汞离子天然吸附剂

汞离子是现代工业中剧毒的污染物之一,研究者致力于汞离子高效吸附剂的研制已有多年.本文基于国内外最新研究文献,系统论述了汞离子天然吸附剂如壳聚糖、矿物、微生物及其改性材料等的吸附性能,并详细比较了各种吸附剂的优缺点,指出天然吸附剂来源广泛、价格便宜,尤其是修饰后的壳聚糖吸附性能甚至可以和一些合成吸附剂相媲美.在所报道的天然吸附剂中,引入巯基后的戊二醛交联壳聚糖,对初始浓度为500 mg/L的汞离子的吸附容量可达1 604.7mg/g,属已知的汞离子天然吸附剂中之最.天然汞离子吸附剂在工业废水处理中显示出了广阔的应用前景.     

氨丙基硅三烷改性介孔二氧化硅及对痕量镉(Ⅱ)的分离富集性能研究

以氨丙基硅三烷作为改性剂,对介孔二氧化硅表面进行修饰,制备了氨基化介孔二氧化硅吸附材料,采用透射电镜和傅立叶红外光谱仪对其进行表征,并用于水样中痕量镉的富集,建立了氨基化介孔二氧化硅分离预富集/火焰原子吸收光谱法测定痕量镉的方法。考察了溶液pH值、样品流速、洗脱剂类型、干扰离子和吸附容量等对痕量镉分离富集的影响,以及该吸附材料对痕量镉(Ⅱ)的吸附性能。结果表明,溶液pH 7.0,样品流速8 m L/min时镉离子能被制备材料高效吸附,吸附的镉(Ⅱ)用5.0 m L 2 mol/L HNO_3完全洗脱,火焰原子吸收法测定。在最佳实验条件下,方法的线性范围为0.6~20 ng/m L,定量下限为0.5 ng/m L,富集倍数为50倍,对10 ng/m L Cd2+测定的相对标准偏差(n=11)为0.92%,加标回收率为98.8%~104.5%。该方法的抗干扰能力较好,富集柱可循环使用12次以上,可用于环境水样中镉(Ⅱ)的测定。     

活性炭富集-电热塞曼原子吸收光谱法测定水中痕量的汞

建立了一种水中痕量汞的测定方法。通过活性炭定量吸附水中痕量汞,采用电热塞曼原子吸收光谱法测定活性炭富集的汞。与目前水中总汞测定方法相比,本方法避免了消解等步骤,减少了汞污染和汞损失,操作更加简单。考察了活性炭粒度、酸处理方法、酸介质和富集时间对富集效率的影响,以及热解温度和干扰离子对方法测定结果的影响。通过空白活性炭加标、空白溶液加标和环境水样加标3种方法制作标准曲线,三者的相关系数达0.9999,经统计检验,3条标准曲线的斜率无差异,表明了在此实验条件下环境水样中的共存物不干扰汞的测定,同时也表明可直接用空白活性炭加标的方法进行标准曲线的绘制。采用本方法对含5和50 ng/L汞的水样进行测定,其相对标准偏差分别为7.2%和4.2%(n=11)。本方法测定下限达到1.2 ng/L。地表水和自来水样中添加10 ng/L汞的加标回收率在92.0%~103.0%之间。用 ICP-MS作对照,二者分析结果相符合,相对误差在2.9%~ 3.4%之间,表明本方法准确可靠、精密度好。     

有机-无机介孔材料对痕量汞的吸附性能的研究

研究了一种有机-无机介孔材料在分离富集和测定痕量汞中的应用,探讨了溶液pH、温度、洗脱条件及干扰离子对汞分离富集的影响,结果发现该材料对Hg的吸附具有较高的选择性和较大的吸附容量。在pH 3.2、温度为20±1℃条件下,汞可被该材料定量吸附。其静态饱和吸附容量为119.15 mg/g。吸附的汞可用浓HCl洗脱,用原子荧光法测定洗脱下来的汞。该方法测定汞的检出限达1.89×10-9g/L(3σ),相对标准偏差为2.7%(n=11,ρ=0.5 ng/mL),线性范围为0.005~5 ng/mL,加标回收率95.3%~104.5%。此法已应用于环境水样中痕量汞的测定。     

