分散液液微萃取-柱前衍生-高效液相色谱法测定水样中双酚A

建立了分散液液微萃取-柱前衍生-高效液相色谱法测定水样中双酚A的分析方法.通过交互正交试验和混合型优化实验设计对影响因素(萃取剂体积、分散剂类型及其体积、水样体积、pH值及离子强度)进行了优化.优化后的分散液液微萃取条件为:60 μL萃取剂,0.4 mL分散剂(甲醇),pH 4.0;优化后的柱前衍生化条件:0.1 mL 2.0 g/L衍生剂(对硝基苯甲酰氯)、衍生化时间30 min;方法的线性范围:0.002～0.2 mg/L(r=0.9997),检出限0.007 μg/L(S/N=3);不同浓度双酚A的萃取率为59.0%～63.0%,相对标准偏差(RSD)2.5%～9.2%(n=5);水样中双酚A的加标率为86.5%～107.1%,RSD为4.0%～11.9%(n=5),其它雌激素(雌酮、雌二醇、雌三醇和17α-乙炔基雌二醇)对双酚A的测定无干扰.本方法可以对水环境中的痕量BPA进行检测,具有操作简便、快速等优点.     

三相中空纤维膜液相微萃取-高效液相色谱法测定水中痕量双酚A

建立了三相中空纤维膜液相微萃取-高效液相色谱(HF-LPME-HPLC)方法,用于分析测定水中痕量双酚A的含量.设计了三相中空纤维膜液相微萃取系统,优化的HP-LPME最佳萃取条件为:萃取剂为正辛醇,接受相NaOH浓度为0.09 mol/L,样品溶液pH=4.0,NaC1加入量为30 g/L,搅拌速度为900 r/min,萃取时间为60 min.萃取后取20 μL接受相进行色谱分析.在最佳萃取条件下,方法的线性范围为0.5～200 μg/L(r＞ 0.999),检出限(信噪比为3)为0.2 μg/L;富集因子为241;方法RSD＜3.2％ (n=3).在实际环境水样中添加5,20和50μg/L的双酚A标准物质,加标平均回收率为92.8％～101.9％.表明本方法可用于水中痕量双酚A的快速准确测定.     

分散液相微萃取-高效液相色谱法测定水样中扑虱灵和哒螨灵

取水样置于离心管中,与含有三氯甲烷（萃取溶剂）的乙腈（分散剂）混合溶液充分混匀,静置5min,使水样中的扑虱灵和哒螨灵迅速富集于三氯甲烷液滴中,离心5min,下层三氯甲烷相经减压蒸干后,加入乙腈-水（75＋25）混合溶液50μL溶解残渣,分取20μL溶液供高效液相色谱法分析。用Symmetry C18色谱柱作固定相,流...     

分散液液微萃取-高效液相色谱法测定食品中的维生素A和E

以维生素 A 和 E 萃取率的平均值为检测指标,采用L18(37)正交试验法考察了萃取剂的类型、用量、分散剂的类型、用量以及萃取时间和离子强度6个影响因素,利用高效液相色谱法测定维生素含量.维生素 A 和 E 在0.23～174μg/mL 范围内线性关系良好;定性检出限分别为3.26 ng和7.6 ng(S/N=3);...     

分散液-液微萃取-高效液相色谱法测定环境水样中的多环芳烃

建立了简便、快速、有效的分散液-液微萃取-高效液相色谱-荧光检测(DLLME-HPLC-FLD)测定环境水样中15种多环芳烃(PAHs)的方法。重点探讨了萃取剂的种类和用量、分散剂的种类和用量以及萃取时间等对PAHs萃取效率的影响。在优化的条件下,评价了方法的可靠性。15种PAHs在0.01～10 μg/L范围内呈良好的线性关系,相关系数r均不小于0.9913,峰面积的相对标准偏差(RSD)在2.3%～4.7%之间(n=6)。在优化条件下,富集因子和萃取回收率良好,分别为674～1032和67.4%～103.2%,15种PAHs的检出限(S/N=3)在0.0003～0.002 μg/L之间。建立的方法应用于敖江水样中PAHs的检测,平均加标回收率在79.5%～92.3%之间,RSD在4.3%～6.7%范围内(n=5)。该方法适用于环境水样中痕量PAHs的分析。     

分散固相萃取-超声辅助分散液液微萃取/高效液相色谱法测定土壤中溴氰菊酯残留

建立了以分散固相萃取-超声辅助分散液液微萃取为样品前处理技术,结合高效液相色谱法(HPLC)测定土壤中溴氰菊酯。样品用甲醇∶水(1∶4,V/V)提取,经布氏漏斗减压抽滤,滤液经N-丙基乙二胺(PSA)、C18、石墨炭黑粉(GCB)净化后,用氯仿萃取,超声,离心后沉积相进行HPLC测定。对分散固相萃取吸附剂的选择及影响分散液液微萃取的因素进行了优化,在最优条件下,溴氰菊酯的富集倍数达到565倍,线性范围为0.005~2.5mg/kg,线性相关系数为0.9998,检出限为0.001mg/kg,平均加标回收率为70.3%~94.5%,相对标准偏差为2.5%~4.7%。该方法具有简便快速、准确灵敏、萃取效率高等特点,可用于土壤中溴氰菊酯残留检测。     

