上转换发光免疫层析试纸条快速定量检测己烯雌酚

采用溶剂热法合成上转换纳米颗粒(UCNPs)-NaYF4∶ Yb,Er,进行表面功能化修饰,将其与己烯雌酚(DES)单克隆抗体偶联,制备荧光探针,以牛血清白蛋白-己烯雌酚(BSA-DES)偶联物和羊抗鼠二抗分别喷涂硝酸纤维膜,形成试纸条检测线(T线)和质控线(C线),建立了上转换发光免疫层析试纸条快速定量检测DES的方法.实验结果表明,此试纸条定量检测DES线性范围为25～ 10000 ng/mL(y=0.43927x-0.57647,R2=0.996),检出限为20.84 ng/mL,单个样品检测时间为15 min,批内和批间变异系数均小于10％,特异性识别能力强,在37℃存放下7天检测值RSD的平均值约为15％.加标回收实验显示平均回收率为90.1％～115.2％,相对标准偏差小于5％,与高效液相色谱法有较好的一致性.     

免标记比色核酸适配体传感器同步快速检测孔雀石绿和无色孔雀石绿

研究以双特异性核酸适配体A3作为传感探针、纳米金(AuNPs)为指示剂、NaCl溶液为聚集诱导剂,构建了一种新型的免标记AuNPs比色生物传感器,可实现水产品中孔雀石绿(MG)和无色孔雀石绿(LMG)的同步、快速、可视化检测。该方法的检测原理是核酸适配体A3对MG和LMG有双特异性识别能力,可作为MG和LMG理想的识别受体。它可通过静电作用吸附到AuNPs表面,保护AuNPs并抑制高盐溶液诱导的聚集,AuNPs溶液颜色不变,即为红色;当加入靶标MG或LMG后,该核酸适配体能够与靶标特异性结合,并从AuNPs表面上解离,AuNPs失去保护作用而在高盐溶液诱导下发生聚集,溶液颜色由红变蓝。根据颜色变化,可通过肉眼定性或通过光谱仪定量分析MG和LMG的残留量。该方法首先将50μL的核酸适配体A3(终浓度150 nmol/L)与150μL的AuNPs(终浓度1.25 nmol/L)混合,室温孵育6 min。随后加入50μL待测液,室温孵育30 min。最后加入50μL NaCl(终浓度150 mmol/L), 4 min后观察溶液颜色变化,并分别测定MG和LMG在520 nm和650 nm下的...     

快速检测甲胎蛋白的免疫层析试条的研制

研制了可简便、快速检出原发性肝癌标志物－－人血清中甲胎蛋白（AFP）的免疫层析试条。为此，研究了用国产试剂和材料制备胶体金、用此胶体金标记抗AFP单抗的影响因素以及抗AFP抗体固化条件、抗AFP抗体与其AFP结合能力等。结果表明，自制国产胶体金质量不亚于进口商品；金标单抗和固化抗体活性稳定，能分别显示出结合AFP分子不同表位的特异性。所得检测试条的检出速度在5至20min内，检测阳性阈值定为20ng AFP/mL血清。     

氟苯尼考胶体金免疫层析定量检测方法的建立

建立了定量检测氟苯尼考的胶体金免疫层析方法.对胶体金标记抗体时溶液pH和抗体浓度、金标抗体用量、检测线上抗原浓度以及检测时间进行了优化.采用胶体金试纸条读取仪测定试纸条检测线和质控线的信号强度,以标准品的浓度为横坐标,阳性样本和阴性样本的检测线/质控线的信号比值(Bx/B0)为纵坐标建立标准曲线.结果表明,胶体金免疫层析试纸定量检测氟苯尼考的线性范围为0.1~1.5 ng/mL,检出限为0.08 ng/mL,检测时间为15 min.本方法具有简便、快速和可定量等特点,适于大批量样品的现场筛查.     

菊酯类农药广谱型免疫层析试纸条的研究及应用

建立了菊酯类农药广谱型免疫层析检测方法,可同时检测水果、蔬菜中12种甲氰菊酯、溴氰菊酯、氯氰菊酯、三氟氯氰菊酯农药残留。以粒径20 nm的胶体金标记羊抗小鼠IgG抗体于金标垫上,分别固定包被原(检测线,T线)、兔抗山羊 IgG 抗体(质控线, C 线)于硝酸纤维素膜( NC 膜)上,与吸水垫及聚氯乙烯( PVC)底板组合成层析试纸条。10 g样品经乙腈提取,PBS稀释4倍,取100μL与菊酯类农药的单克隆抗体混合后,直接用于试纸条检测。结果表明,试纸条对甲氰菊酯、溴氰菊酯、氯氰菊酯、三氟氯氰菊酯农药的裸眼观察检测灵敏度为0.5,5.0,5.0和5.0μg/mL,检测时长为8~10 min,采用QuEChERS方法,方法检测灵敏度可提高16倍。对蔬菜和水果的方法验证表明,除辣椒基质干扰呈假阳性外,其它样本的检测结果均与GC方法结果一致。试纸条采用金标羊抗小鼠IgG二抗的方法,使检测结果的重现性更好、更稳定,且抗基质干扰能力强,为菊酯类农药的累积毒性检测提供了新方法。     