巯基微球富集用于近红外光谱同时定量分析微量汞(Ⅱ)和银(Ⅰ)离子

针对近红外光谱技术的检出限高和金属离子在近红外区无信号响应的问题, 合成了巯基聚倍半硅氧烷微球(PMPSQ), 用以高效富集水溶液中的微量汞(Ⅱ)和银(Ⅰ)离子. 通过金属离子与巯基官能团螯合从而获得相应的近红外信号响应, 采集吸附了金属离子的PMPSQ的近红外漫反射光谱, 采用偏最小二乘法建立了定量校正模型. 结果表明, 采用巯基微球富集结合近红外光谱技术可以同时测定水中浓度分别为0.16~1.80 mg/L的汞(Ⅱ)离子和0.15~1.70 mg/L的银(Ⅰ)离子.     

聚1,8-萘二胺修饰玻碳电极测定痕量汞

采用电化学聚合的方法制备了聚1,8-萘二胺修饰玻碳电极,建立了吸附富集-阳极溶出伏安法测定痕量Hg2+的新方法.优化了各种实验参数(如富集底液的pH,富集时间等),并考察了其它离子的干扰.在最佳实验条件下,Hg2+在0.001～0.1 mg/L及0.1～5.0 mg/L质量浓度范围内均与溶出峰电流成良好的线性关系,检出限为0.0005 mg/L.该法可用于实际工业废水中汞的测定.     

镀金石英砂富集-冷原子吸收光谱法测定环境空气中的汞

建立镀金石英砂富集–冷原子吸收光谱法测定环境空气中的汞。利用大气采样器采集空气样品,优化镀金石英砂工艺,使其与空气中的汞发生金汞齐反应,将大气中的汞进行富集,通过电热蒸发–直接进样,采用冷原子吸收光谱法测定。环境空气中汞含量在0~20 ng范围内与吸光度有良好的线性关系,相关系数大于0.999。采样量为60 L时,方法的检出限为0.001 3 ng/L,测量下限为0.005 2 ng/L。测定结果的相对标准偏差为1.7%~4.5%(n=7),样品的加标回收率为94.7%~102.8%。该方法操作简单,干扰小,检测效率高,适用于空气中汞的测定。     

吸附溶出伏安法测定痕量硒——铜离子对二溴代苤硒脑体系的增敏作用

本文发现Cu~(2+)离子对二溴代苤硒脑在悬汞电极上的吸附溶出行为有显著增敏作用,从而建立了灵敏度高、选择性好的测定痕量硒的吸附溶出伏安法。线性范围为0.02～50ng/ml,检出下限达5×10~(-4)ng/ml。本文初步探讨了Cu~(2+)的增敏机制。     

邻菲咯啉改性膨润土吸附水中镉离子的研究

通过邻菲咯啉改性膨润土,对水中镉离子进行吸附性能的研究.探讨了投加量、pH值、接触时间、温度等影响因素对改性膨润土吸附镉离子的影响.实验结果表明:在25℃,250 r/min,pH 5.5,NaNO3浓度0.01 mol/L,投加量为5.0 g/L,镉离子质量浓度100 mg/L的条件下,未改性膨润土对水中镉离子的吸附...     

微量铁的吸附伏安法测定

在NH_3-NH_4Cl-三乙醇胺底液中用5-Br-PADAP催化极谱法测定铁的检测下限为2.8×10~(-8)mol/L。本文利用吸附伏安法,先进行吸附富集,形成的Fe-5-Br-PADAP在HAc-NaAc介质中产生灵敏的络合吸附峰,将检测下限提高到4.0×10~(-10)mol/L。 实验采用悬汞电极、铂电极和饱和甘汞电极组成的三电极体系。1.0×10~(-2)mol/L含     

Simultaneous Determination of Tin,Nickel, Lead,Cadmium and Mercury in Tobacco and Tobacco Additives by Microwave Digestion and RP‐HPLC Followed by On‐Line Column Enrichment

