳米管(TNT)为工作电极,紫外光光电催化(PEC)还原Cr(VI)的研究.半波脉冲直流电相比稳压直流电(DC)和交流电(AC)具有更佳的载流子分离和光电催化作用.探讨了电压大小、频率及电解质NaCl浓度对Cr(VI)催化还原反应的影响.TNT光电催化和电催化还原Cr(VI)效率随外加电压和频率的增大而增大,但是频率过高对反应有一定的抑制作用.电解质NaCl对反应的影响不显著,这是因为在重金属还原体系中,NaCl作为活性氯物种的母体和增强溶液导电性的作用体现得不明显.     

ZnIn2S4/SnS2 3D异质结的制备及其在可见光下高效还原Cr（Ⅵ）的应用（英文）

随着印染、纺织和镀铬等行业的不断发展,含有六价铬(Cr(VI))工业废水的大量排放造成严重的环境污染,威胁着人类健康.在过去的几十年中,废水中Cr(VI)去除的方法有很多,其中包括离子交换、膜分离、化学沉淀和吸附等.然而,这些传统的方法存在成本高、能耗高、效率低或者去除不彻底等缺点,阻碍了其广泛应用.在此背景下,光催化还原作为一种高效、绿色、有应用前景的Cr(VI)废水处理方法,受到越来越多科学家的关注.开发高效可见光响应光催化剂是实现光催化还原Cr(VI)应用的关键.ZnIn2S4是一种三元硫化物半导体材料,具有较强可见光吸收能力.但纯ZnIn2S4光生载流子复合严重以及可见光响应范围较窄导致其光催化性能较低.为了解决这一问题,构建异质结是一种常见的有效方法.SnS2具有合适的带隙(~2.2 eV),价格低廉,无毒且可见光吸收能力强.因此,构建ZnIn2S4/SnS2异质结有望实现高效可见光催化还原Cr(VI).本文通过简单的水热法成功制备了ZnIn2S4/SnS2三维(3D)异质结,并在可见光照射下对催化剂还原Cr(VI)性能进行了评价.实验结果显示,ZnIn2S4/SnS2 3D异质结光催化活性随着SnS2含量增加呈现先增加后减少的趋势.当SnS2与ZnIn2S4的质量比为1:10时,ZnIn2S4/SnS2 3D异质结催化还原Cr(VI)效率最高.可见光照射下反应70 min,Cr(VI)(50 mg/L)的还原效率达到100%,远高于纯ZnIn2S4和SnS2.荧光光谱分析(PL)和紫外-可见吸收光谱(UV-Vis)显示,光生载流子分离效率和光吸收效率的增强是还原Cr(VI)性能增加的两个原因.此外,经过三个周期的循环实验,ZnIn2S4/SnS2 3D异质结催化还原Cr(VI)效率没有明显降低,表现出较好的光催化稳定性.     

多胺型阴离子交换纤维吸附铬(VI)的动力学

以聚丙烯腈纤维为原料, 采用化学改性法, 制备了多胺型阴离子交换纤维. 研究该纤维对Cr(VI)的吸附特性. 在研究的温度及浓度范围内, 该纤维对Cr(VI)吸附的平衡数据符合Langmuir和Freundlich吸附等温方程, 对Cr(VI)有较强的亲和力, 吸附反应易于进行. 重点研究了该纤维对Cr(VI)的吸附动力学特性, 分别采用Lagergren一级动力学方程、修正伪一级动力学方程、伪二级动力学方程和颗粒内扩散方程进行拟合, 计算相应的速率常数. 研究表明, 该吸附是一个快速吸附过程, 20 min即可接近吸附平衡, 吸附过程符合伪二级动力学方程, 以化学吸附为主, 该纤维能够多次反复对Cr(VI)进行吸附.     

DCB-偶氮胂高灵敏光度法测定痕量铬(Ⅵ)

本文研究了 DCB偶氮胂与 Cr2 O2 - 7的褪色反应。结果表明 ,在硝酸介质中褪色反应具有高的灵敏度 ,拟定了反应的最佳条件 ,建立了一种新的光度法测定痕量铬( )方法。本法检出限为 4.2 2× 1 0 - 11g/m L ,线性范围为 0～ 0 .8μg/1 0 m L ,用于测定人发中的痕量铬 ( ) ,结果令人满意     

New insights on the mechanism of oxidation of D-galacturonic acid by hypervalent chromium

