磁性壳聚糖微球的制备及对Cr(Ⅵ)的吸附性能研究

用壳聚糖包埋磁流体,用戊二醛交联制成磁性壳聚糖微球,并用红外光谱表征其结构。用制备的磁性壳聚糖微球吸附Cr(Ⅵ)离子,考察了其对Cr(Ⅵ)离子的吸附性能;探讨了吸附时间、溶液pH值、吸附剂用量、温度、Cr(Ⅵ)起始浓度以及其他离子存在对Cr(Ⅵ)离子去除率的影响。实验结果表明,磁性壳聚糖微球吸附Cr(Ⅵ)离子的最佳条件为:吸附平衡时间40 min,最佳吸附pH值6左右,磁性壳聚糖微球用量10 mg,温度升高有利于提高磁性壳聚糖微球的吸附效率,Cr(Ⅵ)离子起始质量浓度为12μg/mL,无机盐的存在引起磁性壳聚糖微球的吸附性能降低。并且考察了吸附剂的再生性能,实验结果表明磁性壳聚糖微球具有良好的重复使用性。     

单宁微球对Cr（Ⅵ）的吸附性能

利用单宁微球吸附Cr（Ⅵ）,探讨了温度、pH值、Cr（Ⅵ）初始质量浓度等因素对单宁微球吸附性能的影响,并分析了其吸附等温曲线。结果表明,单宁微球对Cr（Ⅵ）具有很好的吸附效果,吸附量可达到45.5 mg/g。单宁微球对Cr（Ⅵ）的去除率随吸附时间的延长而增大,5 h后基本达到平衡。温度对单宁微球吸附Cr（Ⅵ）的影响比较...     

微流控技术制备磁性聚合物微球及对孔雀石绿的吸附性能研究

以单分散液滴为模板,通过紫外光引发自由基聚合的方法,用微流控技术制备出单分散甲基丙烯酸甲酯/苯乙烯/四氧化三铁磁性聚合物微球,制备装置简易、操作简单.对样品的形貌结构、粒度分布、表面官能团、组成成分、有效磁含量及表面电势进行了表征分析.微球的粒径约为200μm,单分散性良好,且表面电势为-24 mV时能够迅速对水体中的阳离子染料孔雀石绿进行有效吸附分离.探究了pH、孔雀石绿溶液初始浓度、吸附时间和反应温度对吸附效率的影响,发现在孔雀石绿溶液体积为50 mL(50 mg·L^-1),投加量为50 mg, pH为7,温度为30℃时吸附效率高达94.38%,重复利用9次的吸附效率仍可达到80%以上,具有较好的吸附能力.     

一种新型交联羧甲基葡甘聚糖微球对Cr(Ⅵ)的吸附性能研究

通过Fe3+交联羧甲基葡甘聚糖制得了一种新型羧甲基葡甘聚糖凝胶球,研究了羧甲基葡甘聚糖铁凝胶球对Cr(Ⅵ)的吸附性能。分别考察了吸附时间、羧甲基葡甘聚糖浓度、FeCl3浓度、pH值、温度、Cr(Ⅵ)浓度和微球粒径对吸附的影响,同时用红外光谱初步表征了羧甲基葡甘聚糖铁凝胶球-Cr(Ⅵ)复合物的结构。结果表明,293K时,微球对Cr(Ⅵ)的吸附反应在12h时达平衡,当羧甲基葡甘聚糖质量分数为1.0%,FeCl3质量分数为1.0%,Cr(Ⅵ)浓度为400mg/L时,吸附量达到0.4385mmol/g。根据不同温度下微球吸附Cr(Ⅵ)的等温线,计算了吸附过程的热力学参数,同时用Freundlich方程对实验数据进行了拟合,发现该方程适用于所研究的吸附体系。该体系为自发放热过程,体系熵减少,降温有利于吸附。     