A new method for the simultaneous determination of five heavy metal ions, tin, nickel, lead, cadmium and mercury ions as metal‐tetra‐(2‐aminophenyl)‐porphyrin (T₂APP) chelates was developed using reversed‐phase high performance liquid chromatography (RP‐HPLC) equipped with a photodiode array detector and combined with an on‐line enrichment technique. The tin, nickel, lead, cadmium and mercury ions were pre‐column derivatized with T₂APP to form color chelates. The Sn‐T₂APP, Ni‐T₂APP, Hg‐T₂APP, Cd‐T₂‐APP and Pb‐T₂APP chelates can be absorbed onto the front of the enrichment column when they are injected into the injector and sent to the enrichment column [Waters Xterra? RP₁₈(5μ, 3.9 × 20 mm)] with a buffer solution of 0.05 mol/L pyrrolidine‐acetic acid (pH = 10.0) as mobile phase. After the enrichment had finished, by switching the six‐port switching valves, the retained chelates were back‐flushed by mobile phase and traveling towards the analytical column. These chelates separation on the analytical column [Waters Xterra? RP₁₈ (5μ, 3.9 × 150 mm)] was satisfactory by gradient elution with methanol (containing 0.05 mol/L pyrrolidine‐acetic acid buffer salt, pH = 10.0) and acetone (containing 0.05 mol/L pyrrolidine‐acetic acid buffer salt, pH = 10.0) as mobile phase. The linearity range is 0.01?120 μg/L for each metal ion. The detection limits (S/N = 3) of tin, nickel, lead, cadmium and mercury are 4.0 ng/L, 3.5 ng/L, 2.5 ng/L, 3.0 ng/L and 3.0 ng/L, respectively. This method was applied to the determination of tin, nickel, lead, cadmium and mercury ions in tobacco and tobacco additives with good results.     

Critical Evaluation of Adsorption–Desorption Hysteresis of Heavy Metal Ions from Carbon Nanotubes: Influence of Wall Number and Surface Functionalization

Single‐, double‐, and multi‐walled carbon nanotubes (SWCNTs, DWCNTs, and MWCNTs), and two oxidized MWCNTs with different oxygen contents (2.51 wt % and 3.5 wt %) were used to study the effect of the wall number and surface functionalization of CNTs on their adsorption capacity and adsorption–desorption hysteresis for heavy metal ions (Ni^II, Cd^II, and Pb^II). Metal ions adsorbed on CNTs could be desorbed by lowering the solution pH. Adsoprtion of heavy metal ions was not completely reversible when the supernatant was replaced with metal ion‐free electrolyte solution. With increasing wall number and amount of surface functional groups, CNTs had more surface defects and exhibited higher adsorption capacity and higher adsorption–desorption hysteresis index (HI) values. The coverage of heavy metal ions on the surface of CNTs, solution pH, and temperature affect the metal ion adsorption–desorption hysteresis. A possible shift in the adsorption mechanism from mainly irreversible to largely reversible processes may take place, as the amount of metal ions adsorbed on CNTs increases. Heavy metal ions may be irreversibly adsorbed on defect sites.     

Aligned nanogold assisted one step sensing and removal of heavy metal ions

We depict a novel strategy exploiting the chemistry of metal ion adsorption for detection and sequestration of toxic heavy metal from processed water using gold nanoparticles capped with 4-aminothiophenol. The interaction between 4-aminothiophenol capped gold nanoparticles and heavy metal ions was studied as a function of time and concentration using TEM, HRTEM, SEM, EDS, and I-V characterization. Experiments confirmed that pH is one of the crucial controlling parameters. Adsorption capacity was monitored using AAS, UV-vis spectroscopy and I-V measurement. In the absence of any alloy formation between Au and heavy metal ions, the desorption of the heavy metal ions from 4-aminothiophenol capped gold nanoparticles surface by pH modulation serves as a mean of collection of heavy metal ions. Experiments revealed that the concentration of heavy metal ions in processed water after adsorption is below the maximum permissible limit set by the WHO.     