The pollutant Cr(VI) is known to be very carcinogenic. In conditions of excess of Cr(VI), oxidation of D-galacturonic acid (Galur), the major metabolite of pectin, yields d-galactaric acid (Galar) and Cr(III). The redox reaction takes place through a multistep mechanism involving formation of intermediate Cr(II/IV) and Cr(V) species. The mechanism combines one- and two-electron pathways for the reduction of Cr(IV) by the organic substrate: Cr(VI)→ Cr(IV)→ Cr(II) and Cr(VI)→ Cr(IV)→ Cr(III). This is supported by the observation of the optical absorption spectra of Cr(VI) esters, free radicals, CrO(2)(2+) (superoxoCr(III) ion) and oxo-Cr(V) complexes. Cr(IV) cannot be directly detected; however, formation of CrO(2)(2+) provides indirect evidence for the intermediacy of Cr(II/IV). Cr(IV) reacts with Galur much faster than Cr(V) and Cr(VI) do. The analysis of the reaction kinetics via optical absorption spectroscopy shows that the Cr(IV)-Galur reaction rate inversely depends on [H(+)]. Nevertheless, high [H(+)] still does not facilitate accumulation of Cr(IV) in the Cr(VI)-Galur mixture. Cr(VI) and the intermediate Cr(V) react with Galur at comparable rates; therefore the build-up and decay of Cr(V) accompany the decay of Cr(VI). The complete rate laws for the Cr(VI), Cr(V) and Cr(IV)-Galur redox reaction are here derived in detail. Furthermore, the nature of the five-co-ordinated oxo-Cr(V) bischelate complexes formed in Cr(VI)-Galur mixtures at pH 1-5 is investigated using continuous-wave and pulsed electron paramagnetic resonance (EPR) and density functional theory (DFT).     

Removal of Chromium(VI) from Groundwater Using Oil Shale Ash Supported Nanoscaled Zero-valent Iron

Oil shale ash(OSA) supported nanoscaled zero-valent iron(OSA-nZVI) was used as a rapid and efficient reductant for Cr(VI) reduction. The optimal mass ratio of nZVI to OSA and the optimal dosage were explored. The effects of initial pH, reaction temperature, initial Cr(VI) concentration, and common cations and anions in groundwater on Cr(VI) reduction were determined in batch experiments. The results show that the optimum initial pH is 5.0. The reaction temperature has a positive effect on Cr(VI) reduction while the real groundwater has a negative effect. Additionally, 84.22% Cr(VI) was still reduced by 3 g/L OSA-nZVI(1:2)(mass ratio of OSA to Fe⁰ was 1:2) within 120 min for 50 mg/L Cr(VI) under conditions of 10℃ and unadjusted pH.     

Chromic Oxidation of 2-Deoxy-d-Glucose. Comparative Study with Aldoses. I.

Abstract

A rate law for the oxidation of 2-deoxy-d-glucose (2DG) by Cr(VI) in perchloric acid has been derived. This rate law corresponds to the reaction leading to the formation of 2-deoxy-d-gluconic acid (2DGA). No cleavage to carbon dioxide takes place when a twenty-fold or higher excess of aldose over Cr(VI) is employed. Kinetic constants are interpreted in terms of the absence of an hydroxyl group at C-2 on the stability of the chromic ester formed in the first reaction step. Free radicals formed during the reaction convert Cr(VI) to Cr(V). The latter species was detected by EPR measurements.     

Rapid—In—situ Determination of Chromium （VI） in Water Using Modified Diphenylcarbazine with Citrate

In recent years, the determination of Cr (VI) has attracted great attention because of its toxicity to human, plants and animals1-5. Usually, in the industrial waste water, the concentration of Cr (VI) is relatively high and should be determined frequently. So, an accurate, quick, and convenient method for the measurement of Cr (VI) in environmental water, as well as in river, lake, sea and tap water, is of great importance. The method for determination of Cr (VI) by diphenylcarbazine …     

Sequential injection analysis for Cr(VI) and Cr(III) with renewable surface reflection spectrophotometry.

On the basis of the chromogenic reaction of chromium(VI) with 1,5-diphenylcarbohydrazide (DPC) on the surface of Polysorb C-18 beads and the sequential injection renewable surface technique (SI-RST), a highly sensitive reflect spectrophotometric method for the determination of chromium(III) and chromium(VI) was proposed. Considerations of system and flow cell design, and factors that influence the determination performance were discussed. With 300 microl of sample loaded and 0.6 mg of beads trapped, the linear response range was 0.02 - 0.5 mg l(-1) Cr(VI) with a detection limit (3 sigma) of 2.4 microg l(-1) Cr(VI). The method achieves a precision of 1.3% RSD (n = 11) and a throughput of 53 samples per hour. The determination of Cr(III) was based on the same reaction for the determination of Cr(VI) after being oxidized by (NH4)2S2O8. The precision of the oxidation method was evaluated using a 0.2 mg l(-1) Cr(III) standard, yielding an RSD of 2.5% (n = 11). The average recovery of Cr(III) oxidized was tested to be 99.1%. The proposed method was used in the simultaneous determination of Cr(VI) and Cr(III) in water samples, and the error was less than 3%.     

