金属有机框架MIL-101(Fe)对水中微囊藻毒素-LR的吸附

通过溶剂热法制备了性质稳定的金属有机框架材料MIL-101(Fe),并用于吸附去除水中的微囊藻毒素-LR。采用电子显微镜、傅立叶变换红外光谱(FT-IR)、Zeta电位和N_2吸附-脱附等方法对制备的纳米材料进行了表征。MIL-101(Fe)具有多孔结构和较高的比表面积(375.2 m~2/g),尺寸约为500 nm。考察了pH值、离子强度、温度、吸附时间、浓度等参数对吸附剂吸附能力的影响。结果表明,静电作用和配位作用是主要的作用机理。MIL-101(Fe)对微囊藻毒素-LR的吸附速度很快(20 min内达到吸附平衡),吸附过程符合准二级动力学模型;MIL-101(Fe)对微囊藻毒素-LR表现出良好的吸附性能,其最大吸附量为256.4 mg/g。溶液中存在的腐植酸对MIL-101(Fe)的吸附性能产生一定的影响。受腐殖酸、盐类的影响,相同条件下MIL-101(Fe)对江水中微囊藻毒素-LR的吸附性能有所下降,但仍可达到68.1 mg/g。因此,该方法简便、高效,适用于快速除去污染水体中的微囊藻毒素-LR。     

Ce/Zr/Al类水滑石的合成、表征及其吸附性能研究

本研究对Ce/Zr/Al三元类水滑石材料去除微囊藻毒素(MC)的潜在应用进行了探索。采用共沉淀法合成了碳酸根型Ce/Zr/Al三元类水滑石,通过XRD、IR等手段对样品进行了测试和表征。合成的类水滑石用于吸附MC,并详细研究了其对MC的吸附性能。结果显示,控制反应条件为温度80℃,M3+/M4+摩尔投料比为1∶1,pH为8.5,合成的Ce/Zr/Al三元类水滑石对MC具有较高的吸附性能,对微囊藻毒素LR(MC-LR)最大吸附量可达178μg/g,对MC-LR和微囊藻毒素RR(MC-RR)的吸附效率均大于70%,吸附性能明显高于硅胶等常用吸附剂。这些研究数据表明Ce/Zr/Al三元类水滑石对去除水体中微囊藻毒素具有潜在的应用价值。     

CoFe_2O_4纳米粒子对水中微囊藻毒素的去除

通过一步溶剂热合成法制备出Co Fe2O4,Fe3O4,Cu Fe2O43种磁性纳米粒子,将其用于水中生物污染物微囊藻毒素的去除,通过高效液相色谱法检测微囊藻毒素浓度。上述3种磁性粒子中,Co Fe2O4对微囊藻毒素具有最强的吸附性能。采用透射电子显微镜、红外光谱、磁滞回线和X-射线衍射等方法对Co Fe2O4纳米粒子进行表征,Co Fe2O4具有良好的磁性和分散性,粒径约为250 nm。由于具有较强的磁性,Co Fe2O4及吸附于表面的微囊藻毒素可通过施加外加磁场而从溶液中分离。考察了生物污染物初始浓度、溶液酸度、温度、离子强度和水中天然有机物浓度等条件对Co Fe2O4吸附性能的影响。结果显示,较高的分析物浓度与实验温度、较低的p H值及离子强度更有利于微囊藻毒素在磁性粒子表面的吸附。低浓度(0~2.5 mg/L)的腐植酸几乎不影响Co Fe2O4对微囊藻毒素的吸附,而较高浓度的腐植酸使得Co Fe2O4的吸附性能显著下降。静电作用和配位作用在Co Fe2O4吸附毒素的过程中起着重要作用。研究表明,Co Fe2O4纳米粒子的制备方法简单,具有较强的磁场响应性及良好的单分散性,在水环境中生物污染物的去除方面具有优越的应用前景。     