微囊化海藻酸离子移变凝胶的制备、结构与性能

通过静电脉冲技术制备了海藻酸-壳聚糖-海藻酸(Alginate-Chitosan-Alginate,ACA)微胶囊,红外光谱分析表明,ACA是一种以聚电解质配合物为囊膜,以海藻酸钠离子吸附剂为囊心物的微胶囊型离子吸附体系.扫描电镜测试表明,ACA吸附重金属离子的过程是微胶囊囊内海藻酸凝胶化的过程,其解吸附过程是海藻酸凝胶转变成海藻酸溶液的过程.与传统离子交换树脂相比,ACA对Pb²⁺的吸附具有较高的去除率、很强的富集能力和较低的极限吸附浓度,并且能够被多次重复使用.ACA的离子交换速率比传统离子交换树脂快得多,离子交换过程中,交换离子和吸附剂海藻酸分子的相互扩散大大提高了离子交换速率.     

Simultaneous determination of four heavy metal ions in tobacco and tobacco additive by online enrichment followed by RP-HPLC and microwave digestion

A new method for the simultaneous determination of tin, lead, cadmium, and mercury in tobacco and tobacco additive by reversed-phase high-performance liquid chromatography combined with microwave digestion and an online enrichment technique is developed. The tin, lead, cadmium, and mercury ions are precolumn derivatized with tetra-(4-dimethylaminophenyl)-porphyrin (T(4)-DMAPP) to form color chelates. The Sn-T(4)-DMAPP, Hg-T(4)-DMAPP, Cd-T(4)-DMAPP, and Pb-T(4)-DMAPP chelates are absorbed onto the front of the enrichment column using a buffer solution of 0.05 mol/L pyrrolidine-acetic acid (pH = 10.0) as the mobile phase. After the concentration is finished (by switching the six-port switching valve) the retained chelates are back-flushed by the mobile phase and move to the analytical column. The chelate separation on the analytical column is satisfactory using gradient elution with methanol (containing 0.05 mol/L pyrrolidine-acetic acid buffer salt, pH = 10.0) and tetrahydrofuran (containing 0.05 mol/L pyrrolidine-acetic acid buffer salt, pH = 10.0). The linearity range is 0.01-120 micro g/L for each metal ion. The detection limits (S/N = 3) of tin, lead, cadmium, and mercury are 0.6, 0.8, 0.5, and 0.6 ng/L, respectively. This method is applied to the determination of tin, lead, cadmium, and mercury in tobacco and it's additive with good results.     

Preparation of a clay-modified carbon paste electrode based on 2-thiazoline-2-thiol-hexadecylammonium sorption for the sensitive determination of mercury.

A montmorillonite from Wyoming-USA was used to prepare an organo-clay complex, named 2-thiazoline-2-thiol-hexadecyltrimethylammonium-clay (TZT-HDTA-clay), for the purpose of the selective adsorption of the heavy metals ions and possible use as a chemically modified carbon paste electrode (CMCPE). Adsorption isotherms of Hg2+, Pb2+, Cd2+, Cu2+, and Zn2+ from aqueous solutions as a function of the pH were studied at 298 K. Conditions for quantitative retention and elution were established for each metal by batch and column methods. The organo-clay complex was very selective to Hg(II) in aqueous solution in which other metals and ions were also present. The accumulation voltammetry of Hg(II) was studied at a carbon paste electrode chemically modified with this material. The mercury response was evaluated with respect to the pH, electrode composition, preconcentration time, mercury concentration, "cleaning" solution, possible interferences and other variables. A carbon paste electrode modified by TZT-HDTA-clay showed two peaks: one cathodic peak at about 0.0 V and an anodic peak at 0.25 V, scanning the potential from -0.2 to 0.8 V (0.05 M KNO3 vs. Ag/AgCl). The anodic peak at 0.25 V presents excellent selectivity for Hg(II) ions in the presence of foreign ions. The detection limit was estimated as 0.1 microg L(-1). The precision of determination was satisfactory for the respective concentration level.     