新型“磁包金”金磁纳米粒子免疫层析试纸条定量检测血清中的人绒毛膜促性腺激素

将油酸修饰的氧化铁纳米粒子(Oleic acid coated iron oxide nanoparticles, OC-IONPs)与油胺修饰的金纳米粒子(Oleylamine-coated gold nanoparticles, OA-AuNPs)通过乳液自组装法共封装在聚合物基质中,合成了具有"磁包金"核壳异质结构的新型金磁纳米粒子(Magnetic coated gold nanoparticles, MGNPs)。由于OA-AuNPs聚集在内核, OC-IONPs分布于外壳,有效避免了OA-AuNPs的磁屏蔽效应,相较于传统"金包磁"型纳米结构,此MGNPs具有高的磁饱和强度(为初始氧化铁纳米粒子的80%)和强的吸光度(为传统30 nm胶体金纳米粒子的12.5倍)。进一步以此MGNPs为免疫层析(Immunochromatographic assay, ICA)的新型双功能标记探针,以人绒毛膜促性腺激素(Human chorionic gonadotropin, HCG)为模型检测物,建立了高灵敏检测人血清中HCG的免疫层析方法(MGNPs-ICA)。本研究所构建的试纸条定量...     

铁纳米线/壳聚糖/抗体生物探针的制备和层析检测

以戊二醛为交联剂制备Fe纳米线/壳聚糖复合物,研究其对牛血清白蛋白的吸附性能:缓冲液pH为6.0时,达到最大平衡吸附量,为148.40 mg/g;以Fe纳米线/壳聚糖交联吸附α-HCG抗体制备生物探针,组装层析试纸条,进行免疫层析实验,结果表明:其检测灵敏度为10 IU/L,与市场上销售的胶体金早孕试纸条相比,可以将早孕检测时间提前2～3 d.     

胶体金免疫层析法快速检测水产品中河豚毒素的研究

该文将特异性识别河豚毒素的单克隆抗体加以胶体金标记用作示踪物,建立了豚毒素的胶体金免疫层析技术快速检测方法。优化了胶体金体系的pH值、抗原抗体浓度、离子浓度、表面活性剂种类以及样品前处理方法。结果显示：在最优条件下,建立的胶体金免疫层析法对河豚毒素的定量检出限为0.5 ng/mL,线性范围为0.8～10.6 ng/mL,定性检出限（裸眼判别）为12.0 ng/mL。河豚、织纹螺等样品的加标回收率为70.5%～110%,相对标准偏差为3.7%～7.1%,检测结果与LC-MS/MS法一致。所建立的胶体金免疫层析技术在现场快速检测方面具有良好的可行性和实用性,可用于大量样品的快速筛查和河豚毒素中毒后的快速诊断。     

金纳米棒免疫层析试纸条定量检测前列腺特异性抗原

建立了一种基于金纳米棒(GNR)的免疫层析方法,用于快速定量检测前列腺特异性抗原(PSA)。以GNR为标记探针,通过包裹羧基化的聚合物后,采用共价偶联的方式连接抗PSA单克隆抗体形成偶联物,以鼠抗PSA单克隆抗体和羊抗鼠IgG分别喷涂硝酸纤维素膜,形成试纸条的检测线和质控线,采用三明治夹心法构建GNR免疫层析试纸条,用于PSA的定量检测。结果表明,GNR免疫层析试纸条特异性强,稳定性好,灵敏度高,对PSA检测的线性范围为0.1～50 ng/mL,检出限为0.1 ng/mL,批内和批间变异系数均小于10%,且具有良好的保存稳定性。本方法可用于检测血清中PSA的浓度水平,对于前列腺癌的早期诊断、监测治疗及预后判断具有重要意义。     