超声辅助分散液液微萃取-高效液相色谱法快速测定水样中的6种农药

为实现小体积环境水祥中不同农药的准确、快速、高灵敏测定,通过研究萃取剂、分散剂的种类、体积、盐浓度及超声时间对萃取效率的影响,结合分散液液微萃取与超声萃取技术,并与高效液相色谱联用,建立了快速测定环境水样中的吡虫啉、水胺硫磷、辛硫磷、毒死蜱、哒螨灵和阿维菌素6种农药的方法.在优化的萃取条件下,检测6种农药的线性范围为10～ 600 μg/L,检出限(S/N=3)为0.8～3.1 μg/L,相对标准偏差为4.7％～11.3％,富集倍数可达到58～187倍.本方法具有良好的线性、精密度和回收率,并具有较好的实用性.     

分散液液微萃取-高效液相色谱法测定环境水样中2,4-二氯酚

建立了简便、快速、有效的分散液液微萃取-高效液相色谱法测定环境水样中2,4-二氯酚的分析方法。对萃取剂、分散剂的种类和体积、萃取时间、离心时间、盐浓度等影响萃取效率的因素进行了优化。方法的线性范围为1～500μg/L(r=0.9997),相对标准偏差(RSD)为3.8%(n=6),检出限为0.19μg/L。该法适用于环境水样中的痕量2,4-二氯酚的检测。     

磁固相萃取-高效液相色谱法测定环境水样中双酚A

采用磁固相萃取-高效液相色谱法测定环境水样中双酚A的含量。优化的试验条件如下:1 50mL水样中加入20mg磁性微球进行萃取;2水样的pH为3.0;3萃取时间为15min;4解析溶剂为甲醇(80+20)溶液;5解析时间为10 min。采用C18色谱柱为分离柱,以甲醇-水(85+15)混合液为流动相,在检测波长224nm处进行测定。双酚A的质量浓度在5.0~500μg·L-1范围内与其峰面积呈线性关系,方法的检出限(3S/N)为1.0μg·L-1。方法应用于环境水样的分析,加标回收率在81.4%~109%之间,测定值的相对标准偏差(n=6)在5.7%~8.6%之间。     

凝固-漂浮分散液液微萃取-高效液相色谱法测定水样中氯酚

采用凝固-漂浮分散液液微萃取(SFO-DLLME)-高效液相色谱法测定水样中3种氯酚.以密度小于水,且凝固点为24 ℃的1-十二醇为萃取剂,甲醇为分散剂,对水样进行分散液液微萃取.将混合液离心,再通过冷冻凝固操作使漂浮的萃取剂和水相分离,萃取剂复溶后进样测定.本实验确定的最佳实验条件为:萃取剂200 μL、分散剂300 μL、1.2 g NaCl、1 mol/L H3PO4 200 μL、样品体积8.0 mL、萃取时间3 min.3种氯酚测定的线性范围为0.05～6.0 mg/L;检出限为20～38 μg/L.应用本方法分析实际水样,加标回收率在90.11%～107.7%之间;日间相对标准偏差在3.5%～4.6%之间.本方法扩展了分散液液微萃取萃取剂的选择范围,具有简便、快速、准确、环境友好等特点.     

Determination of the Migration of Bisphenol A from Polycarbonate by Dispersive Liquid-Liquid Microextraction Combined with High Performance Liquid Chromatography

A novel method for the determination of the migration of bisphenol A (BPA) from polycarbonate water bottles has been developed by using dispersive liquid–liquid microextraction (DLLME) followed by high performance liquid chromatography for compliance with the regulatory specific migration limit. Experimental parameters, including the type and volume of extractants and dispersers, the sample solution pH, addition of salt, extraction time, and temperature, were examined and optimized. Under the optimum conditions, average recovery rates for the real samples varied from 82% to 98%, with relative standard deviation values less than 3.6%. The method offered excellent linearity over a range of 0.8–600 µg L^?1 with a correlation coefficient of r = 0.9999. Intra-day and inter-day repeatability values expressed as relative standard deviation were 3.9% and 6.9%, respectively. The method quantitation limit and detection limit were 0.7 and 0.2 µg L^?1, respectively. The developed method was successfully applied to the determination of the migration of bisphenol A from 26 polycarbonate water bottles collected locally. The findings indicated the migration from the used bottles was significantly higher than the new ones, and the migration amounts from one sample was very close to the regulatory specific migration limit, and the amounts from seven samples exceeded the daily intake limit for infants.     