微流控法制备的多孔微球对Cr(Ⅵ)的吸附性能

利用玻璃毛细管搭建单级微流控装置制备单分散水包油(O/W)乳液,以乳液为模板,紫外光照射乳液引发自由基聚合,成功制备了单分散聚(甲基丙烯酸甲酯/甲基丙烯酸二甲氨基乙酯)[P (MMA/DMAEMA)]多孔微球。微球粒径偏差系数(CV)值小于5%,单分散性良好。研究P (MMA/DMAEMA)多孔微球对Cr(Ⅵ)的吸附性能、再生吸附性能、吸附机理。结果表明,p H对微球吸附Cr(Ⅵ)有较大影响,当pH=3时,微球对Cr(Ⅵ)的吸附率达到52. 9%,循环4次后其吸附性能基本不变;微球的吸附符合准二级动力学模型,属于化学吸附;微球等温吸附符合Langmuir模型,属于单分子层吸附。     

多孔聚离子液体-对二乙烯基苯聚合物材料的合成与吸附Cr(Ⅵ)性能研究

为了获得孔道更加稳定、比表面积较大的聚离子液体,向咪唑离子液体中引入刚性基团苯环,成功得到BET比表面积约为200 m~2·g~(-1)左右的介孔型聚离子液体材料,对实验所得的产物聚离子液体-对二乙烯基苯进行了性质与结构的表征。并将PIL-DVB应用于Cr(Ⅵ)的吸附,进行了吸附等温线、吸附动力学的研究,其对Cr(Ⅵ)的吸附量可达到273 mg·g~(-1),通过实验与计算结合的方法对吸附机理进行了探究。     

不同类型阴离子交换树脂对Cr(Ⅵ)的吸附性能研究

通过静态吸附实验、动力学实验,从3种吸附去除Cr(Ⅵ)的离子交换树脂中优选出DEX-Cr树脂,研究了pH、温度对其交换性能的影响,进一步对树脂的动态吸附-再生性能和重复使用稳定性进行了考察。结果表明DEX-Cr树脂对Cr(Ⅵ)的吸附去除效果好,且重复使用稳定性高,可以作为分离去除Cr(Ⅵ)的高效吸附剂。     

微流控液滴软模板制备二氧化钛中空微球

应用微流控液滴技术合成功能材料已发展成为一个新兴领域。本文以夹流结构微流控芯片产生的微液滴作为软模板,以液滴模板界面处发生的水解反应生成二氧化钛球壳,并经后续脱核处理,制备二氧化钛中空微球。采用激光诱导荧光成像、扫描电镜等手段对微球形貌结构进行了分析表征。结果表明,通过控制微流控芯片液滴合成条件,可以得到壁厚约2 μm的二氧化钛中空微球。这种以微流控液滴为模板的合成方法简单灵活,若与其他材料改性方法相结合,有望实现对更多元、更复杂功能微球材料的制备,并进一步拓宽其在光电和催化剂材料领域的应用。     

沉淀剂对水热法制备分等级氧化铁纳米结构及其Cr(Ⅵ)吸附性能的影响

以硫酸铁为铁源、硫脲、氟化钠和尿素分别为沉淀剂,采用水热法成功地制备了分等级微米级球状氧化铁粒子、六方柱状粒子相互交织的微米级氧化铁团聚体等。采用X射线衍射、扫描电镜、N2吸附-脱附、磁滞回线和UV紫外分光光度计等测试手段,对比研究了上述沉淀剂对产物微结构、形貌、织构性质及其对剧毒Cr(Ⅵ)吸附性能的影响。结果表明,以硫脲为沉淀剂制得氧化铁的结晶度最高,其晶粒大小为49.7nm,并具有最高的比表面积13.0m2·g-1、最大的孔容0.092cm3·g-1和平均孔径28.6nm;该氧化铁具有最佳的Cr(Ⅵ)吸附性能,30min即达到吸附平衡,饱和吸附量达202.8mg·g-1,并且符合Langmuir单分子层吸附模型;该氧化铁还具有一定的磁性,通过外加磁场可以实现吸附Cr(Ⅵ)后的吸附剂与溶液的彻底分离,因而在重金属废水处理领域显示出良好的应用前景。     