Redox and complexation chemistry of the Cr(VI)/Cr(V)-D-galacturonic acid system

The oxidation of d-galacturonic acid by Cr(VI) yields the aldaric acid and Cr(III) as final products when a 30-times or higher excess of the uronic acid over Cr(VI) is used. The redox reaction involves the formation of intermediate Cr(IV) and Cr(V) species, with Cr(VI) and the two intermediate species reacting with galacturonic acid at comparable rates. The rate of disappearance of Cr(VI), Cr(IV) and Cr(V) depends on pH and [substrate], and the slow reaction step of the Cr(VI) to Cr(III) conversion depends on the reaction conditions. The EPR spectra show that five-coordinate oxo-Cr(V) bischelates are formed at pH < or = 5 with the uronic acid bound to Cr(V) through the carboxylate and the alpha-OH group of the furanose form or the ring oxygen of the pyranose form. Six-coordinated oxo-Cr(V) monochelates are observed as minor species in addition to the major five-coordinated oxo-Cr(V) bischelates only for galacturonic acid : Cr(VI) < or =10 : 1, in 0.25-0.50 M HClO(4). At pH 7.5 the EPR spectra show the formation of a Cr(V) complex where the vic-diol groups of Galur participate in the bonding to Cr(V). At pH 3-5 the Galur-Cr(V) species grow and decay over short periods in a similar way to that observed for [Cr(O)(alpha-hydroxy acid)(2)](-). The lack of chelation at any vic-diolate group of Galur when pH < or = 5 differentiates its ability to stabilise Cr(V) from that of neutral saccharides that form very stable oxo-Cr(V)(diolato)(2) species at pH > 1.     

Preparation and application of a novel core/shell organic nanoparticle as a fluorescence probe in the selective determination of Cr(VI)

A novel core/shell organic nanoparticles, anthracene/poly-acrylamide (AN/PAM), has been prepared successfully. Based on the fluorescence quenching of AN/PAM nanoparticles by Cr(VI), a method for the selective determination of Cr(VI), without separation of Cr(VI) in water, was developed. Furthermore, the reaction mechanism between nano-AN/PAM and Cr(VI) was also discussed. The synthesis and reaction conditions were investigated in detail. The assay is characterized by short reaction time, very few interference stable fluorescence signals, simple instruments and sensitivity. Under optical experimental conditions, a limit of detection of 0.02 microg/ml was achieved. The calibration curve was linear over the concentration range 0.04-2.00 microg/ml with a correlation coefficient of 0.9924. The proposed method has been applied to the selective quantification of Cr(VI) in synthetic samples and waste-water samples with the satisfactory results.     

The interaction of cysteine with chromium(VI) ions under UV irradiation

In 0.1 M phosphate buffer (pH 7.2), the interaction of chromium(VI) with cysteine in the presence and absence of UV irradiation was studied by cyclic voltammetry and electronic spectroscopy techniques. The reduction of Cr(VI) by cysteine takes place through the formation of Cr(VI)-thioester intermediate. On the cyclic voltammograms of cysteine and Cr(VI) mixture, the peaks at -0.315 and -0.800 V were observed, and these peaks are corresponding to the reduction of Cr(VI)-thioester and thiyl radical, respectively. In the cysteine solution exposed to UV irradiation, the formation of free cystine was observed at -0.792 V. In the cysteine and Cr(VI) mixture exposed to UV irradiation, the peak current of thiyl radical increases while the peak current of Cr(VI)-thioester reaches a maximum at 15 min and then decreases by increasing UV irradiation time. The formation of the thioester in the reaction between Cr(VI) and cysteine in aqueous media has been studied by monitoring the decrease of Cr(VI) at 370 nm. It was observed that the reaction is catalyzed by the UV irradiation of the Cr(VI) and cysteine mixture.     

X-ray absorption and EPR spectroscopic studies of the biotransformations of chromium(VI) in mammalian cells. Is chromodulin an artifact of isolation methods?

Very different biological activities are usually ascribed to Cr(VI) (a toxin and carcinogen) and Cr(III) (an antidiabetic agent), although recent evidence suggests that both these types of actions are likely to arise from cellular uptake of varying concentrations of Cr(VI). The first systematic study of XANES spectra of Cr(III) complexes formed in Cr(VI)-treated mammalian cells (A549, HepG2, V79, and C2C12 cell lines), and in subcellular fractions of A549 cells, has been performed using a library of XANES spectra of model Cr(III) complexes. The results of multiple linear regression analyses of XANES spectra, in combination with multiple-scattering fits of XAFS spectra, indicate that Cr(III) formed in Cr(VI)-treated cells is most likely to bind to carboxylato, amine, and imidazole residues of amino acids, and to a lesser extent to hydroxo or aqua ligands. A combination of XANES and EPR spectroscopic data for Cr(VI)-treated cells indicates that the main component of Cr(III) formed in such cells is bound to high-molecular-mass ligands (>30 kDa, probably proteins), but significant redistribution of Cr(III) occurs during the cell lysis, which leads to the formation of a low-molecular-mass (<30 kDa) Cr(III)-containing fraction. The spectroscopic (XANES, XAFS, and EPR) properties of this fraction were strikingly similar to those of the purported natural Cr(III)-containing factor, chromodulin, that was reported to be isolated from the reaction of Cr(VI) with liver. These data support the hypothesis that a chromodulin-like species, which is formed from such a reaction, is an artifact of the reported isolation procedure.