沉淀/共沉淀-膜富集-X射线荧光法快速分析近岸海水中的重金属

建立了近岸海水中多种重金属(铁、镍、锰、铜、锌及铅)的氢氧化物和硫化物的沉淀/共沉淀-膜富集-X射线荧光测定法.在海水样品中加入沉淀剂,使重金属离子生成氢氧化物或硫化物沉淀.沉淀经过滤截留,富集在膜上,直接以手持式X射线荧光仪检测.富集100 mL水样时,两种沉淀法的测定线性范围均为12.5～400 μg/L,即测定限均为12.5 μg/L.对各重金属浓度为100μg/L的试样连续测定7次,相对标准偏差(RSD)为3.7％～6.4％;氢氧化物沉淀法的检出限在1.32～7.84 μ g/L之间;硫化物沉淀法为1.94～11.0 μg/L.用本方法成功测定了厦门近岸海域及九龙江河口海水中的重金属浓度.基于样品酸化与否及过滤先后顺序的不同,本方法可用于海水和河口水样中可溶态、溶解态及游离态重金属的现场快速分析.     

Electrochemical performance of a three-layer electrode based on Bi nanoparticles,multi-walled carbon nanotube composites for simultaneous Hg(II) and Cu(II) detection

Electrochemical analysis is a promising technique for detecting biotoxic and non-biodegradable heavy metals. This article proposes a novel composite electrode based on a polyaniline (PANi) framework doped with bismuth nanoparticle@graphene oxide multi-walled carbon nanotubes (Bi NPs@GO-MWCNTs) for the simultaneous detection of multiple heavy metal ions. Composite electrodes are prepared on screen-printed electrodes (SPCEs) using an efficient dispensing technique. We used a SM200SX-3A dispenser to load a laboratory-specific ink with optimized viscosity and adhesion to draw a pattern on the work area. The SPCE was used as substrate to facilitate cost-effective and more convenient real-time detection technology. Electrochemical techniques, such as cyclic voltammetry and differential pulse voltammetry, were used to demonstrate the sensing capabilities of the proposed sensor. The sensitivity, limit of detection, and linear range of the PANi-Bi NPs@GO-MWCNT electrode are 2.57 × 10² μA L μmol⁻¹ cm⁻², 0.01 nmol/L, and 0.01 nmol/L–5 mmol/L and 0.15 × 10⁻¹ μA L μmol⁻¹ cm⁻², 0.5 nmol/L, and 0.5 nmol/L–5 mmol/L for mercury ion (Hg(II)) and copper ion (Cu(II)) detection, respectively. In addition, the electrode exhibits a good selectivity and repeatability for Hg(II) and Cu(II) sensing when tested in a complex heavy metal ion solution. The constructed electrode system exhibits a detection performance superior to similar methods and also increases the types of heavy metal ions that can be detected. Therefore, the proposed device can be used as an efficient sensor for the detection of multiple heavy metal ions in complex environments.     

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。     

Adsorption of cadmium ions from aqueous solutions using nano-montmorillonite: kinetics,isotherm and mechanism evaluations

With increasing industrial development, heavy metal pollution, e.g., cadmium (Cd) pollution, is increasingly serious in soil and water environments. This study investigated the sorption performance of nano-montmorillonite (NMMT) for Cd ions. Adsorption experiments were carried out to examine the effects of the initial metal ion concentration (22.4–224 mg/L), pH (2.5–7.5), contact time (2–180 min) and temperature (15–40 °C). A simulated acid rain solution was prepared to study the desorption of Cd adsorbed on NMMT. After the adsorption or desorption process, the supernatant was analyzed using a flame atomic absorption spectrometry method. The Cd removal rate increased as the pH and contact time increased but decreased as the initial metal ion concentration increased. The maximum adsorption capacity was estimated to be 17.61 mg/g at a Cd²⁺ concentration of 22.4 mg/L. The sorption process can be described by both the Langmuir and Freundlich models, and the kinetic studies revealed that the pseudo-second-order model fit the experimental data. The Cd desorption rate when exposed to simulated acid rain was less than 1%. NMMT possesses a good adsorption capacity for Cd ions. Additionally, ion exchange was the main adsorption mechanism, but some precipitation or surface adsorption also occurred.