Cr(Ⅵ)离子在CdS催化剂上的吸附及光催化还原

Cr(Ⅵ)在CdS光催化剂上具有较强的暗态吸附,适当的热处理会增强Cr(Ⅵ)离子的吸附;在未经热处理的CdS催化剂上,Cr(Ⅵ)的吸附表现为接近于一个吸附单层的特征,而当催化剂经过了300℃的热处理,Cr(Ⅵ)离子在催化剂表面上的吸附会增加,吸附表现为超过一个单层的特征。热处理过程同样会增加催化剂的光催化活性。对于整个光催化反应而言,吸附过程是反应的控制步骤。Cr(Ⅵ)的光催化还原伴随CdS催化剂的光腐蚀。     

Preparation of cross‐linked porous starch and its adsorption for chromium (VI) in tannery wastewater

Various cross‐linked amino starches were used for chromium (VI) adsorption in the environmental protection area. In order to improve chromium (VI) adsorption, the new cross‐linked amino starch with porous structure (CPS) was synthesized by reverse emulsion polymerization, using waxy corn starch after enzyme hydrolysis (ES) as raw material, N,N′‐methylene‐bis‐acrylamide (MBAA) as cross‐linking agent, and ceric ammonium nitrate as initiator. The effects of the volume ratio of oil phase/aqueous phase, the content of emulsifiers, ES, and MBAA on the swelling, solubility property, chromium (VI) adsorption capacity, grafting ratio, and conversion ratio of CPS were investigated. The properties and morphology of CPS have been characterized by Fourier transform infrared spectroscopy, thermal gravimetric analysis, differential scanning calorimetry, and scanning electron microscopy. The maximum adsorption capacity for chromium (VI) ions of CPS reached 28.83 mg/g when the synthesis condition of CPS was controlled as V_oil: V_H2O 8:1, emulsifier 9%, starch 2%, and MBAA 10%. The new adsorption peaks of CPS at 1641 cm^?1 and 1541 cm^?1 proved the cross‐linking reaction between ES and MBAA. The thermal decomposition temperature of CPS was improved to 250°C, and the gelatinization temperature and enthalpy value of CPS were decreased compared with ES because of the occurrence of the cross‐linking reaction. The CPS was like a sponge with a large amount of pores, and the size of these pores was 5 µm. CPS also exhibited superior adsorption property to other heavy metal ions such as cadmium (II) and lead (II) (17.37 and 35.56 mg/g). Copyright © 2015 John Wiley & Sons, Ltd.     

Preparation of FeS/iron oxide composite and flax stem‐based porous carbon and its Cr(VI) removal ability

Using flax stem and ferrous sulfate, a composite porous carbon material was prepared by means of high‐temperature roasting and a one‐step process in a muffle furnace. The samples were characterized using X‐Ray diffraction (XRD) and Scanning electron microscopy (SEM), and the effects of ferrous sulfate concentration, carbonization temperature, and pH values of Cr(VI) aqueous solution on the removal performance of Cr(VI) were studied. XRD and SEM analysis showed that the prepared samples were amorphous porous carbon loaded with FeS/Fe₂O₃/Fe₃O₄. High FeSO₄ impregnation concentration, high carbonization temperature, and a low pH value of Cr(VI) aqueous solution were beneficial for Cr(VI) removal. When pH = 2, the amount of Cr(VI) removal was 99.93 mg/g by the sample obtained from 1 g flax powder impregnated in 4.5 mmol FeSO₄/40 mL H₂O solution and calcined for 2 hr at 800°C.     

