胶束毛细管电泳在线推扫富集技术测定血液中环丙沙星含量

采用在线Sweeping(推扫 )富集技术 ,建立了胶束毛细管电泳法测定血液中痕量乳酸环丙沙星的方法。考察了背景溶液pH值、SDS浓度、进样时间、血样预处理方法等对乳酸环丙沙星富集效果的影响。使用未涂层的毛细管柱 (5 5cm× 75 μmi.d .,有效柱长 4 7cm) ,30mmol/L硼砂 +80mmol/L十二烷基硫酸钠 (pH =9.4 0 )为背景溶液 ,在紫外检测波长 2 5 4nm、运行电压 1 8kV条件下 ,血浆样品用乙腈除蛋白后直接在线Sweep ing富集 ,富集倍数可达 6 0 0倍。线性范围在 0 .0 4～ 1 0mg/L (r =0 .999,n =8)。检出限为 0 .0 1mg/L。本方法减少了样品预处理的繁琐过程 ,弥补了毛细管电泳 (CE)在测定血液中痕量组分方面的不足 ,为CE在体内痕量药物分析等方面的应用提供了新的方法     

胶束毛细管电泳在线推扫技术分离检测猪肉组织中痕量喹诺酮类药物

利用胶束毛细管电泳法结合在线推扫富集技术对组织中残留的痕量环丙沙星、氧氟沙星和恩诺沙星进行了检测, 弥补了毛细管电泳检测灵敏度低的缺点, 大大减化了操作过程, 为动物食品组织中残留的痕量药物检测提供了一种新的简便可靠的方法.     

胶束在线扫集毛细管电泳法测定三聚氰胺

研究胶束在线扫集毛细管电泳法测定三聚氰胺的可行性,结果表明,与区带毛细管电泳相比,胶束在线扫集毛细管电泳法富集倍数提高约60倍。缓冲体系为140 mmol/L SDS+20 mmol/L NaH2PO4(pH 2.20)+10%(体积分数)甲醇,分离电压-18 kV,进样时间30 s,测量波长214 nm。考察了SDS浓度、pH、进样时间、运行电压等因素对分离测定的影响情况。在优化条件下,三聚氰胺在9 min时出峰,峰面积RSD≤3.7%。方法检出限、线性范围、相关系数分别为:0.13μg/mL、0.50~32.0μg/mL、0.9997。方法可用于奶粉中三聚氰胺的分离测定。     

胶束毛细管电泳在线吹扫富集技术测定面粉中的增白剂过氧化苯甲酰

建立了测定面粉中过氧化苯甲酰含量的一种新方法。面粉用甲醇超声萃取,过滤,直接进样分析。在电泳缓冲液为0.02 mol/L硼砂-硼酸缓冲液（含0.04 mol/L十二烷基硫酸钠）(pH 9.0)、紫外检测波长为214 nm、分离电压为10 kV的条件下,富集倍数可达150倍以上,过氧化苯甲酰的质量浓度和其色谱峰高呈良好的线性关系,过氧化苯甲酰的线性 范围为0.002～0.012 g/L(r=0.9998),最低检测限为2 mg/L。将该法用于面粉中过氧化苯甲酰的分析,样品无需繁琐的预处理过程便可直接定量,缩短了分析周期,简单方便,重现性好。     

胶束扫集毛细管电泳快速测定止咳露中的麻黄碱和可待因

采用胶束扫集毛细管电泳, 建立了快速测定止咳露中麻黄碱和可待因含量的方法, 并通过日间实验、柱间实验等对方法的稳定性进行了考察研究.胶束扫集电动色谱缓冲体系含60 mmol/L 十二烷基磺酸钠, 10 mmol/L NaH2PO4 (pH 2.20), 18%乙腈(V/V), 分离电压-14 kV, 测量波长200 nm. 讨论了pH、 SDS浓度、样品溶剂等对分离效果的影响. 在优化条件下, 麻黄碱和可待因均在5 min内出峰, 方法检出限(μg/mL)、线性范围(μg/mL)、相关系数分别为: 麻黄碱 0.433、 1.73～27.7、 0.9997, 可待因0.833、 3.33～50.3、 0.9996, 回收率在96.7%～103.5%之间. 峰面积日内RSD≤4.2% (n=5), 日间RSD≤8.0% (n=5), 柱间实验RSD≤2.3% (n=3).     

胶束扫集毛细管电泳分离测定绿原酸和咖啡酸

采用胶束扫集毛细管电泳分离测定双黄连口服液中的绿原酸和咖啡酸.试验条件为:重力进样时间40 s;以20 mmol/L NaH_2PO_4,100 mmol/L 十二烷基磺酸钠(SDS)为电泳缓冲液(含体积分数15%甲醇,pH 2.20),分离电压-20 kV,检测波长214 nm,讨论了pH、SDS浓度、样品溶剂等对分离效果的影响.在优化条件下,绿原酸和咖啡酸的检出限分别达到1.02和0.168 μg/mL,线性范围分别为5.86～51.5 μg/mL和1.27～14.5 μg/mL.     