微囊藻毒素的2-甲基-3-甲氧基-4-苯基丁酸检测方法的研究

2甲-基-3-甲氧基-4-苯基丁酸(MMPB)法是检测微囊藻毒素(Microcystins,MC)的重要方法之一。本文研究了温度、pH值、反应时间和氧化剂浓度等实验参数的影响,并在优化条件下采用气相色谱法对水中的微囊藻毒素进行检测。实验得到的最佳反应条件为:pH=9,初始反应温度2℃反应1 h,再升温至25℃反应2 h;KMnO4的初始浓度为0.0156 mol/L。本法对水溶液中的微囊藻的检出限为0.0225μg,回收率为93.5%。     

330阴离子交换树脂对草甘膦的吸附性能

采用静态吸附法研究了330阴离子交换树脂对水中草甘膦的吸附性能,并研究了吸附动力学;测定了溶液的pH值、温度、NaCl含量等因素对330树脂吸附草甘膦的影响.结果表明:330树脂对水中草甘膦的吸附速率快;在pH=2.69时对草甘膦的吸附性能最好;330树脂对草甘膦的吸附是放热、自发的过程,吸附等温线符合Freundli...     

基于石墨烯和金纳米笼修饰的无标记型微囊藻毒素免疫传感器的研制

利用石墨烯及中空结构的金纳米笼构建了无标记型电化学免疫传感器,并用于微囊藻毒素的检测。利用多元醇还原法合成制备了导电性好、催化性强、生物相容性好的金纳米笼;再利用高分散的石墨烯将其固定于玻碳电极表面,进一步吸附固定微囊藻毒素抗体。在无微囊藻毒素存在时,电化学探针[Fe(CN)6]3!/4!在传感器界面上能获得较高的电流响应信号。当培育了微囊藻毒素后,抗体与微囊藻毒素形成免疫结合物,增加了电极表面的电荷密度和传质阻力,阻碍[Fe(CN)6]3!/4!扩散到电极表面,导致[Fe(CN)6]3!/4!的电流响应信号明显降低,电流减小的程度间接地与微囊藻毒素的浓度成比例,可实现对微囊藻毒素的检测。实验考察了抗原培育时间,抗体浓度等条件对该传感器响应性能的影响。结果表明,此传感器对微囊藻毒素的线性响应范围为0.05~1000μg/L,检出限为0.017μg/L,优于文献报道。此传感器操作简单,并且具有良好的稳定性,将其用于实际水样中微囊藻毒素的检测,平均加标回收率为94.1%。     

水产品中微囊藻毒素检测方法的研究进展

微囊藻毒素是蓝藻暴发中出现频率最高、产生量最大和造成危害最严重的藻毒素,具有多器官毒性、遗传毒性和致癌性。水产品中微囊藻毒素的残留会对人体产生危害,并对我国公众健康构成巨大威胁。因此,水产品中微囊藻毒素的检测和控制变得非常重要,迫切需要建立一种简便、快速、灵敏度较高的检测方法,以对水产品中的微囊藻毒素进行监控。为加强水产品中微囊藻毒素的痕量分析技术研究,对水产品中残留的微囊藻毒素开展监测,综述了国内外有关水产品中微囊藻毒素污染检测的提取、净化及分析技术进展。     

弱碱性大孔吸附树脂对腐殖酸的吸附

研究了腐殖酸分子量对弱碱性大孔树脂吸附腐殖酸的影响, 阐明了溶液中小分子芳环化合物(苯酚)及盐含量对树脂吸附腐殖酸的影响机制. 结果表明, 树脂对低分子量腐殖酸的吸附效果要优于高分子量腐殖酸; 低浓度苯酚在溶液中可以促进树脂吸附腐殖酸, 但溶液中苯酚浓度过高会对树脂吸附腐殖酸产生抑制作用; 溶液中的盐对树脂吸附腐殖酸的影响取决于溶液的pH值.     