Determination of Cr(III) and Cr(VI) in industrial and environmental liquid samples by EDXRF method

A rapid, sensitive and selective procedure for determination of Cr(III) and Cr(VI) in environmental and industrial liquid samples via preconcentration with ammonium pyrrolidine dithiocarbamate (APDC) and determination by means of the EDXRF was described. The effect of pH in the range of 3-11 on the recovery of Cr(III) and Cr(VI) has been investigated separately and in combination of these two species. The influence of organic matter, carbonate species and elements V, Mn and Fe on the recovery of each chromium specie (separately/in combination) over whole pH range was also tested in order to simulate condition occurring in natural waters that usually contain certain amount of dissolved organic matter and carbonate ions. Cr(VI) and Cr(III) have shown different behaviors in reaction with APDC at different pH ranges and therefore it is possible to separate those two species. It was found that Cr(VI) creates complex with APDC only in the pH range from 3 to 5 with quantitative recovery (app. 98%) at pH 3, but there was no recovery of Cr(III) at that pH. On the contrary, in pH range from 6 to 11, reaction with Cr(III) and APDC reviled that the only reaction product is Cr(OH)₃ instead of the expected Cr(III)-APDC complex. All reaction products were characterized by IR spectroscopy.     

Chemically selective membrane optode for Cr(VI) determination in aqueous samples

A methodology for simultaneous preconcentration and determination of Cr(VI) from aqueous samples was developed using a membrane optode formed by physical inclusion of a Cr(VI) selective chromophore 1,5-diphenylcarbazide (DPC) into a plasticized cellulose triacetate matrix. The inclusion of an anion exchanger (Aliquat-336) was found to be effective for immobilization of both DPC and Cr(VI)-DPC complex in the optode matrix itself. The proportionality in intensity of the magenta color on the optodes loaded with varying amounts of Cr(VI) suggests its potential applications for screening of Cr(VI) in aqueous samples by visual colorimetry. On loading high amounts of Cr(VI) in the membrane optode, its color changes from magenta to yellow, which indicates the possibility of using it as a threshold detector for Cr(VI). The membrane optode was optimized in terms of obtaining maximum preconcentration efficiency for Cr(VI) and subsequent stable optical response proportional to the amount of Cr(VI) in the membrane optode sample. The membrane optodes were tested for Cr(VI) determination in tap water and seawater samples. Using this optode, Cr(VI) even at levels of 13.6 ppb could be quantitatively detected. The optodes developed in the present work were found to be stable, cost effective, easy to prepare and efficient for direct preconcentration and determination of Cr(VI) in a variety of aqueous samples using spectrophotometry. However, this membrane optode is for one time use only as the reaction of Cr(VI) with DPC is irreversible.     

Amperometric Determination of Cr(III) and Cr(VI) by Flow Injection Analysis

Speciation of Cr(III) and Cr(VI) can be attained by flow injection analysis with amperometric detection. Cr(VI) is reduced in an acidic medium to Cr(III) with a glassy carbon electrode at —0.1 V vs. Ag/AgCl and the current is recorded. Cr(III) is oxidised on-line to Cr(VI) with alkaline hydrogen peroxide solution. From the difference of the total chromium and Cr(VI), the amount of Cr(III) was obtained. A linear calibration curve for Cr(VI) was obtained for the concentration ranges 0.01-5.0ppm of Cr(VI) and we have calculated the limit of determination to be about 0.5ppb. We have studied the degree of reproducibility obtained using the solid electrodes under various conditions. The influence of flow rate, coil length, interfenences and the extent of reaction were studied.     

Determination of Cr(VI) in the presence of Cr(III) and humic acid by cathodic stripping voltammetry

A voltammetric procedure in the flow system for determination of traces of Cr(VI) in the presence of Cr(III) and humic acid is presented. The calibration graph is linear from 5×10⁻¹⁰ to 1×10⁻⁷ mol l⁻¹ for an accumulation time of 120 s. The R.S.D. for 1×10⁻⁸ mol l⁻¹ Cr(VI) is 5.3% (n=5). The detection limit estimated from 3σ for a low concentration of Cr(VI) and accumulation time of 120 s is 2×10⁻¹⁰ mol l⁻¹. The method can be used for Cr(VI) determination in the presence of up to 50 mg l⁻¹ of humic acid. The validation of the method was carried out by studying the recovery of Cr(VI) from spiked river water and by the comparison of the results of determination of Cr(VI) in a soil sample. The method cannot be used for analysis of samples containing high concentrations of chloride ions such as seawater and estuarine water.     