磁性碳纳米管对水中孔雀石绿的吸附性能研究

（1）以磁性碳纳米管吸附处理孔雀石绿溶液,考察了吸附剂用量、孔雀石绿浓度以及温度等对吸附平衡的影响。结果表明,该吸附不受溶液pH值的影响,符合准二级动力学方程（R2＞0.999）。不同温度下,该吸附过程满足Langmuir方程（R2>0.97）和Freundlich方程（R2>0.98）,qmax、KF随温度升高而变大。D-R等温方程拟合结果表明该吸附的机理是以化学吸附为主。热力学参数计算结果表明,该吸附是一个熵增的自发吸热过程,温度越高越利于吸附的进行。     

基于金属有机框架水凝胶的一步式快速富集检测养殖水体中孔雀石绿北大核心CSCD

孔雀石绿是一种三苯甲烷类化合物,在水产品饲养中对疾病的防治有着不错的疗效,但因对人体健康有危害而被列为禁用药。由于实际样品中成分复杂,对于此类染料的检测方法难以同时兼具富集性好、灵敏度高且方便快速的优点。该工作制备了金属有机框架材料(MOF),采用MOF纳米材料掺杂的水凝胶(PAAM-SA/MOF)对养殖水体中的孔雀石绿进行吸附研究。采用一系列表征手段对MOF、PAAM-SA和PAAM-SA/MOF的微观形貌进行分析,结果表明吸附材料已成功合成。通过优化水凝胶吸附剂用量、吸附时间、孔雀石绿溶液pH、吸附温度、孔雀石绿溶液初始浓度等吸附萃取条件,使溶液中的孔雀石绿基本完全吸附在水凝胶中,在最优条件下,吸附效率最高可达97%。此外,采用不同极性的有机溶剂对吸附的孔雀石绿进行洗脱,通过优化洗脱液体积,脱附率最高达99%。在最佳条件下,该方法在高、中、低3个水平下的样品加标回收试验中回收率达到84.8%~118.1%,相对标准偏差小于5.1%,方法的检出限为0.083μg/L(S/N=3),定量限为0.25μg/L(S/N=10)。该方法简化了前处理过程,结合了MOF和水凝胶这二者各自的优点,添加的MOF材料可以在水凝胶体系中发挥其良好的吸附性,既解决了传统的MOF材料因粒径太小而回收率低的难题,便于吸附后直接提取,同时也解决了纯水凝胶吸附效率较低的问题,整体上提高了吸附效率和可回收性。实际样品测试表明该新型水凝胶吸附材料可用于养殖水体中孔雀石绿的快速萃取和检测,在食品检测领域具有很大潜力。     

Synthesis of carboxyl‐functionalized magnetic nanoparticles for adsorption of malachite green from water: Kinetics and thermodynamics studies

Magnetic carboxyl‐coated silica iron oxide nanoparticles (Fe₃O₄@SiO₂‐COOH NPs) were successfully synthesized, characterized, and then applied as a nano‐adsorbent for removal of malachite green (MG) from aqueous solutions. According to the experimental results, about 97.5% of MG could be removed from aqueous solutions using an adsorbent amount of 0.5 g/L at pH = 9 in 120 min. The kinetics and equilibrium adsorptions is well‐described by the pseudo‐second‐order kinetics and Langmuir model with the maximum absorption capacity of 263.16 mg/g, respectively. Thermodynamic studies showed that the adsorption of the hazardous MG dye was spontaneous and endothermic with a random process.     

孔雀石绿与牛血清白蛋白作用的光谱研究

应用荧光及紫外光谱法研究了孔雀石绿(MG)与牛血清白蛋白(BSA)相互作用的光谱特性。测定了16℃、26℃、36℃三个温度下的结合常数KA(7.066×103、4.638×103、1.338×103)和结合位点数n(1.2、1.1、1.0)。结果表明:MG对BSA内源荧光的猝灭机理主要为静态猝灭;MG主要以范德华力与BSA相互作用;同步荧光技术研究了MG对BSA构象的影响,表明BSA的荧光主要源于色氨酸残基,MG对BSA的构象有影响;利用F ster偶极-偶极非辐射能量转移理论,计算了三个温度下MG与BSA的作用距离(r16℃=3.30,r26℃=3.314,r36℃=3.58nm),表明MG对BSA的荧光猝灭中存在能量转移。     

异硫氰基孔雀石绿受激拉曼光谱研究

本文报道了具有时间分辨能力的全频宽带受激拉曼（BBSRS）系统和关于异硫氰基孔雀石绿（MGITC）受激拉曼光谱（sRs）的研究．BBSRS系统的探测光为450-800nm宽带连续白光,泵浦光为280～900nm范围内连续可调谐的ps窄带可见光（带宽≈7．5cm-1,脉宽≈2．5ps）．在合适的泵浦波长下,该系统可同时获取拉曼损失和拉曼增益光谱．MGITC的SRS研究结果表明,当拉曼损失谱峰出现在最大吸收波长（≈627nm）时,共振SRS谱峰强度最大;当泵浦或增益谱峰在最大吸收波长附近时,未观察到明显的共振拉曼信号;共振峰强度随浓度增大而增大,随泵浦功率增大而迅速增大,后趋于饱和;共振和非共振峰强在延时零点附近达到最大值,并随延时绝对值的增大而减小．     