微囊藻毒素在单波长紫外光照射下的光降解动态研究

研究了两种微囊藻毒素在两种紫外光照射下的光降解行为,研究结果表明:UV-C是降解微囊藻毒素较好的光源;光照强度是影响毒素降解重要的因素,其次是温度和酸度;在UV-C的照射下,水体腐殖质对光降解具有抑制作用;微囊藻毒素的光解反应符合准一级动力学模型.同时本工作还按实际环境水体中毒素的含量水平进行了模拟研究,发现紫外光UV-C对环境水体中低含量的微囊藻毒素具有很强的去除能力.为今后发展无毒、高效、经济实用的饮用水处理技术做了有益的探索.     

新型酰乙基葡甲胺树脂的合成及吸硼性能

采用一步法, 用氯乙酰化聚苯乙烯树脂(PS-Acyl-Cl)与葡甲胺反应制得一种同时含有α-酰乙基胺和邻羟基双官能团的新型酰乙基葡甲胺树脂, 考察了溶液pH值、 温度、 初始浓度和吸附时间对酰乙基葡甲胺树脂吸附硼的影响. 结果表明, 在实验浓度范围内, 该树脂对硼的吸附符合Langmuir方程, 最大吸附量约为28.1 mg/g干树脂, 优于氯甲基树脂制得的硼特效树脂. 表明α-酰乙基胺和邻羟基双官能团对硼有双重或协同吸附作用. 该树脂在pH=6.0时对硼的吸附量最大; 温度对树脂吸附的影响不大; 树脂解吸率大于96%; 树脂重复使用5次后吸附量基本不变. 动力学研究结果表明, 吸附过程为液膜扩散控制过程.     

Adsorption of microcystin-Lr onto iron oxide nanoparticles

In this study, the adsorption of microcystin-LR onto iron oxide (maghemite) nanoparticles from water was examined. Factors influencing the sorption behavior included microcystin and maghemite concentration, pH, ionic strength, and the presence of natural organic matter. Adsorption of microcystin-LR was strongly affected by pH. The adsorption increased with decreasing pH, with a maximum adsorption around pH 3. Adsorption of microcystin-LR on maghemite was primarily attributed to electrostatic interactions, although hydrophobic interactions may also play a role. The extent of microcystin-LR adsorption onto maghemite increased with increasing ionic strength at pH 6.4, since salt ions screened the electrostatic repulsion between adsorbed microcystin molecules. Adsorption of microcystin-LR was not significantly affected by the presence of Suwannee River Fulvic acid (SRFA) below 2.5 mg/L. However, adsorption decreased at higher SRFA concentrations (2.5–25 mg/L) due to competitive adsorption between SRFA and microcystin-LR for limited sorption sites.     

Mechanisms and factors influencing the removal of microcystin-LR by ultrafiltration membranes

In this study, we investigate the application of ultrafiltration (UF) for the removal of the cyanotoxin, microcystin-LR, and determine the dominant removal mechanisms. System variables examined included membrane characteristics, feed concentration, water recovery and operating pressure. While adsorption dominated rejection for most UF membranes, at least at early filtration times, both size exclusion and adsorption were important in removing microcystin-LR by the tight thin-film (TF) membranes. Adsorption was primarily attributed to hydrophobic interactions, although hydrogen bonding and physical surface properties such as surface roughness, thickness, and porosity may also play a role. Polysulfone membranes, the most hydrophobic membrane examined, significantly adsorbed microcystin-LR (91%), whereas the more hydrophilic cellulose acetate membranes adsorbed little or no microcystin-LR. The initial feed concentration had a significant influence on the adsorption capacity of TF membranes for microcystin-LR, which could be described based on a linear adsorption isotherm. An increase in water recovery and/or operating pressure led to an increase in the adsorption of microcystin-LR, probably due to increased convective transport. On the other hand, microcystin-LR rejection through size exclusion was reduced for higher water recovery and/or applied pressure.     