毛细管电泳中样品的在线富集

由于毛细管进样体积小以及在柱检测光程短,极大地限制了毛细管电泳检测灵敏度的提高.为了提高毛细管电泳的检测灵敏度,多种样品富集的方法得以发展.本文对近年来毛细管电泳的样品预富集方法与应用作一简明的综述。     

推扫富集胶束电动毛细管色谱法和紫外分光光度法测定血液灌流前后血清中百草枯浓度的比较

胶束电动毛细管色谱;在线推扫富集技术;紫外分光光度法;血液灌流;百草枯;血药浓度     

胶束毛细管电泳在线扫集技术同时分离测定穿心莲内酯和脱水穿心莲内酯的研究

采用胶束毛细管电泳在线扫集技术分离测定了中药穿心莲中脱水穿心莲内酯和穿心莲内酯.电泳条件:以20 mmol/L H3BO310 mmol/L NaH2PO4-50mmol/L SDS(含体积分数20%甲醇,pH 2.4)为电泳运行缓冲溶液,未涂层石英毛细管(58 cm×50 μm i.d.,有效长度为41.2 cm)为分离通道,重力进样,进样高度为11 cm,-20 kV恒压,检测波长为246 nm.富集倍数可以达到200倍以上.在5.70～91.20 mg/L,和3.96～31.68 mg/L范围内呈良好的线性关系,对两种内酯分别进行了定量分析.加标平均回收率脱水穿心莲内酯为100.80%,穿心莲内酯为98.06%.     

胶束扫集毛细管电动色谱法测定药物中3种邻苯二甲酸酯

采用胶束扫集毛细管电动色谱技术,建立了测定药物中邻苯二甲酸二甲酯(DMP)、邻苯二甲酸二乙酯(DZP)和邻苯二甲酸二丁酯(DBP)的方法。电泳缓冲体系含80 mmol/L SDS,20 mmol/L NaH2PO4(pH 2.20),5%甲醇(V/V),分离电压-18 kV,重力进样80s×15.0cm,检测波长225 nm,使用Φ50μm×62.0 cm石英毛细管,有效长度50.0 cm。讨论了磷酸盐浓度、有机改善剂、SDS浓度、分离电压、进样时间等因素的影响,并考察了胶束扫集法对DMP、DEP和DBP的富集能力。在优化条件下,线性关系良好,相关系数大于0.9986,DMP、DEP和DBP的线性范围分别为1.25～240,1.04～200和1.56～200 mg/L,检出限分别为0.26,0.26和0.39 mg/L。方法应用于肠溶片中DMP、DEP和DBP的测定,回收率在93.3%～108%之间,RSD≤5.2%。每次样品测定可在10 min内完成。     

Determination of triazine herbicide residues in water samples by on-line sweeping concentration in micellar electrokinetic chromatography

A new method for the determination of atrazine, simazine and prometryn in water samples by on-line sweeping concentration technique in micellar electrokinetic chromatography （MEKC） was developed. Various parameters affecting sample enrichment and separation efficiency were systematically studied. Compared with the conventional MEKC method, up to 60-200-fold improvement in concentration sensitivity was achieved in terms of peak height by using this sweeping injection technique. The compound strychnine was used as the internal standard for the improvement of the experimental reproducibility. The limits of detection （S/ N = 3：1） for atrazine, simazine and prometryn were 9, 10 and 0.5 ng mL-1, respectively. This method has been successfully applied to the analysis of atrazine, simazine and prometryn in lake, steam and ground water.     

蒙脱石-石墨-聚氯乙烯复合电极测定制药废水中苯酚

报道了当制药废水PH8．0时，用蒙脱石－石墨－聚氯乙烯复合电极可以直接测定苯酚的含量而不受水杨酸存在的干扰，苯酚浓度在1．0μg/mL-25.0μg/mL范围内峰电流与浓度有良好的线性关系，I＝1．262c-0.046，相关系数r=0.998，检出限为0．1μg/mL，用该方法测定模拟制药废水中苯酚，其平均回收率为101．7％。     

Determination of malachite green in fish water samples by cloud‐point extraction coupled to cation‐selective exhaustive injection and sweeping‐MEKC

We have employed a high‐sensitivity off‐line coupled with on‐line preconcentration method, cloud‐point extraction (CPE)/cation‐selective exhaustive injection (CSEI) and sweeping‐MEKC, for the analysis of malachite green. The variables that affect CPE were investigated. The optimal conditions were 250 g/L of Triton X‐100, 10% of Na₂SO₄ (w/v), heat‐assisted at 60°C for 20 min. We monitored the effects of several of the CSEI‐sweeping‐MEKC parameters – including the type of BGE, the concentrations of SDS, the injection length of the high‐conductivity buffer, and the injection time of the sample – to optimize the separation process. The optimal BGE was 50 mM citric acid (pH 2.2) containing 100 mM SDS. In addition, electrokinetic injection of the sample at 15 kV for 800 s provided both high separation efficiency and enhanced sweeping sensitivity. The sensitivity enhancement for malachite green was 1.9×10⁴ relative to CZE; the coefficients of determination exceeded 0.9928. The LOD, based on an S/N of 3:1, of CSEI‐sweeping‐MEKC was 0.87 ng/mL; in contrast, when using off‐line CPE/CSEI‐sweeping‐MEKC the sensitivity increased to 69.6 pg/mL. This proposed method was successfully applied to determine trace amounts of malachite green in fish water samples.     