温控离子液体分散液液微萃取结合高效液相色谱法检测脐橙中染色剂残留

建立了QuEChERS-温控离子液体分散液液微萃取结合高效液相色谱法快速检测脐橙中5种染色剂残留的分析方法。QuEChERS前处理步骤:样品用乙腈快速提取,NaCl和无水MgSO4除水后,经N-丙基乙二胺净化。温控离子液体分散液液微萃取步骤:QuEChERS前处理的净化液(1 mL)为分散剂,1-辛基-3-甲基咪唑六氟磷酸盐离子液体(60μL)为萃取剂,55℃水浴12 min,将目标物富集。用高效液相色谱-紫外检测器分析,检出样品用超高效液相色谱-串联质谱确证。在0.01和0.05 mg/kg的添加水平下,5种染色剂的平均回收率为70.3%~93.6%,相对标准偏差为3.5%~9.2%,定量限为1.1~2.8μg/kg。     

固相微萃取/高效液相色谱法测定水中的微囊藻毒素

采用CWX/DVB萃取头,应用固相微萃取与高效液相色谱联用技术(SPME/HPLC)分析了水溶液中的痕量微囊藻毒素。对SPME的萃取条件进行了优化,并对实际水样进行了分析。该方法测定MC-LR(LR型微囊藻毒素)的线性范围为1.00~200μg/L,相关系数为0.999 5,检出限为0.45μg/L(3σ,n=11),相对标准偏差(RSD)为2.4%,回收率为90%~99%。该方法测定MC-RR(RR型微囊藻毒素)的线性范围为1.00~100μg/L,相关系数为0.998 8,检出限为0.15μg/L(3σ,n=11),RSD为2.4%,回收率为89%~100%。     

Determination of Estrogens in Water Samples by Ionic Liquid-Based Dispersive Liquid-Liquid Microextraction Combined with High Performance Liquid Chromatography

Using 1-hexyl-3-methylimidazolium hexafluorophosphate ([C₆MIM][PF₆]) ionic liquid as extraction solvent, five estrogens including estrone (E₁), 17β-estradiol (E₂), estriol (E₃), 17α -ethynylestradiol (EE₂), and diethylstilbestrol (DES) in water samples were determined by dispersive liquid-liquid microextraction (DLLME) followed by high performance liquid chromatography with a photodiode array detector and a fluorescence detector (HPLC-DAD-FLD). The extraction procedure was induced by the formation of cloudy solution, which was composed of fine drops of [C₆MIM][PF₆] dispersed entirely into the sample solution with the help of a disperser solvent (acetone). Parameters including both extraction and disperser solvents and their volumes, extraction and centrifugal time, sample pH, and salt effect were investigated and optimized. Under the optimized conditions, 110–349 fold enrichment factors of analytes were obtained. The calibration curves were linear in the concentration range of 0.2–100 µg L^?1 for E₂, E₃, and EE₂ detected with FLD, and 1–100 µg L^?1 for E₁ and DES detected with DAD. The correlation coefficient of the calibration curve was between 0.9990 and 0.9997. The limits of detection (LOD, S/N = 3) for the five estrogens were in the range of 0.08–0.5 µg L^?1. The relative standard deviations (RSD) for six replication experiments at the concentration of 5.0 µg L^?1 were ≤5.7%. The proposed method was applied to the analysis of three water samples from different sources (river water, waste water, and sea water). The relative recoveries of spiked water samples are satisfied with 89.3–102.4% and 88.7–105.2% at two different concentration levels of 5.0 and 50.0 µg L^?1, respectively.     

Determination of Trace Bisphenol A in Leachate by Solid Phase Microextraction Coupled with High Performance Liquid Chromatography

Abstract

A rapid determination method for trace bisphenol A in leachate by solid phase microextraction (SPME) coupled with high performance liquid chromatography (HPLC) was developed. The experimental condition of SPME, such as select operation, solid phase microextraction fibers, pH, extraction time, extraction temperature, desorption time, desorption solution, mode, and the analytical conditions of HPLC were optimized. As compared with the graph that was produced by HPLC alone, the graph by only HPLC couldn't analyze bisphenol A and compared to the results of three solid‐phase microextraction fibers. The linear range was between 0.0128 mg/L and 0.192 mg/L in this method, and the correlative coefficient was 0.9975. Limits of detection, repeatability, and reproducibility were also determined. The limit of detection of this method was 3.25 µg/L (3σ, n=11). The relative standard deviation (RSD, n=3) was 4.4%. The method was used for the determination of trace bisphenol A in leachate of Qingshan landfill and leachate of Liufang landfill. The recoveries were between 94.5% and 103.3%. This method is fast, convenient, sensitive, solvent free, and suitable for the determination of trace bisphenol A in leachate.