Retention mechanisms and selectivity in internal-surface reversed-phase liquid chromatography. Studies with cyanobacterial peptide toxins

Summary Microcystins-LA,-LR,-RR,-YR and nodularin, cyanobacterial peptide toxins, were separated by internal-surface reversed-phase (ISRP), high-performance liquid chromatography. The capacity factors of the toxins were measured in the range pH 2–8 using acetonitrile, isopropanol or tetrahydrofuran in potassium dihydrogenphosphate mobile phase. The main retention mechanism of the ISRP column was reversed-phase interaction but cation-exchange offered additional selectivity at neutral and slightly acidic pH. At neutral pH (10% modifier, 0.1 M buffer) the elution order was microcystin-LA (two nonpolar residues leucine and alanine as the variable amino acids), nodularin, microcystin-LR,-YR and-RR (two basic arginines as the variable amino acids). The retention times of all toxins except microcystin-RR were substantially longer at acidic pH. At pH 2 (10% modifier, 0.1 M buffer) where the cation-exchange mechanism was inoperative the elution order was changed to microcystin-RR, nodularin, microcystin-LR,-YR and-LA. The best separation was achieved at pH 2 where even two desmethylated microcystin-RR analogs could be separated from microcystin-RR.     

A competitive microcystin-LR immunosensor based on Au NPs@metal-organic framework (MIL-101)

A porous metal organic frameworks (MOFs) material (MIL-101) based on trivalent chromium skeleton were synthesized by hydrothermal synthesis method, and loaded with Au nanoparticles (Au NPs) to prepare Au NPs@MIL-101 composite materials which were used as a marker to label anti microcystin-LR (Anti-MC-LR). The composite materials have strong catalytic properties to the oxidation of ascorbic acid. Anti-MC-LR was immobilized on glassy carbon electrode surface using electrodeposition graphene oxide (GO) as a fixed matrix to construct a competitive microcystin-LR immunosensor.     

Adsorption of benzoic acid onto high specific area activated carbon cloth

The adsorption of benzoic acid from aqueous solution onto high area carbon cloth at different pH values has been studied. Over a period of 125 min the adsorption process was found to follow a first-order kinetics and the rate constants were determined for the adsorption of benzoic acid at pH 2.0, 3.7, 5.3, 9.1, and 11.0. The extents of adsorption and the percentage coverage of carbon cloth surfaces were calculated at 125 min of adsorption. Adsorption isotherms at pH values of 2.0, 3.7, and 11.0 were derived at 25 degrees C. Isotherm data were treated according to Langmuir and Freundlich equations and the parameters of these equations were evaluated by regression analysis. The fit of experimental isotherm data to both equations was good. It was found that both the adsorption rate and the extent of adsorption at 125 min were the highest at pH 3.7 and decreased at higher or lower pH values. The types of interactions governing in the adsorption processes are discussed considering the surface charge and the dissociation of benzoic acid at different pH values.     

Electrochemical immunoassay using quantum dot/antibody probe for identification of cyanobacterial hepatotoxin microcystin-LR

The presence of cyanobacterial hepatotoxins such as microcystin-LR poses health threats to humans due to their potential for causing severe physiological effects when contaminated drinking water is ingested. Here, the electrochemical detection of microcystin-LR is explored using a quantum dot/antibody (QD/Ab) probe for nanoparticle-based amplification and direct electrochemical transduction. The immunological recognition of microcystin-LR using the QD/Ab probe was amplified and converted to an electrochemical signal by measuring the cadmium ions released from QD based on square wave stripping voltammetry under optimized electrochemical factors. Whereas a qualitative analysis for microcystin-LR was achieved using the specific peak potential of the anodic voltammogram at −0.6 ± 0.05 V, concentration of the toxin was quantified based on the charge density of the anodic peak; a dynamic range of 0.227 to 50 μg/L and limit of detection of 0.099 μg/L were obtained with high sensitivity. The extracted microcystin-LR from Microcystis aeruginosa was estimated as 1,944 μg/g of dried weight of the microorganism.     