Rapid detection of malachite green in fish with a fluorescence probe of molecularly imprinted polymer

A fluorescent probe based on CdTe/CdS quantum dots coated with molecularly imprinted polymer shell was designed. The fluorescence emission of the probe was at 622?nm. The probe presented selective adsorption for malachite green and the adsorption caused fluorescence quenching due to fluorescence resonance energy transfer. A linear relationship ranging from 0.05 to 10?μmol·L^?1 between relative fluorescence quenching intensities and malachite green concentrations was obtained with a detection limit of 0.029?μmol·L^?1. The fluorescent probe was successfully applied to the determination of malachite green in fish with recoveries ranging from 93.3 to 107.7%.     

Adsorptive removal of malachite green and Rhodamine B dyes on Fe3O4/activated carbon composite

This study demonstrates the adsorption experiments of toxic dyes malachite green (MG) and Rhodamine B (RB) on Fe₃O₄-loaded activated carbon (AC). AC, which is known to be a high-capacity adsorbent, was aimed to be easily separated from aqueous media by loading it with Fe₃O₄. Fe₃O₄-loaded AC was prepared by the coprecipitation method and named magnetic activated carbon (M-AC), and the produced M-AC was characterized by x-ray diffraction (XRD), thermogravimetric analysis (TGA), and pH_pzc analyses. MG and RB adsorption by the M-AC was performed separately by batch technique and the effects of adsorbent amount, solution pH, and initial dye concentration on the adsorption were explored. Maximum removal efficiencies were found to be 96.11% for MG and 98.54% for RB, and the Langmuir isotherm model was the most fitted isotherm model for the adsorption. The kinetic and thermodynamic studies showed that the adsorption proceeded via the pseudo-second-order kinetic model and endothermic in-nature for both dyes.     

Magnetic solid-phase extraction of malachite green using soluble eggshell membrane protein doped with magnetic graphene oxide nanocomposite

ABSTRACT

This study describes a new magnetic solid-phase extraction (MSPE) technique based on Fe₃O₄/graphene oxide-soluble eggshell membrane protein (Fe₃O₄/GO-SEP) for accurate measurement of malachite green (MG) residue in various water samples residues by UV-Vis spectroscopy. The morphology of the prepared adsorbent has been studied by scanning electron microscopy and atomic force microscopy in details. Parameters affecting the MSPE were optimised and determined with UV-Vis spectrophotometry thoroughly. Under the optimised extraction circumstances, the introduced method represented a wide linearity over the concentration of 0.5–250 ng mL^?1, a high enrichment factor of 83.3 and low detection limit of 0.2 ng mL^?1. The prepared Fe₃O₄/GO-SEP was successfully used for preconcentration and determination of MG in river and fish farming water samples with suitable precision and accuracy.     

A simple linear sweep voltammetric method for the determination of double-stranded DNA with malachite green

In pH 3.5 Britton—Robinson buffer solution double-stranded (ds) DNA can react with malachite green (MG) to form an interaction complex, which resulted in the decrease of the electrochemical response of MG, MG had a well-defined second-order derivative linear sweep voltammetric peak at −0.73 V (vs. SCE). After the addition of dsDNA into MG solution, the reductive peak current decreased with the positive shift of peak potential, which was the typical characteristic of intercalation. Based on the interaction, an indirect electrochemical determination method for dsDNA was established. The optimum conditions for the reaction were investigated and there were little or no interferences from the commonly coexisting substances. The decrease of peak current was linear with the concentration of dsDNA over the range of 0.8–12.0 μg cm⁻³ with the linear regression equation as ΔI _p″/nA = 91.70 C/(μg cm⁻³) + 74.55 (n = 10, γ = 0.990). The detection limit was calculated as 0.46 μg cm⁻³ (3σ). The method had high sensitivity and was further applied to the dsDNA synthetic samples with satisfactory result. The interaction mechanism was discussed with the intercalation of DNA-MG to form a supramolecular complex and the stoichiometry of the supramolecular complex was calculated by electrochemical method with the binding number 3 and the binding constant 2.35 × 10¹⁵ (mol dm⁻³)⁻³.