紫外差示分光光度法同时测定含苯系物废水中苯胺和苯酚

苯胺、苯酚在不同酸度的水溶液中具有不同的结构和紫外吸收光谱。以苯胺水溶液为测定液,以等浓度的苯胺酸溶液为参比液;以苯酚碱溶液为测定液,以等浓度的苯酚水溶液为参比液,分别测定其吸光度。结果表明:在280 nm处,当苯胺质量浓度为1~100 mg/L时;在287 nm处,当苯酚质量浓度为1~30 mg/L时,苯胺、苯酚的吸光度与浓度之间存在良好的线性关系,据此建立了紫外差示分光光度法。用此法不需分离直接测定了含苯系物废水中的苯胺和苯酚,回收率分别大于94.6%和96.7%。     

Determination of pharmaceuticals in drinking water by CD-modified MEKC: separation optimization using experimental design

A suite of 12 widely used pharmaceuticals (ibuprofen, diclofenac, naproxen, bezafibrate, gemfibrozil, ofloxacin, norfloxacin, carbamazepine, primidone, sulphamethazine, sulphadimethoxine and sulphamethoxazole) commonly found in environmental waters were separated by highly sulphated CD-modified MEKC (CD-MEKC) with UV detection. An experimental design method, face-centred composite design, was employed to minimize run time without sacrificing resolution. Using an optimized BGE composed of 10 mM ammonium hydrogen phosphate, pH 11.5, 69 mM SDS, 6 mg/mL sulphated beta-CD and 8.5% v/v isopropanol, a separation voltage of 30 kV and a 48.5 cm x 50 microm id bare silica capillary at 30 degrees C allowed baseline separation of the 12 analytes in a total analysis time of 6.7 min. Instrument LODs in the low milligram per litre range were obtained, and when combined with offline preconcentration by SPE, LODs were between 4 and 30 microg/L.     

水中痕量苯酚的微波萃取气相色谱分析

A method of microwave-assisted extraction and gas chromatography for determination of trace phenol in water was established.The conditions of microwave extraction and derivation were optimized.Acetone-cyclohexane(1∶1) mixture was used as extracting agent for water sample containing phenol and acetic anhydride was employed for the direct acetylation of phenol.Petroleum ether was used as the extracting agent to extract the derivative of phenol.Detection was carried out in GC-FID equipped with DB-17(30 m×0.53 ...     

高效液相色谱-荧光检测法测定环境水中的苯胺和苯酚

建立了用高效液相色谱荧光检测法同时测定环境水中苯胺和苯酚的分析方法。色谱柱为EclipseXDB C8(4.6mmi.d.×150mm,5μm),流动相为甲醇 磷酸盐缓冲液(0.1mol/L磷酸二氢钾 0 1mol/L磷酸氢二钠,pH6.87)V(甲醇)∶V(磷酸盐缓冲液)=50∶50,流速1 0mL/min,柱温25℃,检测波长0minλex/λem=230/340nm(测定苯胺),3.5minλex/λem=215/300nm(测定苯酚)。测定苯胺的线性范围0.2～120ng,r=0.9999,检出限0.01ng;测定苯酚的线性范围0.4～500ng,r=0.9998,检出限0.02ng,回收率98.1%～101.2%。该方法已用于对环境水中苯胺和苯酚的测定。     

Determination of phenol in industrial waste water by isotachophoresis

Summary The present work deals with the isotachophoretic analysis of phenol in industrial waste water. By variation of pH, temperature, leading and terminating electrolytes an optimal system for the determination of phenol in waste water was found. All samples were examined without preliminary chemical or physical treatment and therefore a direct analysis of waste water containing phenol is possible. The limit of the sensitivity for phenol is 0.1 ppm. The second part of this work concerns the separation of phenolic compounds, such as phenol, p-cresol and vanillin using the method described.

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Bestimmung von Phenol im Industrieabwasser mittels Isotachophorese

Zusammenfassung Die vorliegende Arbeit beschäftigt sich mit der isotachophoretischen Analyse von Phenol im Abwasser von Industriebetrieben. Durch Variation von pH, Temperatur sowie der leading und terminating Elektrolytlösungen wurde ein optimales System zur Analyse von Phenol im Abwasser erstellt. Alle Proben wurden ohne chemische oder physikalische Vorbehandlung untersucht, somit kann eine direkte Analyse zur Bestimmung von Phenol durchgeführt werden. Die Bestimmungsgrenze für Phenol in diesem System liegt bei 0,1 ppm. Ein zweiter Teil dieser Arbeit beschäftigt sich mit der Trennung von Phenol, p-Kresol und Vanillin unter den beschriebenen Analysenbedingungen.