Modeling the adsorption of citric acid onto Muloorina illite and related clay minerals

The adsorption of citric acid onto goethite, kaolinite, and illite was measured as a function of pH (adsorption edges) and concentration (adsorption isotherms) at 25 degrees C. The greatest adsorption was onto goethite and the least onto illite. Adsorption onto goethite was at a maximum below pH 5 and decreased as the pH was increased to pH 9. For kaolinite, maximum adsorption occurred between pH 4.5 and pH 7, decreasing below and above this pH region, while for illite maximum adsorption occurred between about pH 5 and pH 7, decreasing at both lower and higher pH. ATR-FTIR spectra of citrate adsorbed to goethite at pH 4.6, pH 7.0, and pH 8.8 were compared with those of citrate solutions between pH 3.5 and pH 9.1. While the spectra of adsorbed citrate resembled those of the fully deprotonated solution species, there were significant differences. In particular the C[bond]O symmetric stretching band of the adsorbed species at pH 4.6 and 7.0 changed shape and was shifted to higher wave number. Further spectral analysis suggested that citrate adsorbed as an inner-sphere complex at pH 4.6 and pH 7.0 with coordination to the surface most probably via one or more carboxyl groups. At pH 8.8 the intensity of the adsorbed bands was much smaller but their shape was similar to those from the deprotonated citrate solution species, suggesting outer-sphere adsorption. Insufficient citric acid adsorbed onto illite or kaolinite to provide spectroscopic information about the mode of adsorption onto these minerals. Data from adsorption experiments, and from potentiometric titrations of suspensions of the minerals in the presence of citric acid, were fitted by extended constant-capacitance surface complexation models. On the goethite surface a monodentate inner-sphere complex dominated adsorption below pH 7.9, with a bidentate outer-sphere complex required at higher pH values. On kaolinite, citric acid adsorption was modeled with a bidentate outer-sphere complex at low pH and a monodentate outer-sphere complex at higher pH. There is evidence of dissolution of kaolinite in the presence of citric acid. For illite two bidentate outer-sphere complexes provided a good fit to all data.     

Development of a highly sensitive inhibition immunoassay for microcystin-LR

The development of a rapid one-step antigen-immobilized inhibition ELISA for microcystin-LR is described. For microplate coating a microcystin-biotin conjugate was synthesized. Using the commercially available monoclonal antibody MC10E7 in our newly established assay, IC₅₀ values of 0.045 μg l⁻¹ have been achieved. The detection limit for microcystin-LR was 4 ng l⁻¹. Considering the guidelines proposed by the world health organization (WHO) for microcystin-LR in drinking water (1 μg l⁻¹) the sensitivity of our test is more than sufficient. The period of assay processing could successfully be shortened to about 3 h without any loss in sensitivity. The suitability of the newly developed assay was evaluated with microcystin-LR spiked environmental water samples. Recovery rates for microcystin-LR between 60 and 165% were obtained in the linear range of the test format. The antigen-immobilized test format provides a highly reproducible, easy, and fast to perform detection system for microcystin allowing an internal retrospective quality control of the assay.     

倏逝波光纤免疫传感器探头的修饰及表征

光纤探头上修饰生物识别分子是倏逝波光纤免疫传感器实现目标物检测的关键步骤. 以微囊藻毒素-LR (microcystin-LR, MC-LR)为例, 采用先将小分子半抗原MC-LR与经戊二醛活化的惰性蛋白(OVA)反应生成复合物MC-LR-OVA, 然后将该复合物通过双功能试剂连接到硅烷化后的光纤探头表面, 并采用XPS和倏逝波全光纤免疫传感器对其修饰效果进行表征. 结果表明, 修饰后探头表面化学元素组成随不同修饰步骤发生了显著的变化, MC-LR-OVA被共价键合到探头表面上. 探头对MC-LR抗体表现出强烈的特异性响应, 而对其它抗体蛋白的非特异性吸附很弱, 并且具有良好的再生性能. 因此, 该修饰方案适用于环境小分子污染物的检测.