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.     

Selective flow injection analysis of ultra-trace amounts of Cr(VI), preconcentration of it by solvent extraction, and determination by electrothermal atomic absorption spectrometry (ETAAS)

A rapid, robust, sensitive and selective time-based flow injection (FI) on-line solvent extraction system interfaced with electrothermal atomic absorption spectrometry (ETAAS) is described for analyzing ultra-trace amounts of Cr(VI). The sample is initially mixed on-line with isobutyl methyl ketone (IBMK). The Cr(VI) is complexed by reaction with ammonium pyrrolidine dithiocarbamate (APDC), and the non-charged Cr(VI)–PDC chelate formed is extracted into IBMK in a knotted reactor made from PTFE tubing. The organic extractant is separated from the aqueous phase by a gravity phase separator with a small conical cavity and delivered into a collector tube, from which 55 μl organic concentrate is subsequently introduced via an air flow into the graphite tube of the ETAAS instrument. The operations of the FI-system and the ETAAS detector are synchronously coupled. A significant advantage of the approach is that matrix constituents, such as high salt contents, effectively are eliminated. The extraction procedure was optimized by a simplex approach. A central composite design was subsequently employed to verify the estimated operational optimum. An 18-fold enhancement in sensitivity of Cr(VI) was achieved after preconcentration for 99 s at a sample flow rate of 5.5 ml min⁻¹, as compared to direct introduction of 55 μl of sample, yielding a detection limit (3σ) of 3.3 ng l⁻¹. The sampling frequency was 24.2 samples h⁻¹. The proposed method was successfully evaluated by analyzing a NIST Cr(VI)-reference material, synthetic seawater and waste waters, and waste water samples from an incineration plant and a desulphurization plant, respectively.     

石墨烯负载零价纳米铁材料的合成及去除水中Cr(VI)的研究

以石墨粉为原料,采用改良Hummers方法合成石墨烯,然后通过液相还原法制备出石墨烯负载纳米铁材料(Graphene-supported nanoscale zero-valent iron,G-nZVI),借助扫描电子显微镜(SEM)、红外光谱分析仪(FTIR)进行表征,并以G-nZVI为反应材料,研究其对水体中Cr(VI)的去除效率,结果显示:室温下,当G-nZVI投加量为0.4g/L,Cr(VI)的初始浓度为20 mg/L,初始pH值为3.0时,Cr(VI)的去除率在2h内可以达到95%以上。G-nZVI具有磁性,使用后可通过外加磁力除去,以防对水体的二次污染,具有较好的应用前景。     

Removal of Cr (VI) from aqueous solution using magnetic biochar synthesized by a single step method

Magnetic biochar, as an adsorbent, was synthesized by a single step method, where iron salt was directly mixed with pinewood sawdust by chemical co-precipitation and subsequently pyrolyzed at 700°C for Cr (VI) removal from aqueous solution. The effects of some important parameters including adsorbent dosage (0.4–2.8?g/L), pH (1–10) of the solution, contact time (0–1440 minutes), initial concentration (30–120?mg/L), and temperature (20–40°C) were investigated in batch experiments. Both pre- and post-adsorbents were characterized by SEM-EDX and XPS to investigate the adsorption mechanism. The maximum adsorption capacity of the tested magnetic biochar under the certain experimental conditions determined as optimal was 42.7?mg/g for Cr (VI). The adsorption data were proved to be suitable for the pseudo-second order model for kinetics and the Langmuir model for isotherms with correlation R²?=?0.9996 andR²?>?0.9980, respectively, after fitting with four kinetic models (pseudo-first order, pseudo-second order, W-M model, and Elovich) and three isotherm models (Langmuir, Freundlich, and Temkin). The characteristic analyses further verified that the efficient particle was a mixture of iron oxides in essence, and it had a strong effect on the spontaneous and endothermic adsorption process.